Ecological Risk Assessment for Section 3 Registration for Fruit, 

Vegetable, Selected Field Crop, Turf and Ornamental Uses of 

Chlorantraniliprole (PC Code 090100)

(DP Barcode: DP338512)

N

N N

N

O

Cl

Br

N

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Cl

PREPARED BY:

Edward Odenkirchen, Ph.D.

James Hetrick, Ph.D.

Environmental Risk Branch 1

Environmental Fate and Effects Division

Office of Pesticide Programs

APPROVED BY:

Nancy Andrews, Ph. D., Chief

Environmental Risk Branch 1

Environmental Fate and Effects Division

Office of Pesticide Programs
2

I. EXECUTIVE SUMMARY ........................................................................................ 4

A. Nature of Stressor ................................................................................................... 4

1. Effects Summary............................................................................................. 4

2. Fate Summary ..................................................................................................... 4

B. Potential Risk to Non-Target Organisms................................................................ 5

1. Terrestrial Plants................................................................................................. 5

2. Terrestrial Invertebrates...................................................................................... 5

3. Terrestrial Vertebrates ........................................................................................ 6

4. Aquatic Plants..................................................................................................... 6

5. Freshwater Fish and Amphibians........................................................................ 6

6. Freshwater Invertebrates..................................................................................... 6

7. Estuarine/Marine Fish......................................................................................... 8

8. Estuarine/Marine Invertebrates........................................................................... 9

9. Assessment of Potential Effects to Federally Listed Threatened and Endangered 

Species ...................................................................................................................... 11

II. PROBLEM FORMULATION.................................................................................. 12

A. Nature of the Federal Action................................................................................. 12

B. Nature of the Chemical Stressor ........................................................................... 12

C. Use Characterization............................................................................................. 14

D. Ecological Receptors Considered in this Risk Assessment .............................. 18

E. Exposure Pathways Considered for Terrestrial Organisms.............................. 18

F. Exposure Pathways Considered for Aquatic Organisms...................................... 19

G. Conceptual Model................................................................................................. 19

1. Risk Hypothesis................................................................................................ 19

2. Conceptual Diagram ......................................................................................... 20

H. Analysis Plan........................................................................................................... 20

1. Preliminary Identification of Data Gaps and Methods..................................... 20

2. Assessment Endpoints ...................................................................................... 21

3. Exposure Measures........................................................................................... 21

4. Effects Measures............................................................................................... 23
3

IV. ANALYSIS........................................................................................................... 24

A. Environmental Fate and Transport Characterization ........................................ 24

1. Aquatic Organism Exposure ................................................................................ 28

2. Terrestrial Vertebrate Exposure.................................................................... 33

3. Terrestrial Invertebrate Exposure ..................................................................... 33

4. Terrestrial Plant Exposure................................................................................. 33

B. Effects Characterization.................................................................................... 34

1. Avian Toxicity .................................................................................................. 35

2. Mammalian Toxicity......................................................................................... 36

3. Terrestrial Invertebrate Toxicity....................................................................... 37

4. Terrestrial Plant Toxicity.............................................................................. 40

5. Freshwater Invertebrate Toxicity...................................................................... 41

6. Freshwater Fish Toxicity .................................................................................. 43

7. Estuarine/Marine Invertebrate Toxicity............................................................ 44

8. Estuarine Marine Fish Toxicity ........................................................................ 45

9. Aquatic Plant Toxicity...................................................................................... 46

10. Summary of Effects Measurement Endpoint Values Used in the Risk 

Assessment................................................................................................................ 47

V. RISK CHARACTERIZATION............................................................................ 48

A. Risk Estimation................................................................................................. 48

1. Terrestrial Vertebrate Risk Quotients............................................................... 48

2. Terrestrial Invertebrate Risk Quotients............................................................. 49

3. Terrestrial Plant Risk Quotients........................................................................ 49

4. Freshwater Fish Risk Quotients........................................................................ 50

5. Freshwater Invertebrate Risk Quotients............................................................ 52

6. Estuarine/Marine Fish Risk Quotients.............................................................. 54

7. Estuarine/Marine Invertebrate Risk Quotients.................................................. 56

8. Aquatic Plants................................................................................................... 58

B. Risk Discussion..................................................................................................... 62

1. Quantified Risks................................................................................................ 62

2. Qualitative Discussion of Terrestrial Plant Risks............................................. 67

3. Qualitative Discussion of Terrestrial Invertebrate Risks.................................. 67

VI. FEDERALLY LISTED THREATENED AND ENDANGERED SPECIES 

ASSESSMENT................................................................................................................. 68

A. Action Area....................................................................................................... 68

B. Taxonomic Groups Potentially at Risk................................................................. 69

C. Analysis of Dose Response (Effects Study Slope) ............................................... 70

D. Consideration of Alternative Assumptions of Drift. (Need to Work ON)........... 71

E. Critical Habitat...................................................................................................... 72

F. Co-Location Analysis ........................................................................................... 73
4

I. EXECUTIVE SUMMARY

A. Nature of Stressor

The subject of this risk assessment is a Federal Insecticide, Fungicide, Rodenticide Act 

(FIFRA) Section 3 registration for the use of the insecticide chlorantraniliprole. This 

insecticide is proposed for a variety of use sites including brassica (cole), leafy vegetables 

(broccoli, broccoli raab, brussels sprouts, cabbage, chinese cabbage, cauliflower, cavalo 

broccoli, collards, kale, kohlrabi, mizuna, mustard greens, mustard spinach, rape greens), 

curcurbits (vegetables, melons, squash), and fruiting vegetables (eggplant, goundcherry, 

peppers, tomatoes), non-brassica leafy vegetables (celery, lettuce, spinach, Arugula, 

Cardoon, Amaranth leafy), cotton, grape, pome fruit (apple, crabapple, loquat, mayhaw, 

pear, oriental pear, and quice), potato, stone fruits (apricot, sweet cherry, tart cherry, 

plum, chickasaw plum, Damson plum, Japanese plum, plumcot, prune), turf, ornamental 

plants, and groundcovers. 

1. Effects Summary

There were no data gaps in the effects data. In agreement with international 

governmental partners associated with registration efforts for this pesticide, ecological 

effects data evaluation responsibilities are being met through the efforts of the Pesticides 

Safety Directorate (PSD), UK. The Agency is using the results of the PSD review as they

appear in the dossier for registration in Europe. Except where specifically reported,

independent validation of statistical results for effects studies was not performed during 

the PSD reviews.

Chlorantraniliprole can be characterized as having very little toxicity to terrestrial and 

aquatic vertebrates. As can be expected for an insecticide, the compound is toxic to a 

number of terrestrial and aquatic invertebrates. The compound can produce limited 

adverse effects in terrestrial and aquatic plants. 

Available data for formulated products suggested no concern for enhanced toxicity of 

formulations versus the active ingredient alone. Data for degradates suggest no concern 

for toxicity exceeding the parent compound and in most cases toxicity is orders of 

magnitude below the parent. 

2. Fate Summary

There were no identified data gaps in the fate data. Under international agreements the 

Agency was not responsible for conducting environmental fate data reviews. Data 

review is being conducted for use by all parties to the international agreement by the 

Pesticide Control Service, Department of Agriculture and Food, Ireland. The Agency is 

using the results of the PSD review as they appear in the dossier for registration in 

Europe except for the aerobic soil metabolism half-lives. EFED recalculated aerobic soil 
5

metabolism half-lives for chlorantraniliprole to be representative of the total extractable 

chlorantraniliprole fraction in soil. The total extractable soil fraction of 

chlorantraniliprole (water pre-soak and acetonitrile/water + acid/surfactants or 

concentrated acid at evaluated temperature1) was used to a conservative half-life of

bioavailable chlorantraniliprole in soil. 

Based on this review, chlorantraniliprole may be characterized as persistent and mobile in 

terrestrial and aquatic environments. Extended chlorantraniliprole use is expected to 

cause accumulation of residues in soil from year to year. Major routes of dissipation are 

expected to be alkaline-catalyzed hydrolysis, photodegradation in water, leaching, and 

runoff.

Nine degradates/metabolites of the parent compound have been identified in 

environmental fate studies: IN-EQW78, IN-LBA22, IN-LBA24, IN-LBA23

IN-ECD73, IN-F6L99, IN-EVK64, IN-F9N04, and IN-GAZ70. The greatest percentage 

production of a degradate was for IN-LBA24, which was 90% of applied parent produced 

in the photolysis study at pH7. This risk assessment did not quantify the risks from these 

degradates because they were commonly of lower toxic potency than the parent. For 

example IN-LBA24 is orders of magnitude less toxic than the parent pesticide. Coupling 

the observed lower toxic potency with the risk assessments exposure modeling 

assumptions of stability for the parent would suggest that excluding the degradates from 

quantitative risk estimation would not substantially affect the conclusion of the risk 

assessment.

B. Potential Risk to Non-Target Organisms

1. Terrestrial Plants

The conclusion of the risk assessment is that best available information indicates that 

risks of direct effects to non-listed terrestrial plants are below Agency screening levels of 

concern.

2. Terrestrial Invertebrates

While the Agency currently does not use a standard method for quantifying risks of 

pesticides to terrestrial invertebrates, available effects data for insect species, when 

compared with application rates suggest that the insecticide chlorantraniliprole has the 

potential to produce direct adverse effects in some non-target insect species. It appears 

from the effects data that sensitivity to the pesticide is quite varied among tested 

invertebrates. If species specific risk assessment becomes necessary (e.g., assessment of 

a federally listed threatened or endangered species) it is recommended that closer 

 

1

 Total residue half-lives were calculated using the summed chlorantraniliprole concentration (expressed 

as percent applied) in the water pre-soak and acetonitrile/water + acid/surfactants or concentrated acid at 

evaluated temperature soil extracts. 
6

evaluation of the potential representation of the invertebrate data set for a specific 

organism be considered.

3. Terrestrial Vertebrates

The conclusion of the risk assessment is that best available information indicates that 

risks of direct effects to non-listed terrestrial vertebrates are below Agency screening 

levels of concern.

4. Aquatic Plants

The conclusion of the risk assessment is that best available information indicates that 

risks of direct effects to non-listed aquatic plants are below Agency screening levels of 

concern.

5. Freshwater Fish and Amphibians

The conclusion of the risk assessment is that best available information indicates that 

risks of direct effects to non-listed freshwater fish and amphibians are below Agency

screening levels of concern.

6. Freshwater Invertebrates

The following tables present the conclusions of the risk assessment for freshwater 

invertebrates. Acute concerns are triggered by freshwater invertebrate RQ values for 

every exposure scenario modeled (except for ground spray for the OR apple and CA turf 

scenarios, which involve lower rainfall assumptions and thus lower estimates of aquatic 

exposure). These concerns are limited primarily to acute effects to listed species and 

restricted use considerations.

Chronic freshwater invertebrate risk concerns were identified for proposed uses on FL 

peppers (ground or aerial spray), FL cucumbers (ground or aerial spray), CA nursery

(ground spray), FL nursery (ground spray), and TN nursery (ground spray). In all cases 

the RQs were less than an order of magnitude above the Agency concern level. These 

chronic endpoints are calculated using the most sensitive chronic NOEC for daphnids 

(4.47 ug/L ug/L). 
7

Tier II RQs for FW Invertebrates from Aerial Spray Application of DPX-E2Y45 for Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Concerns

Rate

(lbs/A)

#

Int

(days)

FL cabbage 0.065 3 3 2.652 2.146 0.1850 0.4801 RU,LS

FL cucumber 0.065 3 5 5.693 4.939 0.4258 1.1049 RU,LS, Chronic

PA tomato 0.098 2 5 1.513 1.306 0.1126 0.2922 RU,LS

CA tomato 0.098 2 5 1.080 0.922 0.0795 0.2063 LS

FL tomato 0.098 2 5 3.660 3.001 0.2587 0.6714 RU,LS

FL peppers 0.098 2 5 6.749 5.683 0.4899 1.2714 RU,LS Chronic

CA lettuce 0.065 3 3 3.579 2.997 0.2584 0.6705 RU,LS

CA cotton 0.099 2 5 1.785 1.576 0.1359 0.3526 RU,LS

NC cotton 0.099 2 5 3.730 3.207 0.2765 0.7174 RU,LS

MS cotton 0.099 2 5 3.769 3.271 0.2820 0.7318 RU,LS

NY grape 0.099 2 7 1.389 1.197 0.1032 0.2678 RU,LS

CA grape 0.099 2 7 1.188 1.026 0.0884 0.2295 LS

NC apple 0.099 2 10 1.359 1.153 0.0994 0.2579 LS

PA apple 0.099 2 10 1.245 1.091 0.0941 0.2441 LS

OR apple 0.099 2 10 0.786 0.674 0.0581 0.1508 LS

ID potato 0.066 3 5 1.021 0.859 0.0741 0.1922 LS

ME potato 0.066 3 5 1.558 1.392 0.1200 0.3114 RU,LS

GA peach 0.099 2 7 1.086 0.886 0.0764 0.1982 LS

MI Cherry 0.099 2 7 1.035 0.907 0.0782 0.2029 LS

1-Acute Toxicity Endpoint= 11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
8

Tier II RQs for FW Invertebrates from Ground Spray Application of DPX-E2Y45 for Various Crop 

Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lbs/A) # Int

FL cabbage 0.065 3 3 2.531 2.045 0.1763 0.4575 RU,LS

FL cucumber 0.065 3 5 5.624 4.86 0.4190 1.0872 RU,LS, Chronic 

PA tomato 0.098 2 5 1.280 1.097 0.0946 0.2454 LS

CA tomato 0.098 2 5 0.731 0.619 0.0534 0.1385 LS

FL tomato 0.098 2 5 3.436 2.817 0.2428 0.6302 RU,LS

FL peppers 0.098 2 5 6.501 5.475 0.4720 1.2248 RU,LS, Chronic

CA lettuce 0.065 3 3 3.311 2.781 0.2397 0.6221 RU,LS

CA cotton 0.099 2 5 1.470 1.28 0.1103 0.2864 RU,LS

NC cotton 0.099 2 5 3.473 2.995 0.2582 0.6700 RU,LS

MS cotton 0.099 2 5 3.575 3.116 0.2686 0.6971 RU,LS

NY grape 0.099 2 7 1.189 1.025 0.0884 0.2293 LS

CA grape 0.099 2 7 0.813 0.706 0.0609 0.1579 LS

NC apple 0.099 2 10 0.999 0.852 0.0734 0.1906 LS

PA apple 0.099 2 10 1.048 0.898 0.0774 0.2009 LS

OR apple 0.099 2 10 0.410 0.365 0.0315 0.0817 None

ID potato 0.066 3 5 0.812 0.68 0.0586 0.1521 LS

ME potato 0.066 3 5 1.350 1.195 0.1030 0.2673 RU,LS

GA peach 0.099 2 7 0.763 0.62 0.0534 0.1387 LS

MI Cherry 0.099 2 7 0.867 0.739 0.0637 0.1653 LS

FLTurf 0.26 2 7 0.837 0.707 0.0609 0.1582 LS

PA Turf 0.26 2 7 1.102 0.985 0.0849 0.2204 LS

CA Turf 0.26 2 7 0.654 0.554 0.0478 0.1239 None

CA Nursery 0.4992 1 NA 5.663 4.672 0.4028 1.0452 RU,LS, Chronic

CA Residential 0.4992 1 NA 1.779 1.543 0.1330 0.3452 RU,LS

FL Nursery 0.4992 1 NA 9.785 8.136 0.7014 1.8201 RU,LS, Chronic

MI Nursery 0.4992 1 NA 2.508 2.284 0.1969 0.5110 RU,LS

TN Nursery 0.4992 1 NA 10.981 9.126 0.7867 2.0416 RU,LS, Chronic

1-Acute Toxicity Endpoint=11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.

7. Estuarine/Marine Fish

The conclusion of the risk assessment is that best available information indicates risks of 

direct effects to non-listed estuarine/marine fish are below Agency screening levels of 

concern.
9

8. Estuarine/Marine Invertebrates

The following table summarizes the proposed use sites associated with each model 

scenario and identifies the Agency concern levels exceeded. Risks to estuarine/marine 

invertebrates that exceed Agency concern levels are confined to the following Tier II 

modeling scenarios: FL cabbage (aerial or ground spray), FL cucumber (aerial or ground 

spray), FL peppers (aerial or ground spray), FL tomatoes (aerial spray), CA lettuce 

(ground and aerial spray), NC cotton (aerial or ground spray), MS cotton (aerial or 

ground spray) CA nursery (ground spray), TN nursery (ground spray), FL nursery

(ground spray), and MI nursery (ground spray). These risks are generally limited to acute 

effects to listed species. However, the restricted use LOCs are exceeded for the Florida 

vegetable scenarios (cucumber, peppers) and nursery use scenarios (CA nursery, TN 

nursery, and FL nursery scenarios). 

Tier II RQs for Estuarine/Marine Invertebrates from Aerial Spray Application of DPX-E2Y45 for 

Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lbs/A) # Int

FL cabbage 0.065 3 3 2.652 2.146 0.0538 0.0894 LS

FL cucumber 0.065 3 5 5.693 4.939 0.1238 0.2058 RU,LS

PA tomato 0.098 2 5 1.513 1.306 0.0327 0.0544 None

CA tomato 0.098 2 5 1.080 0.922 0.0231 0.0384 None

FL tomato 0.098 2 5 3.660 3.001 0.0752 0.1250 LS

FL peppers 0.098 2 5 6.749 5.683 0.1424 0.2368 RU,LS

CA lettuce 0.065 3 3 3.579 2.997 0.0751 0.1249 LS

CA cotton 0.099 2 5 1.785 1.576 0.0395 0.0657 None

NC cotton 0.099 2 5 3.730 3.207 0.0804 0.1336 LS

MS cotton 0.099 2 5 3.769 3.271 0.0820 0.1363 LS

NY grape 0.099 2 7 1.389 1.197 0.0300 0.0499 None

CA grape 0.099 2 7 1.188 1.026 0.0257 0.0428 None

NC apple 0.099 2 10 1.359 1.153 0.0289 0.0480 None

PA apple 0.099 2 10 1.245 1.091 0.0273 0.0455 None

OR apple 0.099 2 10 0.786 0.674 0.0169 0.0281 None

ID potato 0.066 3 5 1.021 0.859 0.0215 0.0358 None

ME potato 0.066 3 5 1.558 1.392 0.0349 0.0580 None

GA peach 0.099 2 7 1.086 0.886 0.0222 0.0369 None

MI Cherry 0.099 2 7 1.035 0.907 0.0227 0.0378 None

1-Acute Toxicity Endpoint= 39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
10

Tier II RQs for Estuarine/Marine Invertebrates from Ground Spray Application of DPX-E2Y45 for 

Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 2.045 0.0513 0.0852 LS

FL cucumber 0.065 3 5 5.624 4.86 0.1218 0.2025 RU,LS

PA tomato 0.098 2 5 1.280 1.097 0.0275 0.0457 None

CA tomato 0.098 2 5 0.731 0.619 0.0155 0.0258 None

FL tomato 0.098 2 5 3.436 2.817 0.0706 0.1174 None

FL peppers 0.098 2 5 6.501 5.475 0.1372 0.2281 RU,LS

CA lettuce 0.065 3 3 3.311 2.781 0.0697 0.1159 LS

CA cotton 0.099 2 5 1.470 1.28 0.0321 0.0533 None

NC cotton 0.099 2 5 3.473 2.995 0.0751 0.1248 LS

MS cotton 0.099 2 5 3.575 3.116 0.0781 0.1298 LS

NY grape 0.099 2 7 1.189 1.025 0.0257 0.0427 None

CA grape 0.099 2 7 0.813 0.706 0.0177 0.0294 None

NC apple 0.099 2 10 0.999 0.852 0.0214 0.0355 None

PA apple 0.099 2 10 1.048 0.898 0.0225 0.0374 None

OR apple 0.099 2 10 0.410 0.365 0.0091 0.0152 None

ID potato 0.066 3 5 0.812 0.68 0.0170 0.0283 None

ME potato 0.066 3 5 1.350 1.195 0.0299 0.0498 None

GA peach 0.099 2 7 0.763 0.62 0.0155 0.0258 None

MI Cherry 0.099 2 7 0.867 0.739 0.0185 0.0308 None

FLTurf 0.26 2 7 0.837 0.707 0.0177 0.0295 None

PA Turf 0.26 2 7 1.102 0.985 0.0247 0.0410 None

CA Turf 0.26 2 7 0.654 0.554 0.0139 0.0231 None

CA Nursery 0.4992 1 NA 5.663 4.672 0.1171 0.1947 RU,LS

CA Residential 0.4992 1 NA 1.779 1.543 0.0387 0.0643 None

FL Nursery 0.4992 1 NA 9.785 8.136 0.2039 0.3390 RU,LS

MI Nursery 0.4992 1 NA 2.508 2.284 0.0572 0.0952 LS

TN Nursery 0.4992 1 NA 10.981 9.126 0.2287 0.3803 RU,LS

1-Acute Toxicity Endpoint=39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
11

9. Assessment of Potential Effects to Federally Listed Threatened and Endangered Species

The following table summarizes the conclusions of potential concerns for direct and 

indirect effects to federally-listed threatened and endangered species (listed species).

Potential Effects to Federally Listed Taxa

Listed Taxa

Direct 

Effects

Scenario Identified as of 

Concern

Indirect

Effects

Scenario Identified as of 

Concern

Terrestrial and semiaquatic plants -

monocots

Yes4 Yes1all

Terrestrial and semiaquatic plants - dicots Yes4 Yes1

all

Terrestrial invertebrates Yes all No

Birds No Yes1,2,3,5 All 

Terrestrial phase 

amphibians No Yes1,2,5 All 

Reptiles No Yes1,2,3,5 All 

Mammals No Yes1,2,3,5 All 

Aquatic vascular plants No No

Freshwater fish No Yes2,5 All 

Aquatic phase 

amphibians No Yes2,5 All 

Freshwater crustaceans Yes

All except CA turf

(ground spray) and OR 

apple (ground spray)

Yes2,5 All

Mollusks

Yes(may be 

subject to 

further 

evaluation)

All except CA turf

(ground spray) and OR 

apple (ground spray) Yes2,5 All

Marine/estuarine fish No Yes3

FL cabbage, FL cucumber, 

FL pepper, NC cotton, MS 

cotton, CA lettuce, CA nursery, 

FL nursery, MI nursery, TN 

nursery

Marine/estuarine 

invertebrates Yes

FL cabbage, FL cucumber, 

FL pepper, NC cotton, MS 

cotton, CA lettuce, CA nursery, 

FL nursery, MI nursery, TN 

nursery

No

1 direct effects on terrestrial invertebrates

2 direct effects on aquatic invertebrates

3 direct effects on estuarine/marine invertebrates

4

insufficient data to preclude risk

5

direct effects to terrestrial plants at the listed species level of concern suggests concern of animals with obligate relationships to a 

plant species
12

II. PROBLEM FORMULATION

A. Nature of the Federal Action

DuPont crop protection is requesting an Agency decision regarding a FIFRA Section 3 

registration for the pesticide chlorantraniliprole. The nature of the uses of the pesticide 

under this proposed EUP is discussed in the Use Characterization section of this risk 

assessment.

B. Nature of the Chemical Stressor

The risk assessment addresses the active ingredient chlorantraniliprole. The following 

information summarizes basic chemical identity information for the active ingredient:

Chemical Name: 3-Bromo-N-[4-chloro-2-methyl-6- [(methylamino)

carbonyl]phenyl]-1-(3-chloro-2-pyridinyl)-1H-pyrazole-5-carboxamide

Empirical Formula: C18H14N5O2BrCl2

Molecular Weight: 483.15 g/mole

CAS No.: 500008-45-7 (chlorantraniliprole)

Common Name: chlorantraniliprole

Pesticide Type: Insecticide

Chemical Family: Anthranilic diamide

Physical State: Fine Crystalline Powder

Odor: No odor

pH: 5.77 ± 0.087 at 20oC

UV/Visible Absorption: A lambda max under basic conditions was ~320 nm. No 

defined lambda max, above 290 nm, under neutral or acidic conditions.

Melting Point: 208-210oC

Relative Density: 1.5070 at 20oC
13

Dissociation Constant in Water: pKa was approximately 10.88 ± 0.71 at 20°C

Partition Coefficient: Kow (20°C ) = 2.77 at pH 4, 2.86 at pH7 & 2.80 at pH9

Water Solubility: pH 4: 0.972 mg/L (CV = 1.9%) pH 7: 0.880 mg/L (CV = 1.3%) 

pH 9: 0.971 mg/L (CV = 3.8%)

Solubility in Organic Solvents at 20oC:

Acetone 3.446 g/l

Acetonitrile 0.711g/l

Ethyl acetate 1.144 g/l

Dichloromethane 2.476 g/l

Dimethylformamide 2.476 g/l

1-Octanol 0.386 g/l

Methanol 1.714 g/l

n-Hexane <0.0001 g/l

o-Xylene 0.162 g/l

Vapor Pressure (est.): 6.3 x 10-12 PA at20oC (2.1 x 10-11Pa at 25oC)

Henry’s Law Constant: 3.1 x 10-15 atm-m

3

/mol (20oC) (3.1 x 10-10 Pa-m

3

/mol)

The structure of the active ingredient is reported as follows:

N

N N

N

O

Cl

Br

N

O

Cl

While degradates have been identified, the available effects data indicate that their 

toxicity is lower than the parent, often by an order of magnitude. The greatest percentage

production of a degradate was for IN-LBA24, which was 90% of applied parent produced 

in the photodegradation study at a buffered pH of 7. Even at this maximum production 

of degradate, the low toxicity (one tenth that of parent) would not affect quantitative risk 

estimations to any significant degree, and it was assumed that further quantitative 

consideration of risks associated with degradates would not materially add to the 

confidence of the risk assessment conclusions. 
14

C. Use Characterization 

The following is as list of proposed crop uses: brassica (cole), leafy vegetables (broccoli, 

broccoli raab, Brussels sprouts, cabbage, Chinese cabbage, cauliflower, cavalo broccoli, 

collards, kale, kohlrabi, mizuna, mustard greens, mustard spinach, rape greens), 

curcurbits (vegetables, melons, squash), fruiting vegetables (eggplant, goundcherry, 

peppers, tomatoes), cotton, grape, pome fruits, potato, and stone fruits. The pesticide 

may also be applied to turf, and ornamental plants 

Chlorantraniliprole is proposed for the control of a variety of insect pests on crops

including beet armyworm, cotton bollworm, diamondback moth, cabbage looper, corn 

earworm, cross-striped cabbageworm, imported cabbage worm, melon worm, pickle 

worm, leaf miners, whiteflies (suppression only), hornworm, southern armyworm, salt 

marsh caterpillar, soybean looper, western yellow-striped armyworm, tomato fruit worm, 

European corn borer, garden webworm, tomato pinworm, grape berry moth, grape leaf 

roller, western grape skeletonizer, green fruit worm, spotted tentiform leafminer, codling 

moth, oriental fruit moth, tufted apple cut moth, white apple leafhopper, Colorado potato 

beetle, obliquebanded leafroller, peach twig borer, and southern armyworm. In addition 

to crop pests, chlorantraniliprole is proposed for control turf and ornamental plants pests 

including: armyworms, sod webworms, white grubs, European crane fly, billbugs, annual 

bluegrass weevil, spittle bugs, chinch bugs, bagworms, tussock moths, lace bugs, aphids, 

birch leafminer, and clearwing borers.

Proposed label application rates are presented in the following tables. They are 

influenced by product, application method (drip chemigation vs. foliar application), crop,

and target pest.

Proposed Labeled Use Rates for CoragenTM SC

Use Site Application Method Target Pest Application rate

(lb a.i./acre)

Number of 

Applications/ Interval

Brassica and 

leafy 

vegetables

drip chemigation beet armyworm diamondback moth 0.045-0.065 2 to 3 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval 

cabbage looper, corn earworm, 

cross-striped cabbage worm, 

imported cabbageworm

0.045-0.098

foliar (air or ground 

spray)

diamondback moth 0.026-0.045 4 to 7 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

beet armyworm, cabbage looper, 

corn earworm, cross-striped 

cabbage worm, imported 

cabbageworm

0.045-0.065 3 to 4 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

Cucurbits 

vegetables , 

melons, 

squash

drip chemigation melon worm 0.026-0.045 4 to 7 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

beet armyworm, cabbage looper, 

pickle worm

0.045-0.065 3 to 4 for maximum 

crop application of 0.2 
15

Proposed Labeled Use Rates for CoragenTM SC

Use Site Application Method Target Pest Application rate

(lb a.i./acre)

Number of 

Applications/ Interval

lb a.i./acre

10 day interval

leafminers, whiteflies 0.065-0.098 2 to 3 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

foliar (air or ground 

spray)

melon worm 0.026-0.045 4 to 7 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

beet armyworm, cabbage looper, 

pickle worm

0.045-0.065 3 to 4 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

leafminers, whiteflies 0.065-0.09 2 to 3 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

Fruiting 

vegetables, 

peppers, 

tomatoes

drip chemigation beet armyworm, hornworms, 

southern armyworm, western 

yellow striped armyworm

0.045-0.065 3 to 4 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

tomato fruitworm, loopers 0.045-0.09 2 to 4 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

european corn borer, garden 

webworm, leafminers, tomato 

pinworm, whiteflies

0.065-0.098 2 to 3 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

foliar (air or ground 

spray)

hornworms 0.026-0.065 3 to 7 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

beet armyworm, european corn 

borer, garden webworm, loopers, 

southern armyworm, tomato 

fruitworm, tomato pinworm, 

western yelowstriped armyworm

0.045-0.065 3 to 4 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval

leafminers, whiteflies 0.065-0.098 2 to 3 for maximum 

crop application of 0.2 

lb a.i./acre

5 day interval
16

Proposed Labeled Use Rates for AltacorTM WG

Use Site Target Pest Application rate

(lb a.i./acre)

Number of 

Applications/ Interval

Cotton beet armyworm, cotton bollworm, fall 

armyworm, saltmarsh caterpillar, 

southern armyworm, tobacco budworm

0.044-0.088 2 to 4 

applications/season for 

maximum crop 

application of 0.2 lbs 

a.i./acre

5 day interval

cabbage looper, soybean looper 0.066-0.099 2 to 3 

applications/season for 

maximum crop 

application of 0.2 lbs 

a.i./acre

5 day interval

Grape grape berry moth, grape leafroller 0.044-0.099 No more than 4 (2-4) 

applications/season no 

more than 0.2 lbs 

a.i./acre

7 day interval

omnivorous leafroller, western grapeleaf 

skeletonizer

0.066-0.099 No more than 4 (2-3) 

applications/season no 

more than 0.2 lbs 

a.i./acre

7 day interval

Pome fruits green fruitworm, spotted tentiform 

leafminer

0.044-0.088 2 to 3

applications/season for 

maximum crop 

application of 0.2 lbs 

a.i./acre

10 day interval

codling moth, obliquebanded leafroller, 

oriental fruit moth, tufted apple bud 

moth, white apple bud moth

0.066-0.099 2 t o 3 for maximum 

crop application of 0.2 

lb a.i./acre

10 day interval

Potato cabbage looper, Colorado potato beetle, 

European corn borer

0.044-0.066 3 to 4 

applications/season for 

maximum crop 

application of 0.2 lbs 

a.i./acre

5 day interval

Stone fruits Codling moth, obliquebanded leafroller, 

oriental fruit moth, peach twig borer, 

tufted apple bud moth

0.044-0.099 No more than 4 (3-4) 

applications/season no 

more than 0.2 lbs 

a.i./acre

7 day interval
17

Proposed Labeled Use Rates for E2Y45 SC

Use Site Application Method Target Pest Application 

rate

(lb a.i./acre)

Number of 

Applications/ 

Interval

Turf (lawns, 

golf courses, 

and other 

recreational 

turfgrass 

areas

Ground spray lepidoptera 0.026-0.052 9 to 19

maximum annual 

application of 0.5 lbs 

a.i./acre

no interval specified

white grubs, european crane fly, 0.104-0.208 2 to 4

maximum annual 

application of 0.5 lbs 

a.i./acre

no interval specified

billbugs, cinch bugs 0.104-0.26 1-4

maximum annual 

application of 0.5 lbs 

a.i./acre

no interval specified

annual bluegrass weevil, 

spittlebugs

0.157-0.26 1-3

maximum annual 

application of 0.5 lbs 

a.i./acre

no interval specified

Ornamental 

plants

foliar spray Leaf-feeding caterpillars 0.4992 Application numbers 

specified “as needed” 

with 5-day intervals 

However, maximum 

annul application of 

0.5 lbs a.i./acre would 

suggest only 1 

application allowable

soil treatment (drench or soil 

injection)

bark treatment

Lace bugs, aphids, birch leaf miner

clearwinged borers

Unspecified in 

accessible units

Application numbers 

specified “as needed” 

with 5-day intervals 

However, maximum 

annual application of 

0.5 lbs a.i./acre

Ornamental 

flowers and 

ground 

cover

soil treatment White grubs 0.104-0.208 2 to 4

applications/year for 

maximum annual

application of 0.5 lbs 

a.i./acre

5 day interval

Stone fruits Codling moth, obliquebanded 

leafroller, oriental fruit moth, 

peach twig borer, tufted apple bud 

moth

0.044-0.099 No more than 4 (2-4) 

applications/season no 

more than 0.2 lbs 

a.i./acre

7 day interval
18

D. Ecological Receptors Considered in this Risk Assessment

The screening level risk assessment approaches the analysis for adverse effects 

commonly through the use of broad plant and animal taxonomic groups including:

• Birds (also used as surrogate for terrestrial-phase amphibians and reptiles),

• Mammals,

• Terrestrial plants,

• Freshwater fish (also used as a surrogate for aquatic phase amphibians),

• Freshwater invertebrates (including sediment-dwelling species),

 Estuarine/Marine Fish

 Estuarine/Marine Invertebrates

• Algae and vascular aquatic plants

Because of known effects of chlorantraniliprole to arthropods pests, the risks of the

insecticide to non-target terrestrial invertebrates will also be evaluated, but without the 

benefit of Agency established concern thresholds to aid in interpretation of assessment 

results.

E. Exposure Pathways Considered for Terrestrial Organisms

For the purposes of this risk assessment, terrestrial non-target organisms are assumed to 

occupy areas immediately adjacent to treatment sites. The exposure pathways analyzed 

in this risk assessment for terrestrial vertebrate wildlife include dietary uptake of food 

items directly treated with the pesticide at the time of application to the treated field. 

Exposures are calculated on a dietary basis alone. Dose-based exposures are not 

considered due to no evidence of acute oral toxicity. Accumulation from soil to plants or 

animal food sources is not considered in this risk assessment. The very low 

octanol/water partitioning coefficient (log Kow =2.90) suggests that bioaccumulation is 

not likely. Inhalation of vapor phase pesticide is not considered quantitatively in this risk 

assessment. The low vapor pressure of the parent compound (6.3 x 10-12 PA) suggests 

that the pesticide does not readily volatilize and the rat acute inhalation LC50: >5.1 mg/L 

suggests that what little material that would volatilize would not be of significant toxicity. 

Dermal exposure (contact with deposited residues and impingement of spray droplets) for 

terrestrial vertebrates is not considered quantitatively. The low octanol/water partitioning 

coefficient would suggest little potential to cross the dermal barrier, a conclusion

supported by the demonstrated low dermal acute toxicity in the rat (LD50: >5000 mg/kg). 

Other routes of exposure for terrestrial wildlife that are possible but not considered in this 

risk assessment include drinking water exposure, inhalation of pesticide associated with 

suspended soil particulate, inhalation of spray droplets, and oral ingestion of soil particles 

through incidental contact while feeding and preening.
19

Terrestrial plant exposures considered potentially complete for this pesticide include 

exposure of vegetation adjacent to treatment sites via drift, sheet flow runoff, and runoff 

to drainage channels. Drift exposures are considered important to effects measures 

involving direct application to leaf surfaces (e.g. vegetative vigor studies). Drift and 

runoff exposures are also comparable to effects endpoints associated with application of 

pesticide to soil (e.g. seedling emergence studies).

F. Exposure Pathways Considered for Aquatic Organisms

For the purposes of this risk assessment aquatic non-target organisms are assumed to 

occupy a surface water body immediately adjacent to treatment sites. The likely 

pathways for introduction of the chemical stressor to this aquatic water body include:

 direct deposition of applied product through spray drift

 mass transport of chemical stressor dissolved in run-off from the treated field, 

and

 mass transport of chemical stressor adsorbed to eroded solids from the treated 

field.

Once pesticide enters the receiving waters, exposure it likely most significant through 

absorption of dissolved pesticide from the water column or interstitial water across the 

gill, integument, and perhaps the gut of the organism. Food chain exposures are not 

considered to be significant for this pesticide because chlorantraniliprole has a low fish 

bioconcentration factor of <21.

G. Conceptual Model

1. Risk Hypothesis 

The risk hypothesis for this screening-level risk assessment is as follows:

Chlorantraniliprole, used in accordance with the Section 3 labels, results 

in adverse effects upon survival and reproduction of non-target terrestrial 

and aquatic organisms. 
20

2. Conceptual Diagram 

The following is a conceptual plan diagram depicting sources of exposure, potential 

receptors and adverse effects proposed uses of chlorantraniliprole

H. Analysis Plan

H. Analysis Plan

1. Preliminary Identification of Data Gaps and Methods

a. Fate Testing

There were no identified data gaps in the fate data. Under international agreements the 

Agency was not responsible for conducting environmental fate data reviews. Data 

review is being conducted for use by all parties to the international agreement by the 

Pesticide Control Service, Department of Agriculture and Food, Ireland. The Agency is 

using the results of the PSD review as they appear in the dossier for registration in 

Europe except for the aerobic soil metabolism half-lives. EFED recalculated aerobic soil 

metabolism half-lives for chlorantraniliprole to be representative of the total extractable 

fraction in soil. 
21

b. Effects Testing

There were no data gaps in the effects data. In agreement with international 

governmental partners associated with registration efforts for this pesticide, ecological 

effects data evaluation responsibilities are being met through the efforts of the Pesticides 

Safety Directorate (PSD), UK. The Agency is using the results of the PSD review as they

appear in the dossier for registration in Europe. Except where specifically reported,

independent validation of statistical results for effects studies was not performed during 

the PSD reviews.

2. Assessment Endpoints

Assessment endpoints for this screening-level ecological risk assessment are reduced 

survival, reproduction output, and growth of individual organisms. These assessment 

endpoints, while measured at the individual level, provide insight about risks at higher 

levels of biological organization (e.g., populations). It is assumed that toxicants do not 

affect populations or communities except through the impact on the individuals 

comprising the population or community and the demographics of birth, growth, and 

death that govern population dynamics. The number of individuals within a population 

change (intrinsic rate of increase) primarily because of births (fecundity) and deaths 

(survival) and secondarily from migration in and out of a specific area. If effects on the 

survival and reproduction of individuals are limited, it is assumed that risks at the 

population level from such effects will be of minor consequence. However, as the risk of 

reductions in survival and/or reproduction rates increases, so does the potential risk to 

populations.

3. Exposure Measures

Exposures estimated in the screening-level risk assessment for non-target organisms are 

not species specific.

For estimating exposures of aquatic organisms to chlorantraniliprole, the risk assessment 

will use the PRZM/EXAMS modeling shell (PE5V01). Inputs for this model are 

presented in the Environmental Fate and Transport Characterization section of this risk 

assessment. The screening risk assessment commonly uses estimates of the dissolved 

concentration of the pesticide over a single day, 21-day, and 60-day averaging periods 

and the exposure measurement point is that averaging period corresponding to a one in 

ten year return frequency for estimating exposure to water column dwelling organisms. 

This modeling effort focuses on aerial and ground applications only, chemigation and 

injection are not included specifically as there are not adequate modeling scenarios. It is 

expected that over the top aerial and ground applications are adequate to represent 

injection and chemgation. This risk assessment will use this approach, although the 

results are likely to be overestimates of exposure for such a stable compound as 

chlorantraniliprole because the model uses up to 36 years of application events. 
22

Dietary exposures for terrestrial vertebrates are estimated using the T-REX model version 

1.3.1. Inputs for this model are presented in the Environmental Fate and Transport 

Characterization section of this risk assessment. The exposure endpoint for terrestrial 

vertebrates from the T-REX model’s output corresponds to an upper bound single day

peak concentration of pesticide in each of four generalized dietary items. These pesticide 

concentration estimates are then used for either direct comparison with dietary effects 

endpoints or first converted to daily oral dose estimates for feeding wildlife and then 

compared to daily dose effects endpoints. Mean concentrations associated with a peak 

pesticide residue estimate may be used in the risk characterization to provide additional 

context to risk assessment conclusions. However, the results of the initial screen for 

chlorantraniliprole indicate that this additional step will not be required for this case.

For terrestrial vertebrate risks the T-REX model was used with an assumption of a 

maximum 0.5 lb ai/acre single application rate. This is highest application rate from the

proposed labels. The assumption of a single maximum application at the labeled crop 

limit also will allow for consideration of the potential for systemic uptake of the 

pesticide, which is suggested by the following label statement “DupontTM E2Y45SC 

insecticide is a systemic product and will be transmitted upward into the plant from 

root uptake.” If no Agency risk concerns are identified at this conservative level, no 

further refinement would be warranted.
23

4. Effects Measures

The screening-level risk assessment typically relies on a suite of toxicity studies 

performed on a limited number of organisms from broad taxonomic groups that are used 

as surrogates for a variety of taxa. The following presents the tested taxonomic group, its 

target taxa as a surrogate, and the effects measures commonly used in screening risk 

assessment

Tested Surrogate Effects Measures Employed

Taxa For

Birds all birds bird, reptiles, and most sensitive species tested

terrestrial amphibians LD50, LC50, NOAEC for 

reproduction and growth

Mammals (rat) all mammals LD50, NOAEL for 

reproduction and growth

Freshwater fish all fish aquatic amphibians most sensitive species tested

LC50, NOAEC for 

reproduction and growth

Freshwater all freshwater invertebrates most sensitive species tested

invertebrates LC50, NOAEC for 

reproduction and growth

Estuarine/marine all estuarine/marine most sensitive species tested

Fish fish LC50, NOAEC for 

reproduction and growth

Estuarine/marine all estuarine/marine most sensitive species tested

invertebrates invertebrates LC50, NOAEC for 

reproduction and growth

Terrestrial all terrestrial invertebrates LD50

Invertebrate (not commonly a quantitative risk assessment)

Terrestrial plants all terrestrial plants most sensitive species tested 

(monocot/dicot) of monocot and dicot EC25, 

EC5/NOAEC

Aquatic Plants all aquatic plants most sensitive species tested 

(algae/vascular) of algae and vascular EC50/EC25, 

EC5/NOAEC
24

IV. ANALYSIS

A. Environmental Fate and Transport Characterization

Chlorantraniliprole is persistent and mobile in terrestrial and aquatic environments. 

Extended chlorantraniliprole use is expected to cause accumulation of residues in soil

from year to year. Major routes of dissipation are expected to be alkaline-catalyzed 

hydrolysis, photodegradation in water, leaching, and runoff.

Chlorantraniliprole is stable to hydrolytic degradation in pH 5 and 7 buffer solutions. It 

does, however, undergo rapid hydrolysis in pH 9 buffer solution (MRID 46889017). The 

major hydrolysis degradation product is (2-[3-Bromo-1-(3-chloro-2-pyridinyl)-1Hpyrazol-5-yl]-6-chloro-3,8 dimethyl-4(3H)-quinazolinone (IN-EQW78). 

Photodegradation of chlorantraniliprole is a predominant degradation pathway. 

Chlorantraniliprole has a half-life of 0.37 days in pH 7 buffer solution and 0.31 days in 

natural water irradiated with a Xenon arc lamp (MRID 46889018). In a water/sediment 

system, chlorantraniliprole had photodegradation half-lives of 22 days in loamy sand 

sediment and 9.9 days in sandy loam sediment system (MRID 46889122). The major 

photodegradation products are IN-EQW78, IN-LBA22, IN-LBA24, and IN-LBA23. A 

minor photodegradation product was identified as IN-ECD73. 

Chlorantraniliprole is stable (t1/2 = 228 to 924 days) in aerobic soils incubated at 250C 

(MRID 46889015, 46889014, 46889124). It degrades faster at higher soil temperatures 

of 34-350C and 490C (MRID 46889124, 46889015). Major degradation products were 

identified as IN-F6L99, IN-EVK64, IN-EQW78, IN-ECD73, IN-GAZ70. Minor 

degradation products were identified IF-F9N04 and IN-EVK64. Chlorantraniliprole is 

also persistent (t1/2= 231 and 125 days) under stratified redox test conditions in a sand and 

loam sediment/water systems (MRID 46889016). The major degradation product was 

identified as IN-EQW78. Minor degradations products were identified as IN-F6L99, INF9N04, IN-GAZ70, and IN-ECD73. 

Chlorantraniliprole is expected to be mobile in soil and aquatic environments. It has soil: 

water Freundlich batch equilibrium adsorption coefficients of 1.22 (Koc=153, 

1/n=1.0028) in a loamy sand from Spain, 9.16 (Koc=509, 1/n=1.0434) in a silty clay loam 

from IA, 1.36 (Koc=272, 1/n=0.8485) in a sandy loam from MS, 1.59 (Koc= 526, 

1/n=0.9370) in a loamy sand from GA, 2.34 (Koc=180, 1/n=0.9256) in a loam from Italy

(MRID 46889123). Because there is a positive, linear regression between Kd and soil 

organic carbon, it is appropriate to use Koc for environmental fate modeling.
25

Laboratory Environmental Fate Data for Chlorantraniliprole

Data Units Value Source 

Molecular Weight g/mole 483.15

Solubility mg/L 1.023 MRID 46889026

Vapor Pressure Torr 1.57E-13 DuPont 16517

Henrys Constant atm

m

3

/mol

3.1E-15 Estimated

Hydrolysis @ pH 7 Days Stable MRID 46889017

Photodegradation in 

Water

Days 0.31 MRID 46889018

Aerobic Soil Metabolism Days 577.61

537.3

374.6 

410.1

246.6

228.0

888.6

924.1

396.0

MRID 46889124

MRID 46889015

MRID 46889124

(Total Soil Extractable 

Residue @ 25oC) for benzo 

and pyrazole-labeled 

chlorantraniliprole

Aerobic Aquatic 

Metabolism

Days 231

125

MRID 46889016

Anaerobic Aquatic

Metabolism

Days 208 DuPont 14568

Soil:Water Coefficients

(Average Koc)

L/g 153-loam sand

509-silty clay loam

272-sandy loam

526-loamy sand

180-loam

MRID 46889123

1- EFED recalculated first-order half-lives for both benzo- and pyrazole-labeled chlorantraniliprole. Half-lives values presented in the 

OECD Chlorantranilipole Volume 3(1): Annex B, Environmental Fate and Behavior. (mean = 491 (886, 539, 380, 233, 323, 629, 423, 

518 days); SD=203; t90, n-1 =1.417; N=8)
26

The following table presents the degradates associated with each fate study. Structures of 

the degradates, when available are appended to this risk assessment.

Study Degradation 

Product

Maximum Formation 

Percentage

(% of applied parent) 

Chemical Name

Hydrolysis

MRID 46889212

IN-EQW78 86.7 @ pH 9 (2-[3-Bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-3,8 dimethyl-4(3H)-

quinazolinone

Photodegradation 

in Water

MRID 46889018

IN-EQW78 ND @ pH 7 buffer solution

ND @ natural water, sterile

(2-[3-Bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-3,8 dimethyl-4(3H)-

quinazolinone

IN-LBA22 52.1 @ pH 7 buffer solution

3.4 @ natural water, sterile

IN-LBA24 90.2 @ pH 7 buffer solution

89.3 @ natural water, sterile

IN-LBA23 40.8 @ pH 7 buffer solution

51.4 @ natural water, sterile

Soil Metabolism

MRID 46889014

MRID 46889124

MRID 46889015

IN-F6L99 2.1 @ 250C incubation

5.2 @ 350C incubation

4.2 @ 490C incubation

N-Methyl-[3-bromo-1Hpyrazol-5-yl]carboxylic acid

IN-EVK64 ND @ 250C incubation

1.7 @ 350C incubation

5.3 @ 490C incubation

IN-EQW78 9.5 @ 250C incubation

33.3 @ 350C incubation

71.6 @ 490C incubation

(2-[3-Bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-3,8 dimethyl-4(3H)-

quinazolinone

IN-ECD73 4.9 @ 250C incubation

8.2 @ 350C incubation

9.1 @ 490C incubation

2-[3-bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazole-5-yl]-6-

chloro-3,8-dimethyl-4(3H)-

quinazolinone

INGAZ70 4.3 @ 250C incubation

7.4 @ 350C incubation

1.0 @ 490C incubation

2-[3-bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-8-methyl-4(1H)-

quinazolinone

Water/Sediment

Metabolism

MRID 46889016

MRID 46889122

IN-EQW78 30.2 @ no photodegradation

40.9 @ photodegradation

(2-[3-Bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-3,8 dimethyl-4(3H)-

quinazolinone

IN-F6L99 4.2 @ no photodegradation

ND @ photodegradation

5-bromo-N-methyl-1Hpyrazole-3-carboxamide

IN-F9N04 2.7 @ no photodegradation

ND @ photodegradation

N-[2-(Aminocarbonyl)-4-

chloro-6-methylphenyl]-3-

bromo-1-(3-chloro-2-

pyridinyl)1H-pyrazole-5-

carboxamide

IN-GAZ70 3.0 @ no photodegradation 2-[3-bromo-1-(3-chloro-2-
27

Study Degradation 

Product

Maximum Formation 

Percentage

(% of applied parent) 

Chemical Name

ND @ photodegradation pyridinyl)-1H-pyrazol-5-yl]-6-

chloro-8-methyl-4(1H)-

quinazolinone

IN-ECD73 4.7 @ no photodegradation

0.8 @ photodegradation

2-[3-bromo-1-(3-chloro-2-

pyridinyl)-1H-pyrazole-5-yl]-6-

chloro-3,8-dimethyl-4(3H)-

quinazolinone

INLBA22 11.1 @ no photodegradation

ND @ photodegradation

INLBA24 4.6 @ no photodegradation

1.5 @ photodegradation

INLNA23 2.3 @ no photodegradation

0.5 @ photodegradation

Radiolabelled chlorantraniliprole (applied at 0.286 lbs ai/A ) had half-lives of 181 to 222 

days for dissipation studies in CA and Texas bareground field dissipation studies. In the 

Texas study, degradation products include IN-EQW78 (42% of applied @ Day 450), INGAZ70 (7% of applied radioactivity), IN-ECD73 (9.5%@ Day 540), IN-F6L99 (5% @ 

Day 120). Most of radioactivity was detected in the surface 0 to 6 inch soil layer. In the 

California study, degradation products include IN-EQW78 (29% of applied @ Day 741), 

IN-ECD73 (6.8% of applied radioactivity@ Day 740), IN-GAZ70 (5.9%@ Day 300), INF6L99 (2.1% @ Day 531). Applied radioactivity was detected with soil depth. 

Maximum depth of radioactivity detection was 30-36 inches soil layer (2.7% of applied 

radioactivity @ Day 379).

Nonradiolabelled chlorantraniliprole (formulated as 35WG at 0.286 lbs ai/A) had halflives of 210 days in Minnesota study and 274 days in Prince Edward Island study. In the 

Minnesota study, degradation products included IN-EQW78 ( 3.8% of applied @ Day

0), IN-ECD73 (4.1%@ Day 0) and IN-GAZ70 (4.1% day Day 0). Routes of dissipation 

for chlorantraniliprole were identified as leaching (1% of applied @ 12 to 30 inches) and 

runoff (<6% of applied). In the Prince Edward study, IN-EQW78 (5.3% of applied @ 

Day 0), IN-ECD73 (1.3%@ Day 0) and IN-GAZ70 (0.4% day Day 0). 

Chlorantranilipole was detected (<0.5% of applied) at soil depths greater than 30 cm. 

Nonradiolabelled chlorantraniliprole (formulated as 20SC at 0.286 lbs ai/A) on 

bareground plots had half-lives of 52 days in California study, 206 days in the Texas 

study, 697 days in the New Jersey study, and 1130 days in the Georgia study. In the 

California study, degradation products included IN-EQW78 ( 21% of applied @ Day

540) and IN-ECD73 (4.0%@ Day 540). Chlorantranilipole residues were detected at 

depth 18 inches (45 cm). In the Texas study, degradation products included IN-EQW78 

(20% of applied @ Day 540) and IN-ECD73 (2%@ Day 540). Chlorantranilipole 

residues were detected at depths >24 inches (<0.8% of applied). In the New Jersey study, 

degradation products included IN-EQW78 (9% of applied @ Day 475) and IN-ECD73 

(4%@ Day 541). Chlorantranilipole residues were detected at depths > 24 inches (1% of 

applied). In the Georgia study, degradation products included IN-EQW78 (12% of 
28

applied @ Day 540) and IN-ECD73 (6%@ Day 540). Chlorantranilipole residues were 

detected at depths 12 to 18 inches (~0.33 % of applied). 

1. Aquatic Organism Exposure

The aquatic exposure assessment for 3-bromo-N-[4-chloro-2-methyl]-6-[(methylamino) 

carbonyl]phenyl]-1-(3-chloro-2-pyridinyl)-[H-pyrazole-5-carboxamide 

(chlorantraniliprole) was conducted using registrant submitted data. The aquatic 

exposure assessment is based on Tier II surface water modeling (PRZM-EXAMS shell, 

PE5V01). The modeling was conducted using registrant-submitted environmental fate 

data. 

The surface water modeling was conducted using PE5V01. The modeling was conducted 

for only chlorantraniliprole. The modeling strategy was designed to assess major crops 

and application conditions specified in the Section 3 for chlorantraniliprole. 
29

a. Surface Water

The PRZM/EXAMS input parameters for chlorantraniliprole are shown in the table 

below.

PRZM/EXAMS Input Parameters for Chlorantraniliprole

Data Units Value Source Comments

Molecular Weight g/mole 483.15

Solubility mg/L 1.023 MRID 46889026

Vapor Pressure Torr 1.57E-13 DuPont 16517

Henrys Constant atm m3/mol 3.1E-15 Estimated Calculated via 

solubility and vapor 

pressure

Hydrolysis @ pH 7 Days Stable MRID 46889017

Photodegradation in 

Water

days 0.31 MRID 46889018

Aerobic Soil Metabolism Days 631.762,3 MRID 46889124

MRID 46889015

MRID 46889124

Calculated 90th

percentile of mean1

Mean= 509 days 

SD= 252 days

t= 1.40

n= 9

*Several reported 

half-lives in MRID 

46889124

were not used 

because of poor fit 

with first-order 

degradation model 

Aerobic Aquatic 

Metabolism

Days 341.13 MRID 46889016 Calculated 90th

percentile of mean1

Mean= 178 days 

SD= 74.95 days

t= 3.078

n=2

Anaerobic Aquatic

Metabolism

Days 208 DuPont 14568 Value represents 

single half-life value4

Soil:Water Coefficient 

(Koc)

L/g 328 MRID 46889123 Average Koc

1 tinput=Mean+(t90,n-1*SD)/√N-1

2- EFED recalculated first-order half-lives for both benzo- and pyrazole-labeled chlorantraniliprole. The calculated half-lives are 

based on aerobic soil metabolism data in non-sterile soil at 250C. Half-lives used in the assessment include 577.6, 537.3, 374.6, 410.1, 

246.6, 228, 888.6, 924.1, 396 days. 

3- The 90th percentile of the mean half-life for chlorantraniliprole was 600 days for half-lives values presented in the OECD 

Chlorantranilipole Volume 3(1): Annex B, Environmental Fate and Behavior. (mean = 491 ( 886, 539, 380, 233, 323, 629, 423, 518 

days); SD=203; t90, n-1 =1.417; N=8)

4- A single value half-life was used because of the insensitivity of PRZM/EXAMS modeling to anaerobic aquatic metabolism halflives. 

The Agency does not have exposure scenarios for aquatic modeling for all use sites and 

locations in the country. Therefore, Agency risk assessments rely on a series of 

representative model scenarios to represent a suite of use sites and locations. Because 
30

the proposed chlorantraniliprole labels propose a range of application rates with various 

application approaches and crops, EFED conducted a comprehensive modeling analysis 

of the recommended application conditions for chlorantraniliprole. This analysis 

provides a series of possible use scenarios to assess the impact of application rate, 

application method, and crop on DPX-E2Y45 concentrations in surface water. 

Application conditions considered in the modeling are in the following table.

Application Conditions of Chlorantraniliprole for Various Crop Types (Maximum Application Rate)

Scenario Application 

Method

Single Application 

Rate

(lbs ai/A)

Number of 

Applications 

Application 

Interval

(days)

Annual 

Application 

Rate

(lbs ai/A)

DuPontTMCorgenTMSC

FL cabbage Aerial/Ground

Spray

0.065 3 3 0.20

FL cucumber 0.065 3 5 0.20

PA tomato 0.098 2 5 0.20

CA tomato 0.098 2 5 0.20

FL tomato 0.098 2 5 0.20

FL peppers 0.098 2 5 0.20

CA lettuce 0.065 3 3 0.20

DuPontTMAltacorTM WG

CA cotton Aerial/Ground

Spray

0.099 2 5 0.20

NC cotton 0.099 2 5 0.20

MS cotton 0.099 2 5 0.20

NY grape 0.099 2 7 0.20

CA grape 0.099 2 7 0.20

NC apple 0.099 2 10 0.20

PA apple 0.099 2 10 0.20

OR apple 0.099 2 10 0.20

ID potato 0.066 3 5 0.20

ME potato 0.066 3 5 0.20

GA peach 0.099 2 7 0.20

MI cherry 0.099 2 7 0.20

DuPontTME2Y45 SC

Turf Ground Spray 0.26 2 7 0.5

Turf Ground Spray 0.026 19 7 0.5

Ornamental 

Flowers and 

Groundcover

Ground Spray

0.4992 1 NA 0.5

NA- not applicable
31

Tier II aquatic EECs for maximum chlorantraniliprole application rates are shown in the 

next two tables.

PRZM/EXAMS EECs for Application Conditions of Chlorantraniliprole for Various Crop 

Types (Maximum Aerial Application Rate)

Scenario

Application 

Rate

(lbs ai/A)

#

Apps

Application 

Interval

(days)

1 in 10 year Concentration

(μg/L)

Peak 21-day

average

60-day

Average

FL cabbage 0.065 3 3 2.652 2.146 1.466

FL cucumber 0.065 3 5 5.693 4.939 3.748

PA tomato 0.098 2 5 1.513 1.306 1.136

CA tomato 0.098 2 5 1.080 0.922 0.702

FL tomato 0.098 2 5 3.660 3.001 2.312

FL peppers 0.098 2 5 6.749 5.683 4.425

CA lettuce 0.065 3 3 3.579 2.997 2.203

CA cotton 0.099 2 5 1.785 1.576 1.229

NC cotton 0.099 2 5 3.730 3.207 2.584

MS cotton 0.099 2 5 3.769 3.271 2.633

NY grape 0.099 2 7 1.389 1.197 1.041

CA grape 0.099 2 7 1.188 1.026 0.791

NC apple 0.099 2 10 1.359 1.153 0.917

PA apple 0.099 2 10 1.245 1.091 0.857

OR apple 0.099 2 10 0.786 0.674 0.558

ID potato 0.066 3 5 1.021 0.859 0.707

ME potato 0.066 3 5 1.558 1.392 1.319

GA peach 0.099 2 7 1.086 0.886 0.655

MI Cherry 0.099 2 7 1.035 0.907 0.758
32

PRZM/EXAMS EECs for Application Conditions of Chlorantraniliprole for Various Crop 

Types (Maximum Ground Application Rate)

Scenario

Application 

Rate

(lbs ai/A)

#

Apps

Application 

Interval

(days)

1 in 10 year Concentration

(μg/L)

Peak 21-day

average

60-day

Average

FL cabbage 0.065 3 3 2.531 2.045 1.331

FL cucumber 0.065 3 5 5.624 4.860 3.695

PA tomato 0.098 2 5 1.280 1.097 0.914

CA tomato 0.098 2 5 0.731 0.619 0.473

FL tomato 0.098 2 5 3.436 2.817 2.198

FL peppers 0.098 2 5 6.501 5.475 4.234

CA lettuce 0.065 3 3 3.311 2.781 2.057

CA cotton 0.099 2 5 1.470 1.280 1.005

NC cotton 0.099 2 5 3.473 2.995 2.440

MS cotton 0.099 2 5 3.575 3.116 2.469

NY grape 0.099 2 7 1.189 1.025 0.889

CA grape 0.099 2 7 0.813 0.706 0.550

NC apple 0.099 2 10 0.999 0.852 0.689

PA apple 0.099 2 10 1.048 0.898 0.716

OR apple 0.099 2 10 0.410 0.365 0.304

ID potato 0.066 3 5 0.812 0.680 0.513

ME potato 0.066 3 5 1.350 1.195 1.092

GA peach 0.099 2 7 0.763 0.620 0.447

MI Cherry 0.099 2 7 0.867 0.739 0.596

FLTurf 0.26 2 7 0.837 0.707 0.531

FL Turf 0.026 19 7 0.753 0.644 0.488

PA Turf 0.26 2 7 1.102 0.985 0.769

PA Turf 0.026 19 7 1.624 1.357 1.023

CA Turf 0.26 2 7 0.654 0.554 0.416

CA Turf 0.026 19 7 0.766 0.669 0.544

CA Nursery 0.4992 1 NA 5.663 4.672 3.495

CA Residential 0.4992 1 NA 1.779 1.543 1.385

FL Nursery 0.4992 1 NA 9.785 8.136 6.203

MI Nursery 0.4992 1 NA 2.508 2.284 2.033

TN Nursery 0.4992 1 NA 10.981 9.126 6.778

NA- not applicable
33

b. Monitoring Data

There are no surface or groundwater water monitoring data for chlorantraniliprole

because it is a new compound

2. Terrestrial Vertebrate Exposure

Terrestrial vertebrate exposures were estimated using the T-REX v 1.3.1 model. Because 

of the very low toxicity of chlorantraniliprole to mammals and birds, the risk assessment 

considered exposure estimates only for a highly conservative assumed maximum single 

use scenario (0.5 lbs ai/acre). A default dissipation half-life value of 35 days was 

assumed, though it has no impact on peak residue estimates for a single application 

scenario The following table shows the results of the exposure estimate.

T-REX Predicted Dietary EECs for a One-Time Conservative 

Application of 0.5 lb ai/acre

Dietary-based EECs (mg/kg-diet)

Short Grass 120.0

Tall Grass 55.0

Broadleaf plants/sm Insects 67.5

Fruits/pods/seeds/lg Insects 7.5

3. Terrestrial Invertebrate Exposure

The Agency currently has no method for estimating exposure to non-target terrestrial 

invertebrates.

4. Terrestrial Plant Exposure

Exposures for terrestrial plants were estimated using the TERRPLANT model. The low 

water solubility of chlorantraniliprole leads to the use of a runoff factor of 0.01 in the 

model. Because of the low expected toxicity of the pesticide to terrestrial plants, the 

exposure estimates presented in the table below are based on a maximum single 

application rate for both aerial and ground methods. Four application methods were 

considered ground spray application (0.5 lb/acre, 560 g/ha) to turf with no soil 

incorporation, ground spray application (0.5 lb/acre, 560 g/ha) to ornamentals with soil 

incorporation to 6 inches depth (surrogate for soil injection), foliar spray application (0.2 

lb/acre, 114 g/ha) with ground equipment and no incorporation, foliar spray application 

(0.2 lb/acre, 114 g/ha) with aerial equipment and no incorporation. In all cases the 

solubility limit of the pesticide was entered into the model as 0.88 mg/L (pH 7).
34

Estimated Plant Exposures Under Maximum Single Application Scenarios 

Application 

Method/Rate

Total Loading to 

Adjacent Areas 

(EEC = Sheet 

Runoff +Drift)

g ai/ha

Total Loading to 

Semi-aquatic 

Areas (EEC = 

Channelized 

Runoff + Drift) 

g ai/ha

DRIFT EEC 

(for ground: 

application rate x 

0.01) (for aerial: 

application rate x 

0.05)

g ai/ha

Ground Spray to 

Turf and 

ornamentals

Unincorporated/560

g/ha

11.2 61.6 5.6

Ground Spray to 

Turf and 

ornamentals

Incorporated to six 

inches/560 g/ha

6.5 14.9 5.6

Aerial spray 

unincorporated /224

g/ha

13.44 33.6 11.2

Ground spray

unincorporated /224 

g/ha 

4.48 24.64 2.24

B. Effects Characterization

In agreement with international governmental partners associated with registration efforts 

for this pesticide, ecological effects data evaluation responsibilities are being met through 

the efforts of the Pesticides Safety Directorate (PSD), UK. The Agency is using the 

results of the PSD review as they appear in the dossier for registration in Europe. Except 

where specifically reported, independent validation of statistical results for effects studies 

was not performed during the PSD reviews.
35

1. Avian Toxicity

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume. Chlorantraniliprole, degradates and formulated products can be characterized as 

being practically non-toxic from the acute oral and dietary perspectives.

Available Bird Toxicity Data for Chlorantraniliprole, Formulations, and Degradates

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type Endpoint Type

Effects 

Value 

Based 

on A.S.

Units of 

Active 

Substance

Chlorantraniliprole

Technical Technical

DuPont14380

Anas 

platyrhynchos

(Mallard)

Subacute

dietary

LC 50

NOAEC

>5620

5620 mg/kg diet

Chlorantraniliprole

Technical Technical

DuPont14384

Anas 

platyrhynchos

(Mallard) Reproduction

LOAEC (viable 

embryo 

reduction)

NOAEC

250

500 mg/kg diet

Chlorantraniliprole

Technical Technical

DuPont14378

Colinus 

virginianus

(Northern 

bobwhite)

Acute oral 

dose

LD 50

NOAEL 

>2250

2250 mg/kg bw

Chlorantraniliprole

Technical Technical

DuPont14379

Colinus 

virginianus

(Northern 

bobwhite)

Subacute

dietary

LC 50

NOAEC)

>5620

5620 mg/kg diet

Chlorantraniliprole

Technical Technical

DuPont14383

Colinus 

virginianus

(Northern 

bobwhite) Reproduction

LOAEC

(egsheell 

thinning)

NOAEC

250

120 mg/kg-diet

IN-EQW78

Technical 

metabolite

DuPont18859

Colinus 

virginianus

(Northern 

bobwhite)

Acute oral

dose

LD 50

NOAEL

>2250

2250

mg INEQW78/kg 

bw

Chlorantraniliprole

20SC

Formulated 

Product

DuPont18945

Colinus 

virginianus

(Northern 

bobwhite)

Acute oral

dose

LD 50

NOAEL(transient 

clinical signs, no 

mortality)

>2000

432

mg a.i./kg 

bw

Chlorantraniliprole

35WG

Formulated 

Product

DuPont18946

Colinus 

virginianus

(Northern 

bobwhite)

Acute oral

dose

LD 50

NOAEL(transient 

clinical signs, no 

mortality)

>2250

486

mg a.i./kg 

bw

Chlorantraniliprole

20SC

Formulated 

Product

DuPont19420

Colinus 

virginianus

(Northern 

bobwhite)

Subacute

dietary

LC 50

NOAEC

>5620

5620

mg a.i./kg 

diet

The available data show no indications that formulated product, metabolites, or 

degradates are more toxic than active ingredient.
36

2. Mammalian Toxicity

Acute toxicity study effects for the technical active ingredient in mammals are reported 

as follows:

Acute Oral Toxicity LD50: >5000 mg/kg (Rat)

Acute Dermal Toxicity LD50: >5000 mg/kg (Rat) 

Acute Inhalation Toxicity LC50: >5.1 mg/L (Rat)

Formulated products are as equally non-toxic following acute exposures as is

technical chlorantraniliprole. A single dose of chlorantraniliprole 20SC [200 g/L (w/v); 

18.5% (w/w)] (chlorantraniliprole 20SC) was administered by oral gavage to three fasted 

female rats at a dose of 5000 mg/kg. The rats were dosed one at a time at a minimum of 

48-hour intervals. All rats survived until the scheduled sacrifice. No clinical signs of 

toxicity were observed, and no body weight loss occurred after dosing. No gross lesions 

were present in the rats at necropsy. A single dose of chlorantraniliprole 35WG was 

administered by oral gavage to one fasted female rat each at a dose of 175, 550, or 1750 

mg/kg and to three fasted female rats at a dose of 5000 mg/kg. No deaths occurred. The 

rats exhibited no clinical signs of toxicity during the study. No body weight losses 

occurred after dosing. No gross lesions were present in the rats at necropsy. For the 

purposes of this risk assessment, to facilitate a comparison of estimated dietary residues 

with toxicity endpoints for acute effects, the existing rate oral LD50 toxicity study was 

used to estimate a dietary concentration of the pesticide that would correspond to a daily

oral dose equivalent to the LD50. To accomplish this, a conservative ingestion rate of 

100 percent of the body weight was applied. The resulting estimated dietary acute 

toxicity endpoint is >5000 mg/kg-diet [(>5000 mg/kg-bw)(1 kg-bw/1kg-diet) = >5000 

mg/kg-diet].

In developmental toxicity studies in rats and rabbits, chlorantraniliprole exhibited no 

effects on any parameter in pregnant females or their offspring at levels up to and 

including the maximum tested dose of 1,000 mg/kg bw/day. The NOAEL for this study

is 1,000 mg/kg/day.

No reproduction toxicity was observed in a two-generation reproduction study with

chlorantraniliprole in rats. No adverse effects were observed on reproduction, fertility, 

sperm parameters, estrous cycle, litter size, pup survival and developmental landmarks up 

to the maximum tested dose of 20,000 ppm in the diet. There were no adverse 

histological findings indicative of reproductive toxicity. There was a slight reduction in 

the F1 pup (but not F2 pup) weight during lactation at the highest dose level (mean 

maternal intake during lactation equal to 3118 mg/kg-bw/day); this was attributed, in 

part, to weight loss in one dehydrated dam during lactation which had a litter with some 

of the lowest pup weights. The slight change in pup weight was without subsequent 

effects since overall body weight, weight gain and development in F1 rats fed 20,000 

ppm were similar to control animals. The NOAEC for this study is 20,000 ppm or 1000 

mg/kg bw/day as a NOAEL (estimated).
37

3. Terrestrial Invertebrate Toxicity

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume.

The available formulated product data, when adjusted for active ingredient suggest that 

there is no practical difference between the toxicity of active ingredient and formulated 

products to bees.

Available Terrestrial Invertebrate Toxicity Data for Chlorantraniliprole, 

Formulations, and Degradates (data ordered by species to facilitate comparisons of 

a.i. with degradates and products)

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based 

on A.S.

Units of Active 

Substance

Chlorantraniliprole

20SC

Formulated 

Product

DuPont18423Aphidius 

rhopalosiphi

Mortality 

and 

reproduction

LR 50 

and ER 

50 >750 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont12405Aphidius 

rhopalosiphi

Mortality 

and 

reproduction

LR 50 

and ER 

50 >750 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont12753Apis mellifera

(Honeybee) Semi-field NOEC 156.16 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont14387Apis mellifera

(Honeybee) Acute oral LD50 >0.119

mg. 

chlorantraniliprole/bee

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont*-

14387

Apis mellifera

(Honeybee)

Acute 

contact LD50 >0.100

mg. 

chlorantraniliprole/bee

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont14388Apis mellifera

(Honeybee) semi-field NOAEC 52.5 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont14706Apis mellifera

(Honeybee) semi-field NOAEC 52.5 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont16269Apis mellifera

(Honeybee) Acute

Mortality 

<4% 112.5 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont16271Apis mellifera

(Honeybee) semi-field NOAEC >60 g chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont16272Apis mellifera

(Honeybee) semi-field NOAEC >60 g chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17208Apis mellifera

(Honeybee) semi-field NOAEC 60 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17247Apis mellifera

(Honeybee) semi-field

LOAEC 

(mortality 

and 

decreased 

flight 

intensity) >60 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17248Apis mellifera

(Honeybee) semi-field

LOAEC 

(mortality 

and 

decreased 

flight 

intensity) 60 g. chlorantraniliprole/ha

Chlorantraniliprole 

Technical Technical

DuPont17582Apis mellifera

(Honeybee) Acute oral

LD 50 >0.0274

>104.1

μg/bee in water

μg/bee in acetone

chlorantraniliprole/bee

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18085Apis mellifera

(Honeybee) semi-field NOAEC 60 g. chlorantraniliprole/ha

Chlorantraniliprole Formulated DuPont- Apis mellifera semi-field LOAEC 60 g. chlorantraniliprole/ha
38

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based 

on A.S.

Units of Active 

Substance

20SC Product 18086 (Honeybee) (mortality 

and 

decreased 

flight 

intensity)

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18087Apis mellifera

(Honeybee) semi-field NOAEC 60 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18426Apis mellifera

(Honeybee) Acute oral LD 50 >114.1 μg. chlorantraniliprole/bee

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17301

Chrysoperla 

carnea

(Green 

lacewing) 

larvae

Mortality 

Reproduction

EC50 

LOEC

120

120 g chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont19746

Coccinella 

septempunctata 

(Lady bird 

beetle)

Mortality

Reproduction

LOAEC

LOAEC

60

60 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17300

Coccinella 

septempunctata 

(Lady bird 

beetle) larvae

Mortality 

Reproduction

EC50 

LOEC

<120

120 g. chlorantraniliprole/ha

Chlorantraniliprole Technical

DuPont14398Eisenia fetida 

(Earthworm) Acute LC 50 >1000

mg chlorantraniliprole /kg 

soil dry weight.

IN-EQW78

Technical 

metabolite

DuPont15389Eisenia fetida 

(Earthworm) Acute LC 50 >1000

mg IN-EQW78/kg soil 

dry weight.

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont16694Eisenia fetida 

(Earthworm

Reproduction 

Growth NOAEC 350

mg chlorantraniliprole /kg 

soil dry weight.

IN-EQW78

Technical 

metabolite

DuPont17093Eisenia fetida 

(Earthworm

Reproduction 

Growth NOAEC 1000

mg IN-EQW78/kg soil 

dry weight.

IN-F6L99

Technical 

metabolite

DuPont17631Eisenia fetida 

(Earthworm) Acute LC 50 632.5

mg IN-F6L99/kg soil dry 

weight.

IN-ECD73

Technical 

metabolite

DuPont17632Eisenia fetida 

(Earthworm)

Reproduction 

Growth NOAEC 1000

mg IN-ECD73/kg 

artificial soil dry weight

IN-GAZ70

Technical 

metabolite

DuPont17633Eisenia fetida 

(Earthworm)

Reproduction 

Growth NOAEC 1000

mg IN-GAZ70/kg soil dry 

weight

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont18817Eisenia fetida 

(Earthworm) Acute LC 50 >350

mg chlorantraniliprole/kg 

drysoil

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18818Eisenia fetida 

(Earthworm) Acute LC 50 >200

mg chlorantraniliprole/kg 

drysoil

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont16532

Episyrphus 

balteatus

(Hoverfly) Mortality LR100 120 g chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18082

Episyrphus 

balteatus

(Hoverfly)

Mortality 

Reproduction

LR 50 

ER 50

12.6

13.3 g chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont19747

Episyrphus 

balteatus

(Hoverfly)

Mortality 1st

treatment

Mortality 2nd

treatment

Reproduction

<control

>control

NOAEL

60

60

60

G chlorantraniliprole/ha

twice with 7-day interval

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont18084

Episyrphus 

balteatus

(Hoverfly)

Mortality

Reproduction

LR50

ER 50

4.64

>4.4 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated

Product

DuPont20303

Episyrphus 

balteatus

(Hoverfly)

Mortality 1st

treatment

Mortality 2nd

treatment

Reproduction

<control

<control

NOAEL

60

60

60

g. chlorantraniliprole/ha

twice with 7-day interval

IN-EQW78

Technical 

metabolite

DuPont16531

Folsomia

candida 

(Springtail) Reproduction

EC 50 

NOEC

>100

100

mg IN-EQW78/kg dry 

soil

IN-ECD73

Technical 

metabolite

DuPont17083Folsomia 

candida Reproduction

EC 50 

NOEC

>100

100 mg IN-ECD73/kg dry soil
39

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based 

on A.S.

Units of Active 

Substance

(Springtail)

Chlorantraniliprole Technical

DuPont18730

Folsomia 

candida 

(Springtail) Reproduction

EC 50 

NOEC

0.48 

0.39 

mg chlorantraniliprole /kg 

dry soil

Chlorantraniliprole Technical

DuPont19748Hypoaspis 

aculeifer (mite) Reproduction NOAEC 100

mg chlorantraniliprole /kg 

dry soil

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18081 

RV1

Orius 

laevigatus

Mortality 

and 

reproduction

LR 50 & 

ER 50 >120 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont12406Typhlodromus 

pyri

Mortality 

and 

reproduction

LR 50 

and ER 

50 >750 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont14704Typhlodromus 

pyri

Mortality 

and 

reproduction

LR 50 

ER 50 >750 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont17312Typhlodromus 

pyri

Population 

study NOAEC 750 g. chlorantraniliprole/ha

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont14705Typhlodromus 

pyri

Population 

reduction 

(transient) LOAEC 52.5 g. chlorantraniliprole/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18424Typhlodromus 

pyri

Mortality 

and 

reproduction

LR 50 

and ER 

50 >750 g. chlorantraniliprole/ha
40

4. Terrestrial Plant Toxicity

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume.

The following table presents the available terrestrial plant toxicity data.

Available Terrestrial Plant Toxicity Data for Chlorantraniliprole, Formulations, 

and Degradates

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects Value 

Based on A.S.

Units of Active 

Substance

Chlorantraniliprole

20SC

Formulated 

Product

DuPont19074Zea mays 

(corn)

Avena sativa 

(oat)

Allium cepa 

(common 

onion)

Lolium 

perenne 

(perennial 

ryegrass)

Cucumis 

sativa 

(cucumber)

Brassica 

napus (rape)

Pisum sativum 

(pea)

Glycine max 

(soybean)

Beta vulgaris 

(sugarbeet)

Lycopersicon 

esculentum 

(tomato)

Vegetative 

vigor

EC25 

dicots

EC5 

dicots

EC25 

monocots

EC5 

monocots

>300

>300 cucumber, 

rape

<300 all others

>300 

<300 Onion

>300 otherl 

species

g. chlorantraniliprole

/ha

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont19075Zea mays 

(corn)

Avena sativa 

(oat)

Allium cepa 

(common 

onion)

Lolium 

perenne 

(perennial 

ryegrass)

Cucumis 

sativa 

(cucumber)

Brassica 

napus (rape)

Pisum sativum 

(pea)

Glycine max 

(soybean)

Beta vulgaris 

(sugarbeet)

Lycopersicon 

esculentum 

(tomato)

Seedling 

emergence

EC25 

monocots

EC5 

monocots

EC25 

dicots

EC5 

dicots

>300 (except 

rygrass with 34% 

effect)

<300 

<300 all others

>300 

<300 (cucumber, 

rape, pea, sugar 

beet)

>300 otherl 

species

g. chlorantraniliprole 

/ha
41

5. Freshwater Invertebrate Toxicity

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume. Chlorantraniliprole can be characterized as very highly toxic to freshwater 

invertebrates.

Available Freshwater Invertebrate Toxicity Data for Chlorantraniliprole, 

Formulations, and Degradates (data ordered by species to facilitate comparisons of 

a.i. with degradates and products)

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species 

Test 

Type

Endpoint 

Type

Effects 

Value 

Based on 

A.S. Units of Active Substance

Chlorantraniliprole

Technical Technical

DuPont18428Brachionus 

calyciflorus Acute EC 50 >1.00 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont15109

Centroptilum 

triangulifer

(Mayfly) Acute LC 50 0.0116 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont17585

Chimarra 

atterima

(Caddisfly) Acute LC 50 0.0117 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont15112

Chironomus 

riparius

(Midge) Acute LC 50 0.0859 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont14396

Chironomus 

riparius

(Midge) Chronic

NOAEC

(pore 

water 

from 28-d 

sediment 

study 0.005

mg chlorantraniliprole/kg 

spiked sediment dry weight

Chlorantraniliprole 

Technical Technical

DuPont18090

Copepods (of 

the suborder 

Cyclopoida) Acute LC 50 >1.00

mg chlorantraniliprole 

technical/L

Chlorantraniliprole 

Technical Technical

DuPont15868

28-day old 

Daphnia magna

(Water flea) Acute EC 50 0.0166 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont12411*Daphnia magna

(Water flea) Acute EC 50 0.0116 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont12754 

RV1

Daphnia magna

(Water flea) Chronic NOAEC 0.00447 mg chlorantraniliprole/L

LBA24-002

Technical 

metabolite

DuPont14889 

RV1

Daphnia magna

(Water flea) Acute

EC 50

NOAEC

>10

10 mg LBA24-002/L

LBA22-002

Technical 

metabolite

DuPont14890 

RV1

Daphnia magna

(Water flea) Acute

EC 50

NOAEC

>0.24

0.24 mg LBA22-002/L

Chlorantraniliprole 

35WG

Formulated 

Product

DuPont15113Daphnia magna

(Water flea) Acute EC 50 0.011 mg chlorantraniliprole/L

IN-EQW78

Technical 

metabolite

DuPont15388Daphnia magna

(Water flea) Acute

EC 50

NOAEC

>0.138

0.138 mg IN-EQW78/L

Chlorantraniliprole 

Technical Technical

DuPont15874Daphnia magna

(Water flea) Chronic NOAEC 0.00447 mg chlorantraniliprole/L

LBA23-000

DuPont16754 

RV1

Daphnia magna

(Water flea) Acute

EC 50

NOAEC >0.01 mg LBA23-000/L

Chlorantraniliprole 

Technical Technical

DuPont17653Daphnia magna

(Water flea) Acute EC 50 0.0098 mg chlorantraniliprole/L

IN-GAZ70

Technical 

metabolite

DuPont18387Daphnia magna

(Water flea) Acute

EC 50

NOAEC

>0.00987

0.00987 mg IN-GAZ70/L
42

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species 

Test 

Type

Endpoint 

Type

Effects 

Value 

Based on 

A.S. Units of Active Substance

Chlorantraniliprole 

20SC

Formulated 

Product

DuPont18427 

RV1

Daphnia magna

(Water flea) Acute EC 50 0.0071 mg chlorantraniliprole/L

IN-ECD73

Technical 

metabolite

DuPont18472Daphnia magna

(Water flea) Acute

EC 50

NOAEC

>0.013

0.0138 mg IN-ECD73/L

IN-F6L99

Technical 

metabolite

DuPont18473Daphnia magna

(Water flea) Acute EC 50 46.8 mg IN-F6L99/L

IN-F9N04

Technical 

metabolite

DuPont18474Daphnia magna

(Water flea) Acute EC 50 0.03 mg IN-F9N04/L

Chlorantraniliprole 

Technical Technical

DuPont15877Gammarus 

pseudolimnaeus Acute LC 50 0.0351 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont15114 Hyalella azteca Acute LC 50 >0.389 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont15873

Lumbriculus 

variegatus

(California 

blackworm) Acute LC 50 >1.49 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont15872Oronectes virilis

(Crayfish) Acute LC 50 >1.42 mg chlorantraniliprole/L

Chlorantraniliprole 

Technical Technical

DuPont18804

Soyedina 

carolinensis

(Carolina 

Forestfly) Acute LC 50 >0.978 mg chlorantraniliprole/L

The available data show no indications that formulated product, metabolites, or 

degradates are more toxic than active ingredient.
43

6. Freshwater Fish Toxicity

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume. While non-definitive LC50 values are only available for chlorantraniliprole, it 

can be characterized as being slightly to practically non-toxic to freshwater fish.

Available Freshwater Fish Toxicity Data for Chlorantraniliprole, Formulations, 

and Degradates (data ordered by species to facilitate comparisons of a.i. with 

degradates and products)

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species 

Test 

Type

Endpoint 

Type

Effects 

Value 

Based 

on A.S. Units of Active Substance

Chlorantraniliprole

Technical Technical

DuPont14278

Ictalurus 

punctatus

(Channel 

catfish) Acute LC 50 >13.4 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont12333

Lepomis 

macrochirus

(Bluegill 

sunfish) Acute LC 50 >15.1 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont12332

Oncorhynchus 

mykiss

(Rainbow trout) Acute LC 50 >13.8 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont14279

Oncorhynchus 

mykiss

(Rainbow trout) Chronic NOAEC 0.11 mg chlorantraniliprole/L

Chlorantraniliprole

35WG

Formulated 

Product

DuPont15396

Lepomis 

macrochirus

(Bluegill 

sunfish) Acute LC 50 >1.19 mg chlorantraniliprole/L

Chlorantraniliprole

20SC

Formulated 

Product

DuPont18602

Lepomis 

macrochirus

(Bluegill 

sunfish) Acute LC 50 >1.84 mg chlorantraniliprole/L

Chlorantraniliprole

35WG

Formulated 

Product

DuPont15386

Oncorhynchus 

mykiss

(Rainbow trout) Acute LC 50 >1.09 mg chlorantraniliprole/L

Chlorantraniliprole

20SC

Formulated 

Product

DuPont18601

Oncorhynchus 

mykiss

(Rainbow trout) Acute LC 50 >2.16 mg chlorantraniliprole/ha

* Study reviewed by PSD at the time of risk assessment.

The available data show no indications that formulated products are more toxic than 

active ingredient.
44

7. Estuarine/Marine Invertebrate Toxicity

The following table presents the available estuarine/marine invertebrate toxicity data. 

This risk assessment uses the summarized acute and chronic toxicity data from Volume 3, 

Annex B.9: Ecotoxicology with the regulatory evaluation and approval as completed by

the PSD. The full text of those summaries and evaluations are available in the above 

volume. Chrlorantraniliprole is very highly toxic to certain estuarine marine 

invertebrates, based on the data for the eastern oyster.

Available Estuarine/Marine Invertebrate Toxicity Data for Chlorantraniliprole, 

Formulations, and Degradates

Test Material 

Identification

Nature of

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based 

on A.S. Units of Active Substance

Chlorantraniliprole

Technical Technical

DuPont12335

Americamysis 

bahia

(Mysid shrimp) Acute LC 50 1.15 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont14397

Americamysis 

bahia

(Mysid shrimp) Chronic NOAEC 0.695 mg chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont12412

Crassostrea 

virginica

(Eastern oyster) Acute EC 50 0.0399 mg chlorantraniliprole/L

Because the most sensitive species acutely (oyster) is not represented by chronic values, 

the acute to chronic ratio for the mysid (1.15/0.695 = 1.65) was applied to the oyster 

LC50 to estimate a chronic effects endpoint for this species (0.0399 mg/L/1.65 = 0.024 

mg/L).
45

8. Estuarine Marine Fish Toxicity

The following table presents the available estuarine/marine fish toxicity data This risk 

assessment uses the summarized acute and chronic toxicity data from Volume 3, Annex 

B.9: Ecotoxicology with the regulatory evaluation and approval as completed by the 

PSD. The full text of those summaries and evaluations are available in the above 

volume. While non-definitive LC50 values are only available for chlorantraniliprole, it 

can be characterized as being slightly to practically non-toxic to estuarine/marine fish.

Available Estuarine/Marine Fish Toxicity Data for Chlorantraniliprole, 

Formulations, and Degradates

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based on 

A.S.

Units of 

Active 

Substance

Chlorantraniliprole

Technical Technical

DuPont12334

Cyprinodon 

variegatus

(Sheepshead 

minnow) Acute LC 50 >12.0 mg/L

Chlorantraniliprole

Technical Technical

DuPont14394

Cyprinodon 

variegatus

(Sheepshead 

minnow)

Early Life 

Stage 

Toxicity NOAEC 1.28 mg/L
46

9. Aquatic Plant Toxicity

The following table presents the available aquatic plant toxicity data. This risk 

assessment uses the summarized acute and chronic toxicity data from Volume 3, Annex 

B.9: Ecotoxicology with the regulatory evaluation and approval as completed by the 

PSD. The full text of those summaries and evaluations are available in the above 

volume.

Available Aquatic Plant Toxicity Data for Chlorantraniliprole, Formulations, and 

Degradates

Test Material 

Identification

Nature of 

Tested 

Material

Registrant 

Study ID Test Species Test Type

Endpoint 

Type

Effects 

Value 

Based 

on 

A.S.

Units of Active 

Substance

Chlorantraniliprole

Technical Technical

DuPont14390

Anabaena flosaquae

(Blue-green algae)

Growth / 

Reproduction

EC50 

NOAEC

>2

2

mg. 

chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont12409 

RV1

Lemna gibba 

(Duckweed)

Growth / 

Reproduction

EC50 

NOAEC

>2

2

mg. 

chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont14392 

RV1

Navicula 

pelliculosa

Growth / 

Reproduction

EC50

NOEC

>15.1

15.1

mg. 

chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont12408 

RV1

Selenastrum 

capricornutum

(Green algae)

Growth / 

Reproduction

EC50

NOEC

>2

2

mg. 

chlorantraniliprole/L

Chlorantraniliprole

Technical Technical

DuPont14391Skeletonema 

costatum

Growth / 

Reproduction

EC50

NOEC

>14.6

14.6

mg. 

chlorantraniliprole/L

Chlorantraniliprole

20SC

Formulated 

Product

DuPont18088

Pseudokirchneriella 

subcapitata

(Green algae)

Growth / 

Reproduction

EC50

NOEC

>4

4

mg. 

chlorantraniliprole/L

Chlorantraniliprole

35WG

Formulated 

Product

DuPont18089

Pseudokirchneriella 

subcapitata

(Green algae)

Growth / 

Reproduction

EC50

NOEC

>1.78

1.78

mg.

chlorantraniliprole/L
47

10. Summary of Effects Measurement Endpoint Values Used in the Risk Assessment

The following table presents the effects measurement endpoints used in the risk 

assessment for chlorantraniliprole.

Effects Measurement Endpoints Used in Quantitative Risk Assessment

Taxa Effects Measurement Endpoint Rationale

Birds (reptiles, 

terrestrial 

invertebrates)

Survival – bobwhite and mallard LC50>5620 mg/kg-diet

Reproduction – mallard 120 mg/kg-diet

Most sensitive tested

Most sensitive tested

Mammals Survival – estimated rat LC50>5000 mg/kg-diet

Reproduction – rat NOAEC 20,000 mg/kg-diet

Most sensitive tested LD50 

adjusted to estimate dietary 

equivalent (100% bw

consumed/day)

Most sensitive tested

Terrestrial plants Vegetative Vigor Dicot EC25 >300 g/ha

 Dicot EC5 <300 g/ha

 Monocot EC25 >300g/ha

 Monocot EC5 <300g/ha

Seedling Emergence Dicot EC25 >300 g/ha

 Dicot EC5 <300 g/ha

 Monocot EC25 <300 /ha

Monocot EC5 <300 g/ha

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Most sensitive tested

Freshwater 

invertebrates

Survival – daphnid 48-h EC50 0.0116 mg/L

Reproduction –daphnid NOAEC 0.0044 mg/L

Most sensitive tested

Most sensitive tested

Freshwater fish Survival – trout 96-h LC50 > 13.8 mg/L

Reproduction – trout NOAEC 0.11 mg/L

Most sensitive tested

Most sensitive tested

Estuarine/marine

invertebrates

Survival – oyster 48-h EC50 0.0399 mg/L

Chronic effect estimate – 0.024 mg/L

Most sensitive tested

Most sensitive tested for 

acute adjusted with available 

ACR

Estuarine/marine 

fish

Survival– sheepshead 96-h LC50 > 12 mg/L

Reproduction – sheepshead NOAEC 1.28 mg/L

Most sensitive tested

Most sensitive tested

Aquatic plants Growth/reproduction – Unicellular NOEC 1.78 mg/L

Growth – Vascular NOEC 2 mg/L

Most sensitive tested

Most sensitive tested
48

V. RISK CHARACTERIZATION

A. Risk Estimation

1. Terrestrial Vertebrate Risk Quotients

Because of the very low toxicity of chlorantraniliprole to mammals and birds, the risk 

assessment presents risk quotients (RQs) only for a highly conservative assumed 

maximum single use scenario (0.5 lbs ai/acre). The following two tables show the results 

of these RQ calculations. No Agency levels of concern (LOCs) were exceeded for birds 

or mammals under this upper bound exposure assumption. There would be no concern 

for labeled uses which are all of lower application.

Mammal RQs

Dietary Item

Estimated 

EEC

mg/kg-diet

Acute 

Effects 

Endpoint 

mg/kg-diet

Chronic

Effects 

Endpoint 

mg/kg-diet

Acute 

RQ*

Chronic

RQ*

Identified 

Concerns**

Short Grass 120.0 >5000 20,000 <0.1 <1 None

Tall Grass 55.0 <0.1 <1 None

Broadleaf plants/sm 

Insects 67.5

<0.1 <1 None

Fruits/pods/seeds/lg 

Insects 7.5

<0.1 <1 None

* RQ = EEC/effects endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.2), and listed 

species (0.1). Chronic RQs compared with chronic LOC of 1.

Bird RQs

Dietary Item

Estimated 

EEC

mg/kg-diet

Acute 

Effects 

Endpoint 

mg/kg-diet

Chronic

Effects 

Endpoint 

mg/kg-diet

Acute 

RQ*

Chronic

RQ*

Identified 

Concerns**

Short Grass 120.0 >5620 500 <0.1 <1 None

Tall Grass 55.0 <0.1 <1 None

Broadleaf plants/sm 

Insects 67.5

<0.1 <1 None

Fruits/pods/seeds/lg 

Insects 7.5

<0.1 <1 None

* RQ = EEC/effects endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.2), and listed 

species (0.1). Chronic RQs compared with chronic LOC of 1.
49

2. Terrestrial Invertebrate Risk Quotients

The Agency currently does not have a method for calculating risk quotients for terrestrial 

invertebrates.

3. Terrestrial Plant Risk Quotients

Only the highest application scenario was modeled for plant exposures. For seedling 

emergence-based risk quotients runoff plus drift loading to adjacent areas is directly

compared with available toxicity endpoints (see table below). Because these endpoints 

were not definitive endpoints it, numerical conclusions regarding exceeding Agency

levels of concern cannot be made. Instead, the risk discussion section of this document 

will provide further context.

Seedling Emergence Plant RQs Under Maximum Single Application Rate

Application 

Method/Rate

Total 

Loading 

to 

Adjacent 

Areas

g ai/ha

Total 

Loading to 

Semiaquatic 

Areas

g ai/ha

Plant 

Type

NonListed

Effects 

Endpoint

(g/ha)

Listed 

Effects 

Endpoint

(g/ha)

NonListed 

RQ

Listed 

RQ

Ground 

Unincorp./100.8 

g/ha

2.0160 11.0880 Monocot

Dicot

<300

>300

<300

<300

>0.0067

<0.0067

>0.037

>0.037

Ground 

Incorp/100.8 

g/ha

2.0160 11.0880 Monocot

Dicot

<300

>300

<300

<300

>0.0067

<0.0067

>0.037

>0.037

Aerial /100.8 

g/ha

6.0480 15.1200 Monocot

Dicot

<300

>300

<300

<300

>0.020

<0.020

>0.050

>0.050

For vegetative vigor-based risk quotients runoff plus drift loading to adjacent areas is 

directly compared with available toxicity endpoints (see table below). Because these

endpoints were not definitive endpoints it, numerical conclusions regarding exceeding 

Agency levels of concern cannot be made. Instead, the risk discussion section of this 

document will provide further context.
50

Vegetative Vigor Plant RQs Under Maximum Single Application Rate

Application 

Method/Rate

DRIFT EEC 

(for ground: 

application rate x 

0.01) (for aerial: 

application rate x 

0.05)

g ai/ha

Plant 

Type

NonListed

Effects 

Endpoint

(g/ha)

Listed 

Effects 

Endpoint

(g/ha)

NonListed 

RQ

Listed 

RQ

Ground 

Unincorp./100.8 

g/ha

1.0080 Monocot

Dicot

>300

>300

<300

<300

<0.0034

<0.0034

>0.0034

>0.0034

Ground 

Incorp/100.8 g/ha

1.0080 Monocot

Dicot

>300

>300

<300

<300

<0.0034

<0.0034

>0.0034

>0.0034

Aerial /100.8 g/ha 5.0400 Monocot

Dicot

>300

>300

<300

<300

<0.017

<0.017

>0.017

>0.017

4. Freshwater Fish Risk Quotients

The following tables present the RQs for freshwater fish. No RQs exceeded Agency

levels of concern.

PRZM/EXAMS RQs for FW Fish from Aerial Spray Application of DPX-E2Y45 for Various Crop 

Types 

Scenario

Application

Peak 60-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lbs/A) # Int

FL cabbage 0.065 3 3 2.652 1.466 0.0001 0.0133 None

FL cucumber 0.065 3 5 5.693 3.748 0.0003 0.0341 None

PA tomato 0.098 2 5 1.513 1.136 0.0001 0.0103 None

CA tomato 0.098 2 5 1.080 0.702 0.0001 0.0064 None

FL tomato 0.098 2 5 3.660 2.312 0.0002 0.0210 None

FL peppers 0.098 2 5 6.749 4.425 0.0003 0.0402 None

CA lettuce 0.065 3 3 3.579 2.203 0.0002 0.0200 None

CA cotton 0.099 2 5 1.785 1.229 0.0001 0.0112 None

NC cotton 0.099 2 5 3.730 2.584 0.0002 0.0235 None

MS cotton 0.099 2 5 3.769 2.633 0.0002 0.0239 None

NY grape 0.099 2 7 1.389 1.041 0.0001 0.0095 None

CA grape 0.099 2 7 1.188 0.791 0.0001 0.0072 None

NC apple 0.099 2 10 1.359 0.917 0.0001 0.0083 None

PA apple 0.099 2 10 1.245 0.857 0.0001 0.0078 None

OR apple 0.099 2 10 0.786 0.558 0.0000 0.0051 None

ID potato 0.066 3 5 1.021 0.707 0.0001 0.0064 None

ME potato 0.066 3 5 1.558 1.319 0.0001 0.0120 None

GA peach 0.099 2 7 1.086 0.655 0.0000 0.0060 None

MI Cherry 0.099 2 7 1.035 0.758 0.0001 0.0069 None

1-Acute Toxicity Endpoint=13,800 μg/L

2-Chronic Toxicity Endpoint=110 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
51

PRZM/EXAMS RQs for FW Fish from Ground Spray Application of DPX-E2Y45 for Various 

Crop Types

Scenario

Application

Peak 60-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 1.331 0.0001 0.0121 None

FL cucumber 0.065 3 5 5.624 3.695 0.0003 0.0336 None

PA tomato 0.098 2 5 1.280 0.914 0.0001 0.0083 None

CA tomato 0.098 2 5 0.731 0.473 0.0000 0.0043 None

FL tomato 0.098 2 5 3.436 2.198 0.0002 0.0200 None

FL peppers 0.098 2 5 6.501 4.234 0.0003 0.0385 None

CA lettuce 0.065 3 3 3.311 2.057 0.0001 0.0187 None

CA cotton 0.099 2 5 1.470 1.005 0.0001 0.0091 None

NC cotton 0.099 2 5 3.473 2.440 0.0002 0.0222 None

MS cotton 0.099 2 5 3.575 2.469 0.0002 0.0224 None

NY grape 0.099 2 7 1.189 0.889 0.0001 0.0081 None

CA grape 0.099 2 7 0.813 0.550 0.0000 0.0050 None

NC apple 0.099 2 10 0.999 0.689 0.0000 0.0063 None

PA apple 0.099 2 10 1.048 0.716 0.0001 0.0065 None

OR apple 0.099 2 10 0.410 0.304 0.0000 0.0028 None

ID potato 0.066 3 5 0.812 0.513 0.0000 0.0047 None

ME potato 0.066 3 5 1.350 1.092 0.0001 0.0099 None

GA peach 0.099 2 7 0.763 0.447 0.0000 0.0041 None

MI Cherry 0.099 2 7 0.867 0.596 0.0000 0.0054 None

FLTurf 0.26 2 7 0.837 0.531 0.0000 0.0048 None

FL Turf 0.026 19 7 0.753 0.488 0.0000 0.0044 None

PA Turf 0.26 2 7 1.102 0.769 0.0001 0.0070 None

PA Turf 0.026 19 7 1.625 1.023 0.0001 0.0093 None

CA Turf 0.26 2 7 0.654 0.416 0.0000 0.0038 None

CA Turf 0.026 19 7 0.766 0.544 0.0000 0.0049 None

CA Nursery 0.4992 1 NA 5.663 3.495 0.0003 0.0318 None

CA Residential 0.4992 1 NA 1.779 1.385 0.0001 0.0126 None

FL Nursery 0.4992 1 NA 9.785 6.203 0.0004 0.0564 None

MI Nursery 0.4992 1 NA 2.508 2.033 0.0001 0.0185 None

TN Nursery 0.4992 1 NA 10.98

1

6.778 0.0005 0.0616

None

1-Acute Toxicity Endpoint=13,800 μg/L

2-Chronic Toxicity Endpoint=110 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
52

5. Freshwater Invertebrate Risk Quotients

The following table presents the RQs for freshwater invertebrates.

PRZM/EXAMS RQs for FW Invertebrates from Aerial Spray Application of DPX-E2Y45 for Various 

Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.652 2.146 0.1850 0.4801 RU,LS

FL cucumber 0.065 3 5 5.693 4.939 0.4258 1.1049 RU,LS, C

PA tomato 0.098 2 5 1.513 1.306 0.1126 0.2922 RU,LS

CA tomato 0.098 2 5 1.080 0.922 0.0795 0.2063 LS

FL tomato 0.098 2 5 3.660 3.001 0.2587 0.6714 RU,LS

FL peppers 0.098 2 5 6.749 5.683 0.4899 1.2714 RU,LS,C

CA lettuce 0.065 3 3 3.579 2.997 0.2584 0.6705 RU,LS

CA cotton 0.099 2 5 1.785 1.576 0.1359 0.3526 RU,LS

NC cotton 0.099 2 5 3.730 3.207 0.2765 0.7174 RU,LS

MS cotton 0.099 2 5 3.769 3.271 0.2820 0.7318 RU,LS

NY grape 0.099 2 7 1.389 1.197 0.1032 0.2678 RU,LS

CA grape 0.099 2 7 1.188 1.026 0.0884 0.2295 LS

NC apple 0.099 2 10 1.359 1.153 0.0994 0.2579 LS

PA apple 0.099 2 10 1.245 1.091 0.0941 0.2441 LS

OR apple 0.099 2 10 0.786 0.674 0.0581 0.1508 LS

ID potato 0.066 3 5 1.021 0.859 0.0741 0.1922 LS

ME potato 0.066 3 5 1.558 1.392 0.1200 0.3114 RU,LS

GA peach 0.099 2 7 1.086 0.886 0.0764 0.1982 LS

MI Cherry 0.099 2 7 1.035 0.907 0.0782 0.2029 LS

1-Acute Toxicity Endpoint= 11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
53

PRZM/EXAMS RQs for FW Invertebrates from Ground Spray Application of DPX-E2Y45 for Various 

Crop Types 

Scenario

Application

Peak 21-day

Ave

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 2.045 0.1763 0.4575 RU,LS

FL cucumber 0.065 3 5 5.624 4.86 0.4190 1.0872 RU,LS,C

PA tomato 0.098 2 5 1.280 1.097 0.0946 0.2454 LS

CA tomato 0.098 2 5 0.731 0.619 0.0534 0.1385 LS

FL tomato 0.098 2 5 3.436 2.817 0.2428 0.6302 RU,LS

FL peppers 0.098 2 5 6.501 5.475 0.4720 1.2248 RU,LS,C

CA lettuce 0.065 3 3 3.311 2.781 0.2397 0.6221 RU,LS

CA cotton 0.099 2 5 1.470 1.28 0.1103 0.2864 RU,LS

NC cotton 0.099 2 5 3.473 2.995 0.2582 0.6700 RU,LS

MS cotton 0.099 2 5 3.575 3.116 0.2686 0.6971 RU,LS

NY grape 0.099 2 7 1.189 1.025 0.0884 0.2293 LS

CA grape 0.099 2 7 0.813 0.706 0.0609 0.1579 LS

NC apple 0.099 2 10 0.999 0.852 0.0734 0.1906 LS

PA apple 0.099 2 10 1.048 0.898 0.0774 0.2009 LS

OR apple 0.099 2 10 0.410 0.365 0.0315 0.0817 None

ID potato 0.066 3 5 0.812 0.68 0.0586 0.1521 LS

ME potato 0.066 3 5 1.350 1.195 0.1030 0.2673 RU,LS

GA peach 0.099 2 7 0.763 0.62 0.0534 0.1387 LS

MI Cherry 0.099 2 7 0.867 0.739 0.0637 0.1653 LS

FLTurf 0.26 2 7 0.837 0.707 0.0609 0.1582 LS

FL Turf 0.026 19 7 0.753 0.644 0.0649 0.1441 LS

PA Turf 0.26 2 7 1.102 0.985 0.0849 0.2204 LS

PA Turf 0.026 19 7 1.625 1.357 0.1400 0.3036 RU,LS

CA Turf 0.26 2 7 0.654 0.554 0.0478 0.1239 None

CA Turf 0.026 19 7 0.766 0.669 0.0660 0.1500 LS

CA Nursery 0.4992 1 NA 5.663 4.672 0.4028 1.0452 RU,LS,C

CA Residential 0.4992 1 NA 1.779 1.543 0.1330 0.3452 RU,LS

FL Nursery 0.4992 1 NA 9.785 8.136 0.7014 1.8201 RU,LS,C

MI Nursery 0.4992 1 NA 2.508 2.284 0.1969 0.5110 RU,LS

TN Nursery 0.4992 1 NA 10.981 9.126 0.7867 2.0416 RU,LS,C

1-Acute Toxicity Endpoint=11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
54

6. Estuarine/Marine Fish Risk Quotients

The following table presents the RQs for estuarine/marine fish. No Agency levels of 

concern were exceeded.

PRZM/EXAMS RQs for Estuarine/Marine Fish from Aerial Spray Application of DPX-E2Y45 for 

Various Crop Types 

Scenario

Application

Peak 60-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.652 1.466 0.0001 0.0011 None

FL cucumber 0.065 3 5 5.693 3.748 0.0003 0.0029 None

PA tomato 0.098 2 5 1.513 1.136 0.0001 0.0009 None

CA tomato 0.098 2 5 1.080 0.702 0.0001 0.0005 None

FL tomato 0.098 2 5 3.660 2.312 0.0002 0.0018 None

FL peppers 0.098 2 5 6.749 4.425 0.0004 0.0035 None

CA lettuce 0.065 3 3 3.579 2.203 0.0002 0.0017 None

CA cotton 0.099 2 5 1.785 1.229 0.0001 0.0010 None

NC cotton 0.099 2 5 3.730 2.584 0.0002 0.0020 None

MS cotton 0.099 2 5 3.769 2.633 0.0002 0.0021 None

NY grape 0.099 2 7 1.389 1.041 0.0001 0.0008 None

CA grape 0.099 2 7 1.188 0.791 0.0001 0.0006 None

NC apple 0.099 2 10 1.359 0.917 0.0001 0.0007 None

PA apple 0.099 2 10 1.245 0.857 0.0001 0.0007 None

OR apple 0.099 2 10 0.786 0.558 0.0000 0.0004 None

ID potato 0.066 3 5 1.021 0.707 0.0001 0.0006 None

ME potato 0.066 3 5 1.558 1.319 0.0001 0.0010 None

GA peach 0.099 2 7 1.086 0.655 0.0001 0.0005 None

MI Cherry 0.099 2 7 1.035 0.758 0.0001 0.0006 None

1-Acute Toxicity Endpoint=12,000 μg/L

2-Chronic Toxicity Endpoint= 1280 μg/L

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
55

PRZM/EXAMS RQs for Estuarine/Marine Fish from Ground Spray Application of DPX-E2Y45 

for Various Crop Types

Scenario

Application

Peak 60-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 1.331 0.0001 0.0010 None

FL cucumber 0.065 3 5 5.624 3.695 0.0003 0.0029 None

PA tomato 0.098 2 5 1.280 0.914 0.0001 0.0007 None

CA tomato 0.098 2 5 0.731 0.473 0.0000 0.0004 None

FL tomato 0.098 2 5 3.436 2.198 0.0002 0.0017 None

FL peppers 0.098 2 5 6.501 4.234 0.0004 0.0033 None

CA lettuce 0.065 3 3 3.311 2.057 0.0002 0.0016 None

CA cotton 0.099 2 5 1.470 1.005 0.0001 0.0008 None

NC cotton 0.099 2 5 3.473 2.440 0.0002 0.0019 None

MS cotton 0.099 2 5 3.575 2.469 0.0002 0.0019 None

NY grape 0.099 2 7 1.189 0.889 0.0001 0.0007 None

CA grape 0.099 2 7 0.813 0.550 0.0000 0.0004 None

NC apple 0.099 2 10 0.999 0.689 0.0001 0.0005 None

PA apple 0.099 2 10 1.048 0.716 0.0001 0.0006 None

OR apple 0.099 2 10 0.410 0.304 0.0000 0.0002 None

ID potato 0.066 3 5 0.812 0.513 0.0000 0.0004 None

ME potato 0.066 3 5 1.350 1.092 0.0001 0.0009 None

GA peach 0.099 2 7 0.763 0.447 0.0000 0.0003 None

MI Cherry 0.099 2 7 0.867 0.596 0.0000 0.0005 None

FLTurf 0.26 2 7 0.837 0.531 0.0000 0.0004 None

FL Turf 0.026 19 7 0.753 0.488 0.0000 0.0003 None

PA Turf 0.26 2 7 1.102 0.769 0.0001 0.0006 None

PA Turf 0.026 19 7 1.625 1.023 0.0001 0.0008 None

CA Turf 0.26 2 7 0.654 0.416 0.0000 0.0003 None

CA Turf 0.026 19 7 0.766 0.544 0.0000 0.0004 None

CA Nursery 0.4992 1 NA 5.663 3.495 0.0003 0.0027 None

CA Residential 0.4992 1 NA 1.779 1.385 0.0001 0.0011 None

FL Nursery 0.4992 1 NA 9.785 6.203 0.0005 0.0048 None

MI Nursery 0.4992 1 NA 2.508 2.033 0.0002 0.0016 None

TN Nursery 0.4992 1 NA 10.98

1

6.778 0.0006 0.0053

None

FLTurf 0.26 2 7 2.531 1.331 0.0001 0.0010 None

1-Acute Toxicity Endpoint=12,000 μg/L

2-Chronic Toxicity Endpoint= 1,280 μg/L

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
56

7. Estuarine/Marine Invertebrate Risk Quotients

The following table presents the RQs for estuarine/marine invertebrates.

PRZM/EXAMS RQs for Estuarine/Marine Invertebrates from Aerial Spray Application of DPX-E2Y45 

for Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.652 2.146 0.0538 0.0894 LS

FL cucumber 0.065 3 5 5.693 4.939 0.1238 0.2058 RU,LS

PA tomato 0.098 2 5 1.513 1.306 0.0327 0.0544 None

CA tomato 0.098 2 5 1.080 0.922 0.0231 0.0384 None

FL tomato 0.098 2 5 3.660 3.001 0.0752 0.1250 LS

FL peppers 0.098 2 5 6.749 5.683 0.1424 0.2368 RU,LS

CA lettuce 0.065 3 3 3.579 2.997 0.0751 0.1249 LS

CA cotton 0.099 2 5 1.785 1.576 0.0395 0.0657 None

NC cotton 0.099 2 5 3.730 3.207 0.0804 0.1336 LS

MS cotton 0.099 2 5 3.769 3.271 0.0820 0.1363 LS

NY grape 0.099 2 7 1.389 1.197 0.0300 0.0499 None

CA grape 0.099 2 7 1.188 1.026 0.0257 0.0428 None

NC apple 0.099 2 10 1.359 1.153 0.0289 0.0480 None

PA apple 0.099 2 10 1.245 1.091 0.0273 0.0455 None

OR apple 0.099 2 10 0.786 0.674 0.0169 0.0281 None

ID potato 0.066 3 5 1.021 0.859 0.0215 0.0358 None

ME potato 0.066 3 5 1.558 1.392 0.0349 0.0580 None

GA peach 0.099 2 7 1.086 0.886 0.0222 0.0369 None

MI Cherry 0.099 2 7 1.035 0.907 0.0227 0.0378 None

1-Acute Toxicity Endpoint= 39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
57

PRZM/EXAMS RQs for Estuarine/Marine Invertebrates from Ground Spray Application of DPXE2Y45 for Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 2.045 0.0513 0.0852 LS

FL cucumber 0.065 3 5 5.624 4.86 0.1218 0.2025 RU,LS

PA tomato 0.098 2 5 1.280 1.097 0.0275 0.0457 None

CA tomato 0.098 2 5 0.731 0.619 0.0155 0.0258 None

FL tomato 0.098 2 5 3.436 2.817 0.0706 0.1174 None

FL peppers 0.098 2 5 6.501 5.475 0.1372 0.2281 RU,LS

CA lettuce 0.065 3 3 3.311 2.781 0.0697 0.1159 LS

CA cotton 0.099 2 5 1.470 1.28 0.0321 0.0533 None

NC cotton 0.099 2 5 3.473 2.995 0.0751 0.1248 LS

MS cotton 0.099 2 5 3.575 3.116 0.0781 0.1298 LS

NY grape 0.099 2 7 1.189 1.025 0.0257 0.0427 None

CA grape 0.099 2 7 0.813 0.706 0.0177 0.0294 None

NC apple 0.099 2 10 0.999 0.852 0.0214 0.0355 None

PA apple 0.099 2 10 1.048 0.898 0.0225 0.0374 None

OR apple 0.099 2 10 0.410 0.365 0.0091 0.0152 None

ID potato 0.066 3 5 0.812 0.68 0.0170 0.0283 None

ME potato 0.066 3 5 1.350 1.195 0.0299 0.0498 None

GA peach 0.099 2 7 0.763 0.62 0.0155 0.0258 None

MI Cherry 0.099 2 7 0.867 0.739 0.0185 0.0308 None

FLTurf 0.26 2 7 0.837 0.707 0.0177 0.0295 None

FL Turf 0.026 19 7 0.753 0.644 0.0189 0.0268 None

PA Turf 0.26 2 7 1.102 0.985 0.0247 0.0410 None

PA Turf 0.026 19 7 1.625 1.357 0.0407 0.0565 None

CA Turf 0.26 2 7 0.654 0.554 0.0139 0.0231 None

CA Turf 0.026 19 7 0.766 0.669 0.0192 0.0279 None

CA Nursery 0.4992 1 NA 5.663 4.672 0.1171 0.1947 RU,LS

CA Residential 0.4992 1 NA 1.779 1.543 0.0387 0.0643 None

FL Nursery 0.4992 1 NA 9.785 8.136 0.2039 0.3390 RU,LS

MI Nursery 0.4992 1 NA 2.508 2.284 0.0572 0.0952 LS

TN Nursery 0.4992 1 NA 10.98

1 9.126 0.2287 0.3803 RU,LS

1-Acute Toxicity Endpoint=39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
58

8. Aquatic Plants

The following two tables present the RQs for aquatic plants. No Agency levels of 

concern were exceeded.

PRZM/EXAMS RQs for Vascular Plants from Aerial Spray Application of DPXE2Y45 for Various Crop Types

Scenario

Application

Peak

NonListed

RQ

Listed

RQ

Identified

Rate Concerns

(lbs/A) # Int

FL cabbage 0.065 3 3 2.652 0.0013 0.0013 None

FL cucumber 0.065 3 5 5.693 0.0028 0.0028 None

PA tomato 0.098 2 5 1.513 0.0008 0.0008 None

CA tomato 0.098 2 5 1.080 0.0005 0.0005 None

FL tomato 0.098 2 5 3.660 0.0018 0.0018 None

FL peppers 0.098 2 5 6.749 0.0034 0.0034 None

CA lettuce 0.065 3 3 3.579 0.0018 0.0018 None

CA cotton 0.099 2 5 1.785 0.0009 0.0009 None

NC cotton 0.099 2 5 3.730 0.0019 0.0019 None

MS cotton 0.099 2 5 3.769 0.0019 0.0019 None

NY grape 0.099 2 7 1.389 0.0007 0.0007 None

CA grape 0.099 2 7 1.188 0.0006 0.0006 None

NC apple 0.099 2 10 1.359 0.0007 0.0007 None

PA apple 0.099 2 10 1.245 0.0006 0.0006 None

OR apple 0.099 2 10 0.786 0.0004 0.0004 None

ID potato 0.066 3 5 1.021 0.0005 0.0005 None

ME potato 0.066 3 5 1.558 0.0008 0.0008 None

GA peach 0.099 2 7 1.086 0.0005 0.0005 None

MI Cherry 0.099 2 7 1.035 0.0005 0.0005 None

1-Non-Listed Toxicity Endpoint=> 2,000 μg/L

2-Listed Toxicity Endpoint= 2,000μg/L 

* RQ = EEC/toxicity endpoint

** RQs compared with LOCs for non listed and listed species (1.0)
59

PRZM/EXAMS RQs for Vascular Plants from Ground Spray Application of DPXE2Y45 for Various Crop Types

Scenario

Application

Peak

NonListed

RQ

Listed

RQ

Identified

Rate Concerns

(lbs/A) # Int

FL cabbage 0.065 3 3 2.531 0.0013 0.0013 None

FL cucumber 0.065 3 5 5.624 0.0028 0.0028 None

PA tomato 0.098 2 5 1.280 0.0006 0.0006 None

CA tomato 0.098 2 5 0.731 0.0004 0.0004 None

FL tomato 0.098 2 5 3.436 0.0017 0.0017 None

FL peppers 0.098 2 5 6.501 0.0033 0.0033 None

CA lettuce 0.065 3 3 3.311 0.0017 0.0017 None

CA cotton 0.099 2 5 1.470 0.0007 0.0007 None

NC cotton 0.099 2 5 3.473 0.0017 0.0017 None

MS cotton 0.099 2 5 3.575 0.0018 0.0018 None

NY grape 0.099 2 7 1.189 0.0006 0.0006 None

CA grape 0.099 2 7 0.813 0.0004 0.0004 None

NC apple 0.099 2 10 0.999 0.0005 0.0005 None

PA apple 0.099 2 10 1.048 0.0005 0.0005 None

OR apple 0.099 2 10 0.410 0.0002 0.0002 None

ID potato 0.066 3 5 0.812 0.0004 0.0004 None

ME potato 0.066 3 5 1.350 0.0007 0.0007 None

GA peach 0.099 2 7 0.763 0.0004 0.0004 None

MI Cherry 0.099 2 7 0.867 0.0004 0.0004 None

FLTurf 0.26 2 7 0.837 0.0004 0.0004 None

FL Turf 0.026 19 7 0.753 0.0004 0.0004 None

PA Turf 0.26 2 7 1.102 0.0006 0.0006 None

PA Turf 0.026 19 7 1.625 0.0008 0.0008 None

CA Turf 0.26 2 7 0.654 0.0003 0.0003 None

CA Turf 0.026 19 7 0.766 0.0004 0.0004 None

CA Nursery 0.4992 1 NA 5.663 0.0028 0.0028 None

CA Residential 0.4992 1 NA 1.779 0.0009 0.0009 None

FL Nursery 0.4992 1 NA 9.785 0.0049 0.0049 None

MI Nursery 0.4992 1 NA 2.508 0.0013 0.0013 None

TN Nursery 0.4992 1 NA 10.981 0.0055 0.0055 None

1-Non-Listed Toxicity Endpoint=> 2,000 μg/L

2-Listed Toxicity Endpoint= 2,000 μg/L

* RQ = EEC/toxicity endpoint

** RQs compared with LOCs for non listed and listed species (1.0)
60

PRZM/EXAMS RQs for Unicellular Plants from Aerial Spray Application of DPXE2Y45 for Various Crop Types

Scenario

Application

Peak

NonListed

RQ

Listed

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.652 0.0015 0.0015 None

FL cucumber 0.065 3 5 5.693 0.0032 0.0032 None

PA tomato 0.098 2 5 1.513 0.0009 0.0009 None

CA tomato 0.098 2 5 1.080 0.0006 0.0006 None

FL tomato 0.098 2 5 3.660 0.0021 0.0021 None

FL peppers 0.098 2 5 6.749 0.0038 0.0038 None

CA lettuce 0.065 3 3 3.579 0.0020 0.0020 None

CA cotton 0.099 2 5 1.785 0.0010 0.0010 None

NC cotton 0.099 2 5 3.730 0.0021 0.0021 None

MS cotton 0.099 2 5 3.769 0.0021 0.0021 None

NY grape 0.099 2 7 1.389 0.0008 0.0008 None

CA grape 0.099 2 7 1.188 0.0007 0.0007 None

NC apple 0.099 2 10 1.359 0.0008 0.0008 None

PA apple 0.099 2 10 1.245 0.0007 0.0007 None

OR apple 0.099 2 10 0.786 0.0004 0.0004 None

ID potato 0.066 3 5 1.021 0.0006 0.0006 None

ME potato 0.066 3 5 1.558 0.0009 0.0009 None

GA peach 0.099 2 7 1.086 0.0006 0.0006 None

MI Cherry 0.099 2 7 1.035 0.0006 0.0006 None

1-Non-Listed Toxicity Endpoint=> 1,780 μg/L

2-Listed Toxicity Endpoint= 1780μg/L 

* RQ = EEC/toxicity endpoint

** RQs compared with LOCs for non listed and listed species (1.0)
61

PRZM/EXAMS RQs for Unicellular Plants from Ground Spray Application of DPXE2Y45 for Various Crop Types

Scenario

Application

Peak

NonListed

RQ

Listed

RQ

Identified

Rate Concerns

(lb/A) # Int

FL cabbage 0.065 3 3 2.531 0.0014 0.0014 None

FL cucumber 0.065 3 5 5.624 0.0032 0.0032 None

PA tomato 0.098 2 5 1.280 0.0007 0.0007 None

CA tomato 0.098 2 5 0.731 0.0004 0.0004 None

FL tomato 0.098 2 5 3.436 0.0019 0.0019 None

FL peppers 0.098 2 5 6.501 0.0037 0.0037 None

CA lettuce 0.065 3 3 3.311 0.0019 0.0019 None

CA cotton 0.099 2 5 1.470 0.0008 0.0008 None

NC cotton 0.099 2 5 3.473 0.0020 0.0020 None

MS cotton 0.099 2 5 3.575 0.0020 0.0020 None

NY grape 0.099 2 7 1.189 0.0007 0.0007 None

CA grape 0.099 2 7 0.813 0.0005 0.0005 None

NC apple 0.099 2 10 0.999 0.0006 0.0006 None

PA apple 0.099 2 10 1.048 0.0006 0.0006 None

OR apple 0.099 2 10 0.410 0.0002 0.0002 None

ID potato 0.066 3 5 0.812 0.0005 0.0005 None

ME potato 0.066 3 5 1.350 0.0008 0.0008 None

GA peach 0.099 2 7 0.763 0.0004 0.0004 None

MI Cherry 0.099 2 7 0.867 0.0005 0.0005 None

FLTurf 0.26 2 7 0.837 0.0005 0.0005 None

FL Turf 0.026 19 7 0.753 0.0004 0.0004 None

PA Turf 0.26 2 7 1.102 0.0006 0.0006 None

PA Turf 0.026 19 7 1.625 0.0009 0.0009 None

CA Turf 0.26 2 7 0.654 0.0004 0.0004 None

CA Turf 0.026 19 7 0.766 0.0004 0.0004 None

CA Nursery 0.4992 1 NA 5.663 0.0032 0.0032 None

CA Residential 0.4992 1 NA 1.779 0.0010 0.0010 None

FL Nursery 0.4992 1 NA 9.785 0.0055 0.0055 None

MI Nursery 0.4992 1 NA 2.508 0.0014 0.0014 None

TN Nursery 0.4992 1 NA 10.981 0.0062 0.0062 None

1-Non-Listed Toxicity Endpoint=> 1,780 μg/L

2-Listed Toxicity Endpoint= 1,780 μg/L

* RQ = EEC/toxicity endpoint

** RQs compared with LOCs for non listed and listed species (1.0
62

B. Risk Discussion

1. Quantified Risks

The primary concerns for quantifiable risks associated with this pesticide are for acute 

and chronic effects to aquatic invertebrates. The following table presents the proposed 

Section 3 uses associated with RQ estimates for the model scenarios included in the 

quantitative freshwater invertebrate risk assessment.

Tier II RQs for FW Invertebrates from Aerial Spray Application of DPX-E2Y45 for Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Concerns lb/A # Int

FL cabbage 0.065 3 3 2.652 2.146 0.1850 0.4801 RU,LS

FL cucumber 0.065 3 5 5.693 4.939 0.4258 1.1049 RU,LS, C

PA tomato 0.098 2 5 1.513 1.306 0.1126 0.2922 RU,LS

CA tomato 0.098 2 5 1.080 0.922 0.0795 0.2063 LS

FL tomato 0.098 2 5 3.660 3.001 0.2587 0.6714 RU,LS

FL peppers 0.098 2 5 6.749 5.683 0.4899 1.2714 RU,LS, C

CA lettuce 0.065 3 3 3.579 2.997 0.2584 0.6705 RU,LS

CA cotton 0.099 2 5 1.785 1.576 0.1359 0.3526 RU,LS

NC cotton 0.099 2 5 3.730 3.207 0.2765 0.7174 RU,LS

MS cotton 0.099 2 5 3.769 3.271 0.2820 0.7318 RU,LS

NY grape 0.099 2 7 1.389 1.197 0.1032 0.2678 RU,LS

CA grape 0.099 2 7 1.188 1.026 0.0884 0.2295 LS

NC apple 0.099 2 10 1.359 1.153 0.0994 0.2579 LS

PA apple 0.099 2 10 1.245 1.091 0.0941 0.2441 LS

OR apple 0.099 2 10 0.786 0.674 0.0581 0.1508 LS

ID potato 0.066 3 5 1.021 0.859 0.0741 0.1922 LS

ME potato 0.066 3 5 1.558 1.392 0.1200 0.3114 RU,LS

GA peach 0.099 2 7 1.086 0.886 0.0764 0.1982 LS

MI Cherry 0.099 2 7 1.035 0.907 0.0782 0.2029 LS

1-Acute Toxicity Endpoint= 11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
63

Tier II RQs for FW Invertebrates from Ground Spray Application of DPX-E2Y45 for Various Crop 

Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Concerns lb/a # Int

FL cabbage 0.065 3 3 2.531 2.045 0.1763 0.4575 RU,LS

FL cucumber 0.065 3 5 5.624 4.86 0.4190 1.0872 RU,LS, 

PA tomato 0.098 2 5 1.280 1.097 0.0946 0.2454 LS

CA tomato 0.098 2 5 0.731 0.619 0.0534 0.1385 LS

FL tomato 0.098 2 5 3.436 2.817 0.2428 0.6302 RU,LS

FL peppers 0.098 2 5 6.501 5.475 0.4720 1.2248 RU,LS, C

CA lettuce 0.065 3 3 3.311 2.781 0.2397 0.6221 RU,LS

CA cotton 0.099 2 5 1.470 1.28 0.1103 0.2864 RU,LS

NC cotton 0.099 2 5 3.473 2.995 0.2582 0.6700 RU,LS

MS cotton 0.099 2 5 3.575 3.116 0.2686 0.6971 RU,LS

NY grape 0.099 2 7 1.189 1.025 0.0884 0.2293 LS

CA grape 0.099 2 7 0.813 0.706 0.0609 0.1579 LS

NC apple 0.099 2 10 0.999 0.852 0.0734 0.1906 LS

PA apple 0.099 2 10 1.048 0.898 0.0774 0.2009 LS

OR apple 0.099 2 10 0.410 0.365 0.0315 0.0817 None

ID potato 0.066 3 5 0.812 0.68 0.0586 0.1521 LS

ME potato 0.066 3 5 1.350 1.195 0.1030 0.2673 RU,LS

GA peach 0.099 2 7 0.763 0.62 0.0534 0.1387 LS

MI Cherry 0.099 2 7 0.867 0.739 0.0637 0.1653 LS

FLTurf 0.26 2 7 0.837 0.707 0.0609 0.1582 LS

PA Turf 0.26 2 7 1.102 0.985 0.0849 0.2204 LS

CA Turf 0.26 2 7 0.654 0.554 0.0478 0.1239 None

CA Nursery 0.4992 1 NA 5.663 4.672 0.4028 1.0452 RU,LS, C

CA Residential 0.4992 1 NA 1.779 1.543 0.1330 0.3452 RU,LS

FL Nursery 0.4992 1 NA 9.785 8.136 0.7014 1.8201 RU,LS, C

MI Nursery 0.4992 1 NA 2.508 2.284 0.1969 0.5110 RU,LS

TN Nursery 0.4992 1 NA 10.981 9.126 0.7867 2.0416 RU,LS, C

1-Acute Toxicity Endpoint=11.6 μg/L

2-Chronic Toxicity Endpoint= 4.47 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
64

Acute concerns are triggered by freshwater invertebrate RQ values for every exposure

scenario modeled except the CA turf (ground spray) and OR apple (ground spray). These 

concerns are limited primarily to acute effects to listed species and RQ values that are 

sufficiently high to raise non-listed species concerns but within the manageable range for 

restricted use considerations. However, even for these proposed Section 3 uses, the 

restricted use concern level is just barely exceeded and no exposure estimate reaches the 

median lethal concentration for the most sensitive species tested. 

Chronic freshwater invertebrate risk concerns were identified for proposed uses on FL 

peppers (ground or aerial spray), FL cucumbers (ground or aerial spray), CA nursery

(ground spray), FL nursery (ground spray), and TN nursery (ground spray). In all cases 

the RQs were less than an order of magnitude above the Agency concern level. 

Concerns to estuarine/marine invertebrates that exceed Agency concern levels are 

confined to the following Tier II modeling scenarios: FL cabbage (aerial or ground 

spray), FL cucumber (aerial or ground spray), FL peppers (aerial or ground spray), FL 

tomatoes (aerial spray), CA lettuce (ground and aerial spray), NC cotton (aerial or 

ground spray), MS cotton (aerial or ground spray) CA nursery (ground spray), TN 

nursery (ground spray), FL nursery (ground spray), and MI nursery (ground spray). 

These risks are generally limited to acute effects to listed species. However, the restricted 

use LOCs are exceeded for the Florida vegetable scenarios (cucumber, peppers) and 

nursery use scenarios (CA nursery, TN nursery, and FL nursery scenarios). 
65

Tier II RQs for Estuarine/Marine Invertebrates from Aerial Spray Application of DPX-E2Y45 for 

Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Concerns lb/a # Int

FL cabbage 0.065 3 3 2.652 2.146 0.0538 0.0894 LS

FL cucumber 0.065 3 5 5.693 4.939 0.1238 0.2058 RU,LS

PA tomato 0.098 2 5 1.513 1.306 0.0327 0.0544 None

CA tomato 0.098 2 5 1.080 0.922 0.0231 0.0384 None

FL tomato 0.098 2 5 3.660 3.001 0.0752 0.1250 LS

FL peppers 0.098 2 5 6.749 5.683 0.1424 0.2368 RU,LS

CA lettuce 0.065 3 3 3.579 2.997 0.0751 0.1249 LS

CA cotton 0.099 2 5 1.785 1.576 0.0395 0.0657 None

NC cotton 0.099 2 5 3.730 3.207 0.0804 0.1336 LS

MS cotton 0.099 2 5 3.769 3.271 0.0820 0.1363 LS

NY grape 0.099 2 7 1.389 1.197 0.0300 0.0499 None

CA grape 0.099 2 7 1.188 1.026 0.0257 0.0428 None

NC apple 0.099 2 10 1.359 1.153 0.0289 0.0480 None

PA apple 0.099 2 10 1.245 1.091 0.0273 0.0455 None

OR apple 0.099 2 10 0.786 0.674 0.0169 0.0281 None

ID potato 0.066 3 5 1.021 0.859 0.0215 0.0358 None

ME potato 0.066 3 5 1.558 1.392 0.0349 0.0580 None

GA peach 0.099 2 7 1.086 0.886 0.0222 0.0369 None

MI Cherry 0.099 2 7 1.035 0.907 0.0227 0.0378 None

1-Acute Toxicity Endpoint= 39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
66

Tier II RQs for Estuarine/Marine Invertebrates from Ground Spray Application of DPX-E2Y45 for 

Various Crop Types 

Scenario

Application

Peak 21-day

Average

Acute1

RQ

Chronic2

RQ

Identified

Concerns lb/A # Int

FL cabbage 0.065 3 3 2.531 2.045 0.0513 0.0852 LS

FL cucumber 0.065 3 5 5.624 4.86 0.1218 0.2025 RU,LS

PA tomato 0.098 2 5 1.280 1.097 0.0275 0.0457 None

CA tomato 0.098 2 5 0.731 0.619 0.0155 0.0258 None

FL tomato 0.098 2 5 3.436 2.817 0.0706 0.1174 None

FL peppers 0.098 2 5 6.501 5.475 0.1372 0.2281 RU,LS

CA lettuce 0.065 3 3 3.311 2.781 0.0697 0.1159 LS

CA cotton 0.099 2 5 1.470 1.28 0.0321 0.0533 None

NC cotton 0.099 2 5 3.473 2.995 0.0751 0.1248 LS

MS cotton 0.099 2 5 3.575 3.116 0.0781 0.1298 LS

NY grape 0.099 2 7 1.189 1.025 0.0257 0.0427 None

CA grape 0.099 2 7 0.813 0.706 0.0177 0.0294 None

NC apple 0.099 2 10 0.999 0.852 0.0214 0.0355 None

PA apple 0.099 2 10 1.048 0.898 0.0225 0.0374 None

OR apple 0.099 2 10 0.410 0.365 0.0091 0.0152 None

ID potato 0.066 3 5 0.812 0.68 0.0170 0.0283 None

ME potato 0.066 3 5 1.350 1.195 0.0299 0.0498 None

GA peach 0.099 2 7 0.763 0.62 0.0155 0.0258 None

MI Cherry 0.099 2 7 0.867 0.739 0.0185 0.0308 None

FLTurf 0.26 2 7 0.837 0.707 0.0177 0.0295 None

PA Turf 0.26 2 7 1.102 0.985 0.0247 0.0410 None

CA Turf 0.26 2 7 0.654 0.554 0.0139 0.0231 None

CA Nursery 0.4992 1 NA 5.663 4.672 0.1171 0.1947 RU,LS

CA Residential 0.4992 1 NA 1.779 1.543 0.0387 0.0643 None

FL Nursery 0.4992 1 NA 9.785 8.136 0.2039 0.3390 RU,LS

MI Nursery 0.4992 1 NA 2.508 2.284 0.0572 0.0952 LS

TN Nursery 0.4992 1 NA 10.981 9.126 0.2287 0.3803 RU,LS

1-Acute Toxicity Endpoint=39.9 μg/L

2-Chronic Toxicity Endpoint= 24 μg/L 

* RQ = EEC/toxicity endpoint

** Acute RQs compared with acute LOCs for non listed species (0.5), restricted use (0.1), and listed species (0.05). Chronic RQs 

compared with chronic LOC of 1.
67

2. Qualitative Discussion of Terrestrial Plant Risks

The lack of definitive EC5 or NOEC values for terrestrial plants renders the risk 

conclusions for plants uncertain. 

Inhibition of seedling emergence was reduced 5 to 34% for monocot plant species tested 

and from 0 to 18% for dicot species tested. Non-listed species RQs are within a fiftieth 

of Agency concern levels and within a twentieth of listed species concerns, suggesting 

that the dose/response curve for seedling emergence would have to be unusually steep for 

predicted exposures to exceed non-listed plant concern levels. Confidence in the lack of 

risk concerns for listed species is less than for non-listed plants, primarily because most 

species tested at single concentration in the seedling emergence study exhibited effects 

well in excess for the maximum 5% acceptable level for listed species. Even though 

exposures were well below the tested concentration, the confidence in predicting that 

they would be associated with below a 5% or less effect response is uncertain.

Similar statements can be made for risk predictions based on vegetative vigor effects 

data, except that confidence that no non-listed plant effects are expected as no tested 

monocot or dicot even approached the 25% effects level that would trigger non-listed 

plant concerns. However, listed plant RQ values are beyond an order of magnitude of 

concern levels, but the finding that available effects data show response as high as 12% 

inhibition in vegetative growth it is uncertain whether predicted exposures would fall 

below thresholds triggering concern for listed species (i.e., effects at or below 5%).

Consequently listed species plant concerns cannot be dismissed with available data.

3. Qualitative Discussion of Terrestrial Invertebrate Risks

The Agency currently does not have a quantitative method to assess risks of pesticides to 

non-target terrestrial invertebrates. At first principles, it would appear reasonable that an 

insecticide would pose some risk to non-target terrestrial invertebrates, including nontarget insects. The highest application rate of chlorantraniliprole in a year is on the order 

of 200 g/ha. Comparing this application rate to the available insect toxicity data 

expressed in g of pesticide per hectare suggests that acute effects on some insects (e.g. 

hoverfly, ladybird beetles, and lacewings) are possible. Therefore, the screening level 

risk assessment conclusion is that effects on non-target insects cannot be precluded. 
68

VI. FEDERALLY LISTED THREATENED AND ENDANGERED SPECIES 

ASSESSMENT

A. Action Area

For listed species assessment purposes, the action area is considered to be the area 

affected directly or indirectly by the Federal action and not merely the immediate area 

involved in the action. At the initial screening-level, the risk assessment considers 

broadly described taxonomic groups and conservatively assumes that listed species 

within those broad groups are located on or adjacent to the treated site and aquatic 

organisms are assumed to be located in a surface water body adjacent to the treated site. 

The assessment also assumes that the listed species are located within an assumed area 

which has the relatively highest potential exposure to the pesticide, and that exposures are 

likely to decrease with distance from the treatment area. 

If the assumptions associated with the screening-level action area result in RQs that are 

below the listed species LOCs, a "no effect" determination conclusion is made with 

respect to listed species in that taxonomic group, and no further refinement of the action 

area is necessary. Furthermore, RQs below the listed species LOCs for a given 

taxonomic group indicate no concern for indirect effects upon listed species that depend 

upon the taxonomic group covered by the RQ as a resource. However, in situations 

where the screening assumptions lead to RQs in excess of the listed species LOCs for a 

given taxonomic group, a potential for a "may affect" conclusion exists and may be 

associated with direct effects on listed species belonging to that taxonomic group or may

extend to indirect effects upon listed species that depend upon that taxonomic group as a 

resource. In such cases, additional information on the biology of listed species, the 

locations of these species, and the locations of use sites could be considered to determine 

the extent to which screening assumptions regarding an action area apply to a particular 

listed organism. These subsequent refinement steps could consider how this information 

would impact the action area for a particular listed organism and may potentially include 

areas of exposure that are downwind and downstream of the pesticide use site.
69

B. Taxonomic Groups Potentially at Risk

The Level I screening assessment process for listed species employs the generic 

taxonomic group-based process to make inferences on direct effect concerns for listed 

species. The first iteration of reporting the results of the Level I screening is a listing of 

pesticide use sites and taxonomic groups for which RQ calculations reveal values that 

meet or exceed the listed species LOCs. An evaluation of risk conclusions for each 

taxonomic group is presented below.

Potential Effects to Federally Listed Taxa

Listed Taxa

Direct 

Effects

Scenario Identified as of 

Concern

Indirect 

Effects

Scenario Identified as of 

Concern

Terrestrial and semiaquatic plants -

monocots

Yes4 Yes1all

Terrestrial and semiaquatic plants - dicots Yes4 Yes1

all

Terrestrial invertebrates Yes all No

Birds No Yes1,2,3,5 All 

Terrestrial phase 

amphibians No Yes1,2,5 All 

Reptiles No Yes1,2,3,5 All 

Mammals No Yes1,2,3,5 All 

Aquatic vascular plants No No

Freshwater fish No Yes2,5 All 

Aquatic phase 

amphibians No Yes2,5 All 

Freshwater crustaceans Yes

All except CA turf

(ground spray) and OR 

apple (ground spray)

Yes2,5 All

Mollusks

Yes(may be 

subject to 

further 

evaluation)

All except CA turf

(ground spray) and OR 

apple (ground spray) Yes2,5 All

Marine/estuarine fish No Yes3

FL cabbage, FL cucumber, 

FL pepper, NC cotton, MS 

cotton, CA lettuce, CA nursery, 

FL nursery, MI nursery, TN 

nursery

Marine/estuarine 

invertebrates Yes

FL cabbage, FL cucumber, 

FL pepper, NC cotton, MS 

cotton, CA lettuce, CA nursery, 

FL nursery, MI nursery, TN 

nursery

No

1 direct effects on terrestrial invertebrates

2 direct effects on aquatic invertebrates

3 direct effects on estuarine/marine invertebrates

4

insufficient data to preclude risk

5

direct effects to terrestrial plants at the listed species level of concern suggests concern of animals with obligate relationships to a 

plant species
70

C. Analysis of Dose Response (Effects Study Slope)

There was insufficient information in the PSD data reviews to establish a definitive slope 

for acute toxicity studies supplying endpoints for the calculation of risk quotients. An 

assumed typical probit slope of 4.5 and an assumed range of 2 to 9 for this slope estimate 

were used to estimate of individual mortality at when exposures for a taxonomic group

are at the listed species LOC. Data for freshwater invertebrates provided both a 

geometric mean slope and a range of measured values. These were used to estimate the 

changes of individual morality for the freshwater invertebrate taxonomic group.

Slopes for animal endpoints and associated chance of individual mortality 

associated with RQ = Acute Listed Species LOC

Taxa/acute 

study

Slope Chance of 

Individual 

Mortality at 

RQ= Listed 

Species 

LOC

Confidence Intervals

Assumed slopes use slope interval 2 to 9

Measured slopes use measured range

Bird oral dose

No mortality 

observed

Not 

calculated, 

no mortality 

observed

Not calculated, no mortality observed

Bird dietary No mortality 

observed

Not 

calculated, 

no mortality 

observed

Not calculated, no mortality observed

Mammal oral 

dose

No mortality 

observed

Not 

calculated, 

no mortality 

observed

Not calculated, no mortality observed

Freshwater fish No mortality 

observed

Not 

calculated, 

no mortality 

observed

Not calculated, no mortality observed

Freshwater 

invertebrate

Assume 4.5 1 in 

4.75E+02

1 in 1.73E+01 to 1 in 1.27E+03

Estuarine/marine 

fish

No mortality 

observed

Not 

calculated, 

no mortality 

observed

Not calculated, no mortality observed

Estuarine/marine 

invertebrate

Assume 4.5 1 in 

4.18E+08

1 in 2.16E+02 to <<1 in 1.0 E+16
71

D. Consideration of Alternative Assumptions of Drift

In keeping with Agency policy, this screening risk assessment’s aquatic exposure 

modeling assumes that spray drift loading to adjacent aquatic systems comprises 5% 

(aerial application scenarios) and 1% (ground application scenarios) of the field 

application rate. In order to see how important drift was to the ecological risk assessment 

estimates, the aquatic exposure model was run both with assumed drift and without for 

maximum single aerial application. As can be seen from the following able, drift 

accounts for 6% to 78% of estimated aquatic concentrations, depending on the site and 

the averaging time. This would suggest that alternative assumption drift could have 

impact on the overall risk estimation values. 

Comparison of Surface Water Concentration Model Results With and Without a 5% 

Drift Assumption

Scenario

Peak EEC 21 day average EEC 60 day average EEC

with drift without 

drift

Fraction 

of total as 

drift

with drift without 

drift

Fraction 

of total as 

drift

with drift without 

drift

Fraction 

of total as 

drift

FL cabbage 2.652 2.376 0.10 2.146 1.920 0.11 1.466 1.236 0.16

FL cucumber 5.693 5.327 0.06 4.939 4.598 0.07 3.748 3.497 0.07

PA tomato 1.513 1.159 0.23 1.306 0.994 0.24 1.136 0.828 0.27

CA tomato 1.080 0.625 0.42 0.922 0.519 0.44 0.702 0.391 0.44

FL tomato 3.660 3.212 0.12 3.001 2.632 0.12 2.312 2.058 0.11

FL peppers 6.749 6.117 0.09 5.683 5.152 0.09 4.425 3.976 0.10

CA lettuce 3.579 3.038 0.15 2.997 2.590 0.14 2.203 1.92 0.13

CA cotton 1.785 1.330 0.25 1.576 1.147 0.27 1.229 0.901 0.27

NC cotton 3.730 3,240 0.13 3.207 2.795 0.13 2.584 2.288 0.11

MS cotton 3.769 3.352 0.11 3.271 2.924 0.11 2.633 2.308 0.12

NY grape 1.389 1.085 0.22 1.197 0.936 0.22 1.041 0.797 0.23

CA grape 1.188 0.287 0.76 1.026 0.234 0.77 0.791 0.174 0.78

NC apple 1.359 0.864 0.36 1.153 0.738 0.36 0.917 0.600 0.35

PA apple 1.245 0.935 0.25 1.091 0.802 0.26 0.857 0.647 0.25

OR apple 0.786 0.377 0.52 0.674 0.334 0.50 0.558 0.278 0.50

ID potato 1.021 0.722 0.29 0.859 0.603 0.30 0.707 0.452 0.36

ME potato 1.558 1.264 0.19 1.392 1.106 0.21 1.319 0.983 0.25

GA peach 1.086 0.647 0.40 0.886 0.526 0.41 0.655 0.379 0.42

MI Cherry 1.035 0.793 0.23 0.907 0.674 0.26 0.758 0.531 0.30

AgDrift modeling at the Tier 1 series of assumptions shows that water bodies (the 

standard assessment pond) adjacent to sprayed fields may receive between 6.99% (coarse 

spray) to 24.25% (very fine spray) of the aerially applied field rate through spray drift. 

These values would raise loadings from the assumed 5% by factors ranging from 1.4 to 

4.9. Assuming a range of 6% to 78 % of total loadings could be attributable to drift, 

accounting for higher drift fractions could increase EEC estimates and resulting RQ 

values by 1 to 3X. These values would be insufficient to trigger any additional concerns 

for aquatic vertebrates. It could increase freshwater invertebrate risks to include a more 

frequent triggering of the non-listed acute risk concern. Higher drift assumptions could 

increase the number of sites triggering listed species acute concerns for estuarine/marine 

invertebrates. However, without more site-specific evaluations, it is not possible to 

ascertain which additional use areas would be of concern for estuarine marine 

invertebrate risks.
72

E. Critical Habitat

In the evaluation of pesticide effects on designated critical habitat, consideration is given 

to the physical and biological features (primary constituent elements) of a critical habitat 

identified by the U.S Fish and Wildlife and National Marine Fisheries Services as 

essential to the conservation of a listed species and which may require special 

management considerations or protection. The evaluation of impacts for a screening 

level pesticide risk assessment focuses on the biological features that are primary

constituent elements and is accomplished using the screening-level taxonomic analysis 

(RQs) and listed species’ levels of concern (LOCs) that are used to evaluate direct and 

indirect effects to listed organisms.

The screening-level risk assessment for chlorantraniliprole has identified potential 

concerns for direct and indirect effects on listed species for those organisms dependant 

upon a variety of taxonomic groups. In light of the potential for indirect effects, the next 

step for EPA and the Service(s) is to identify which listed species and critical habitat are 

potentially implicated.

Analytically, the identification of such species and critical habitat can occur in either of 

two ways. First, the agencies could determine whether the action area overlaps critical 

habitat or the occupied range of any listed species. If so, EPA would examine whether 

the pesticide's potential impacts on non-endangered species would affect the listed 

species indirectly or directly affect a primary constituent element of the critical habitat. 

Alternatively, the agencies could determine which listed species depend on biological 

resources, or have constituent elements that fall into the taxa that may be directly or 

indirectly impacted by a pesticide. Then EPA would determine whether or not use of the 

pesticide overlaps the critical habitat or the occupied range of those listed species. At 

present, the information reviewed by EPA is not sufficient to permit use of either 

analytical approach to make a definitive identification of species that are potentially

impacted indirectly or critical habitats that are potentially impacted directly by the use of 

pesticides. EPA and the Service(s) are working together to conduct the necessary

analysis.

This screening-level risk assessment for critical habitat provides a listing of potential 

biological features that, if they are primary constituent elements of one or more critical 

habitats, would be of potential concern. Risk to a variety of taxa exceeded the LOCs; 

therefore, they were identified as being of potential concern for indirect effects. These 

results may be used to develop a problem formulation for further assessment of critical 

habitat impacts outlined above, should additional work be necessary.
73

F. Co-Location Analysis

Appended to this document is a listing of federally listed threatened and endangered 

species from the direct and indirect potentially affected taxonomic groups. This list was 

generated using the Agency’s LOCATES database.
74

APPENDIX A

Available Structures for Degradates
75
76
77
78
79
80

APPENDIX B-PRZM-EXAMS OUTPUT

APPENDIX

PRZM/EXAM OUTPUT

Surface Water Modeling

CA Nursey

stored as CAnursey.out

Chemical: DPXE2Y45

PRZM environment: CAnurserySTD.txt modified Wedday, 24 January 2007 at 09:18:18

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23188.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3087 0.2961 0.2598 0.1896 0.155 0.07079

1962 0.3588 0.3454 0.2966 0.2215 0.1848 0.08507

1963 0.8084 0.7755 0.6574 0.4897 0.4217 0.1773

1964 0.2993 0.2872 0.2436 0.1929 0.161 0.0639

1965 1.278 1.229 1.054 0.8463 0.7108 0.2686

1966 1.919 1.838 1.546 1.306 1.131 0.3364

1967 0.8282 0.802 0.7058 0.5636 0.556 0.2682

1968 4.709 4.516 3.824 2.771 2.274 0.8007

1969 0.4603 0.4432 0.3816 0.2895 0.2845 0.1361

1970 0.7214 0.6923 0.5879 0.4391 0.3612 0.148

1971 0.8821 0.8482 0.7259 0.5475 0.4586 0.2294

1972 0.3687 0.3576 0.3057 0.219 0.1755 0.1099

1973 0.8953 0.8636 0.7887 0.6198 0.5252 0.2212

1974 0.9828 0.9462 0.816 0.6005 0.4991 0.2207

1975 4.22 4.069 3.6 2.676 2.221 0.8166

1976 1.266 1.215 1.032 0.8465 0.7557 0.3072

1977 2.485 2.39 2.046 1.521 1.251 0.5434

1978 2.242 2.167 1.998 1.531 1.267 0.4622

1979 1.146 1.101 0.9936 0.8308 0.6962 0.2562

1980 1.799 1.725 1.46 1.094 0.9067 0.3227

1981 7.807 7.505 6.723 5.058 4.202 1.474

1982 5.768 5.552 4.766 3.575 2.99 1.103

1983 5.796 5.614 4.828 3.586 2.953 1.055

1984 0.3583 0.3446 0.2953 0.2338 0.1988 0.09669

1985 1.667 1.599 1.445 1.017 0.6826 0.2238

1986 1.542 1.506 1.345 1.075 0.9133 0.4214

1987 0.5282 0.5075 0.4328 0.3233 0.2951 0.1451

1988 1.896 1.821 1.561 1.134 0.9401 0.3569

1989 0.8781 0.8427 0.7164 0.5272 0.4413 0.1864

1990 0.5054 0.4894 0.437 0.3371 0.3495 0.1661

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 7.807 7.505 6.723 5.058 4.202 1.474

0.0645161290322581 5.796 5.614 4.828 3.586 2.99 1.103

0.0967741935483871 5.768 5.552 4.766 3.575 2.953 1.055

0.129032258064516 4.709 4.516 3.824 2.771 2.274 0.8166

0.161290322580645 4.22 4.069 3.6 2.676 2.221 0.8007

0.193548387096774 2.485 2.39 2.046 1.531 1.267 0.5434

0.225806451612903 2.242 2.167 1.998 1.521 1.251 0.4622

0.258064516129032 1.919 1.838 1.561 1.306 1.131 0.4214
81

0.290322580645161 1.896 1.821 1.546 1.134 0.9401 0.3569

0.32258064516129 1.799 1.725 1.46 1.094 0.9133 0.3364

0.354838709677419 1.667 1.599 1.445 1.075 0.9067 0.3227

0.387096774193548 1.542 1.506 1.345 1.017 0.7557 0.3072

0.419354838709677 1.278 1.229 1.054 0.8465 0.7108 0.2686

0.451612903225806 1.266 1.215 1.032 0.8463 0.6962 0.2682

0.483870967741936 1.146 1.101 0.9936 0.8308 0.6826 0.2562

0.516129032258065 0.9828 0.9462 0.816 0.6198 0.556 0.2294

0.548387096774194 0.8953 0.8636 0.7887 0.6005 0.5252 0.2238

0.580645161290323 0.8821 0.8482 0.7259 0.5636 0.4991 0.2212

0.612903225806452 0.8781 0.8427 0.7164 0.5475 0.4586 0.2207

0.645161290322581 0.8282 0.802 0.7058 0.5272 0.4413 0.1864

0.67741935483871 0.8084 0.7755 0.6574 0.4897 0.4217 0.1773

0.709677419354839 0.7214 0.6923 0.5879 0.4391 0.3612 0.1661

0.741935483870968 0.5282 0.5075 0.437 0.3371 0.3495 0.148

0.774193548387097 0.5054 0.4894 0.4328 0.3233 0.2951 0.1451

0.806451612903226 0.4603 0.4432 0.3816 0.2895 0.2845 0.1361

0.838709677419355 0.3687 0.3576 0.3057 0.2338 0.1988 0.1099

0.870967741935484 0.3588 0.3454 0.2966 0.2215 0.1848 0.09669

0.903225806451613 0.3583 0.3446 0.2953 0.219 0.1755 0.08507

0.935483870967742 0.3087 0.2961 0.2598 0.1929 0.161 0.07079

0.967741935483871 0.2993 0.2872 0.2436 0.1896 0.155 0.0639

0.1 5.6621 5.4484 4.6718 3.4946 2.8851 1.03116

Average of yearly averages: 0.369098333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAnursey

Metfile: w23188.dvf

PRZM scenario: CAnurserySTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.5591 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-3 dd/mm or dd/mmm or dd-mm or dd-mmm

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Residential

stored as CAresidential.out

Chemical: DPXE2Y45

PRZM environment: CAresidential.txt modified Tueday, 20 February 2007 at 12:04:34

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23234.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)
82

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5404 0.5281 0.4654 0.4019 0.38 0.2314

1962 1.562 1.529 1.388 1.129 0.9753 0.4413

1963 1.781 1.717 1.546 1.272 1.165 0.5281

1964 1.628 1.589 1.374 1.024 0.8675 0.4046

1965 0.5824 0.5671 0.5065 0.415 0.3696 0.2223

1966 0.514 0.4982 0.4638 0.3742 0.3476 0.2211

1967 3.914 3.777 3.582 2.753 2.367 0.9559

1968 1.234 1.193 1.06 0.8829 0.7864 0.3947

1969 1.288 1.257 1.183 1.082 0.9418 0.4011

1970 1.405 1.374 1.264 1.007 0.8713 0.3842

1971 0.4374 0.4227 0.3947 0.3497 0.3327 0.2185

1972 0.3352 0.3234 0.2805 0.2556 0.2482 0.1846

1973 1.759 1.699 1.5 1.341 1.187 0.5039

1974 0.6929 0.6693 0.5862 0.4708 0.4481 0.2708

1975 0.7903 0.7655 0.6905 0.5696 0.5511 0.2978

1976 0.604 0.582 0.523 0.4394 0.4065 0.2403

1977 1.063 1.023 0.8787 0.671 0.5996 0.3292

1978 1.357 1.32 1.186 1.145 1.086 0.5018

1979 1.71 1.655 1.515 1.39 1.268 0.5621

1980 1.089 1.055 1.012 0.8784 0.8343 0.3913

1981 1.281 1.237 1.083 0.8581 0.7571 0.3527

1982 5.073 4.877 4.168 3.236 2.804 1.172

1983 1.419 1.371 1.264 1.108 0.9981 0.4348

1984 0.3464 0.3342 0.2898 0.2574 0.2501 0.179

1985 0.6526 0.627 0.5521 0.4792 0.4478 0.2562

1986 1.462 1.411 1.249 1.126 0.9797 0.4383

1987 0.8782 0.8472 0.7545 0.6033 0.5688 0.3157

1988 0.4931 0.4772 0.4254 0.3766 0.3514 0.2265

1989 0.3303 0.318 0.2735 0.2323 0.2258 0.1685

1990 0.5572 0.5378 0.4669 0.4006 0.3756 0.2349

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 5.073 4.877 4.168 3.236 2.804 1.172

0.0645161290322581 3.914 3.777 3.582 2.753 2.367 0.9559

0.0967741935483871 1.781 1.717 1.546 1.39 1.268 0.5621

0.129032258064516 1.759 1.699 1.515 1.341 1.187 0.5281

0.161290322580645 1.71 1.655 1.5 1.272 1.165 0.5039

0.193548387096774 1.628 1.589 1.388 1.145 1.086 0.5018

0.225806451612903 1.562 1.529 1.374 1.129 0.9981 0.4413

0.258064516129032 1.462 1.411 1.264 1.126 0.9797 0.4383

0.290322580645161 1.419 1.374 1.264 1.108 0.9753 0.4348

0.32258064516129 1.405 1.371 1.249 1.082 0.9418 0.4046

0.354838709677419 1.357 1.32 1.186 1.024 0.8713 0.4011

0.387096774193548 1.288 1.257 1.183 1.007 0.8675 0.3947

0.419354838709677 1.281 1.237 1.083 0.8829 0.8343 0.3913

0.451612903225806 1.234 1.193 1.06 0.8784 0.7864 0.3842

0.483870967741936 1.089 1.055 1.012 0.8581 0.7571 0.3527

0.516129032258065 1.063 1.023 0.8787 0.671 0.5996 0.3292

0.548387096774194 0.8782 0.8472 0.7545 0.6033 0.5688 0.3157

0.580645161290323 0.7903 0.7655 0.6905 0.5696 0.5511 0.2978

0.612903225806452 0.6929 0.6693 0.5862 0.4792 0.4481 0.2708

0.645161290322581 0.6526 0.627 0.5521 0.4708 0.4478 0.2562

0.67741935483871 0.604 0.582 0.523 0.4394 0.4065 0.2403

0.709677419354839 0.5824 0.5671 0.5065 0.415 0.38 0.2349

0.741935483870968 0.5572 0.5378 0.4669 0.4019 0.3756 0.2314

0.774193548387097 0.5404 0.5281 0.4654 0.4006 0.3696 0.2265

0.806451612903226 0.514 0.4982 0.4638 0.3766 0.3514 0.2223

0.838709677419355 0.4931 0.4772 0.4254 0.3742 0.3476 0.2211

0.870967741935484 0.4374 0.4227 0.3947 0.3497 0.3327 0.2185

0.903225806451613 0.3464 0.3342 0.2898 0.2574 0.2501 0.1846

0.935483870967742 0.3352 0.3234 0.2805 0.2556 0.2482 0.179

0.967741935483871 0.3303 0.318 0.2735 0.2323 0.2258 0.1685

0.1 1.7788 1.7152 1.5429 1.3851 1.2599 0.5587

Average of yearly averages: 0.38212

Inputs generated by pe5.pl - Novemeber 2006
83

Data used for this run:

Output File: CAresidential

Metfile: w23234.dvf

PRZM scenario: CAresidential.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.5591 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-1 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval days Set to 0 or delete line for single app.

app. rate 1 apprate kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Cotton

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:12

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.527 0.506 0.4303 0.3275 0.2753 0.09387

1962 0.5664 0.5479 0.4758 0.3683 0.3059 0.1042

1963 1.04 1.001 0.9082 0.7729 0.6652 0.2561

1964 0.5514 0.5278 0.4462 0.3358 0.2783 0.09922

1965 2.888 2.774 2.37 1.79 1.464 0.5119

1966 0.5761 0.5549 0.4758 0.3581 0.2952 0.1081

1967 0.9171 0.8842 0.7675 0.607 0.5365 0.1948

1968 0.71 0.6859 0.5944 0.5486 0.4689 0.1644

1969 2.595 2.508 2.144 1.581 1.305 0.4404

1970 1.766 1.717 1.509 1.098 0.9047 0.3138

1971 0.6536 0.6282 0.537 0.4002 0.411 0.1705

1972 0.545 0.5242 0.4452 0.3273 0.2687 0.09284

1973 0.8286 0.8014 0.7123 0.5682 0.475 0.1637

1974 0.6707 0.6469 0.5602 0.4829 0.4135 0.1448

1975 0.5399 0.5199 0.4524 0.362 0.3051 0.1055

1976 0.5442 0.5238 0.4639 0.3495 0.2896 0.09897

1977 0.5343 0.5128 0.4349 0.3947 0.3389 0.1209

1978 1.128 1.088 0.9495 0.7247 0.6197 0.2163

1979 0.8605 0.8291 0.7376 0.5598 0.4631 0.158

1980 1.787 1.724 1.583 1.243 1.037 0.353

1981 0.556 0.536 0.4854 0.4094 0.3494 0.1238

1982 0.7089 0.6887 0.619 0.509 0.4401 0.1577
84

1983 1.021 0.9858 0.8637 0.6774 0.5693 0.1996

1984 0.5436 0.5222 0.4432 0.3276 0.2694 0.09201

1985 0.5329 0.511 0.4402 0.3438 0.2849 0.0962

1986 0.923 0.8938 0.8005 0.678 0.5814 0.2001

1987 1.113 1.074 0.9513 0.7165 0.606 0.2135

1988 0.8307 0.8038 0.6746 0.5419 0.509 0.1935

1989 1.382 1.329 1.139 1.017 0.8606 0.3063

1990 0.5509 0.5295 0.4521 0.3388 0.3163 0.1224

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.888 2.774 2.37 1.79 1.464 0.5119

0.0645161290322581 2.595 2.508 2.144 1.581 1.305 0.4404

0.0967741935483871 1.787 1.724 1.583 1.243 1.037 0.353

0.129032258064516 1.766 1.717 1.509 1.098 0.9047 0.3138

0.161290322580645 1.382 1.329 1.139 1.017 0.8606 0.3063

0.193548387096774 1.128 1.088 0.9513 0.7729 0.6652 0.2561

0.225806451612903 1.113 1.074 0.9495 0.7247 0.6197 0.2163

0.258064516129032 1.04 1.001 0.9082 0.7165 0.606 0.2135

0.290322580645161 1.021 0.9858 0.8637 0.678 0.5814 0.2001

0.32258064516129 0.923 0.8938 0.8005 0.6774 0.5693 0.1996

0.354838709677419 0.9171 0.8842 0.7675 0.607 0.5365 0.1948

0.387096774193548 0.8605 0.8291 0.7376 0.5682 0.509 0.1935

0.419354838709677 0.8307 0.8038 0.7123 0.5598 0.475 0.1705

0.451612903225806 0.8286 0.8014 0.6746 0.5486 0.4689 0.1644

0.483870967741936 0.71 0.6887 0.619 0.5419 0.4631 0.1637

0.516129032258065 0.7089 0.6859 0.5944 0.509 0.4401 0.158

0.548387096774194 0.6707 0.6469 0.5602 0.4829 0.4135 0.1577

0.580645161290323 0.6536 0.6282 0.537 0.4094 0.411 0.1448

0.612903225806452 0.5761 0.5549 0.4854 0.4002 0.3494 0.1238

0.645161290322581 0.5664 0.5479 0.4758 0.3947 0.3389 0.1224

0.67741935483871 0.556 0.536 0.4758 0.3683 0.3163 0.1209

0.709677419354839 0.5514 0.5295 0.4639 0.362 0.3059 0.1081

0.741935483870968 0.5509 0.5278 0.4524 0.3581 0.3051 0.1055

0.774193548387097 0.545 0.5242 0.4521 0.3495 0.2952 0.1042

0.806451612903226 0.5442 0.5238 0.4462 0.3438 0.2896 0.09922

0.838709677419355 0.5436 0.5222 0.4452 0.3388 0.2849 0.09897

0.870967741935484 0.5399 0.5199 0.4432 0.3358 0.2783 0.0962

0.903225806451613 0.5343 0.5128 0.4402 0.3276 0.2753 0.09387

0.935483870967742 0.5329 0.511 0.4349 0.3275 0.2694 0.09284

0.967741935483871 0.527 0.506 0.4303 0.3273 0.2687 0.09201

0.1 1.7849 1.7233 1.5756 1.2285 1.02377 0.34908

Average of yearly averages: 0.187213666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile: w93193.dvf

PRZM scenario: CAcotton_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond
85

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CACOTGRD.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:12

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1054 0.1012 0.08607 0.0718 0.0655 0.02393

1962 0.1368 0.1327 0.1171 0.1008 0.0861 0.03001

1963 0.8479 0.815 0.7454 0.6182 0.5251 0.1855

1964 0.126 0.1209 0.1034 0.08048 0.06786 0.02735

1965 2.7 2.592 2.211 1.669 1.364 0.4545

1966 0.1497 0.1449 0.1268 0.09949 0.08396 0.0371

1967 0.6359 0.6124 0.53 0.4132 0.3423 0.1197

1968 0.4076 0.3972 0.3541 0.29 0.2567 0.09259

1969 2.273 2.196 1.877 1.374 1.132 0.3805

1970 1.477 1.417 1.256 0.9118 0.7409 0.2512

1971 0.5204 0.4989 0.4227 0.3094 0.2507 0.101

1972 0.1176 0.1133 0.09689 0.07229 0.05972 0.02249

1973 0.4626 0.4477 0.3989 0.316 0.2596 0.08877

1974 0.3286 0.3167 0.2734 0.2388 0.2003 0.0719

1975 0.1271 0.1228 0.1071 0.09393 0.08094 0.02919

1976 0.1336 0.1282 0.1132 0.08945 0.07504 0.02596

1977 0.2375 0.2282 0.208 0.1551 0.1324 0.04984

1978 0.8018 0.7724 0.6754 0.5125 0.4212 0.1429

1979 0.4451 0.4288 0.3942 0.3048 0.2508 0.08577

1980 1.41 1.381 1.283 1.015 0.8477 0.2884

1981 0.2124 0.2054 0.1785 0.147 0.1292 0.04983

1982 0.437 0.4253 0.3793 0.2809 0.2289 0.0825

1983 0.6704 0.6467 0.5661 0.432 0.3586 0.1241

1984 0.1161 0.1117 0.09529 0.07134 0.05899 0.02176

1985 0.1231 0.1184 0.1016 0.08643 0.07332 0.02529

1986 0.6333 0.6145 0.5594 0.4261 0.3734 0.1302

1987 0.8108 0.7792 0.6963 0.5203 0.4245 0.1456

1988 0.4923 0.478 0.4079 0.3461 0.3345 0.1285

1989 1.126 1.085 0.9277 0.8256 0.6988 0.2412

1990 0.2269 0.2179 0.1849 0.1336 0.1086 0.0518

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.7 2.592 2.211 1.669 1.364 0.4545

0.0645161290322581 2.273 2.196 1.877 1.374 1.132 0.3805

0.0967741935483871 1.477 1.417 1.283 1.015 0.8477 0.2884

0.129032258064516 1.41 1.381 1.256 0.9118 0.7409 0.2512

0.161290322580645 1.126 1.085 0.9277 0.8256 0.6988 0.2412

0.193548387096774 0.8479 0.815 0.7454 0.6182 0.5251 0.1855

0.225806451612903 0.8108 0.7792 0.6963 0.5203 0.4245 0.1456

0.258064516129032 0.8018 0.7724 0.6754 0.5125 0.4212 0.1429

0.290322580645161 0.6704 0.6467 0.5661 0.432 0.3734 0.1302

0.32258064516129 0.6359 0.6145 0.5594 0.4261 0.3586 0.1285

0.354838709677419 0.6333 0.6124 0.53 0.4132 0.3423 0.1241

0.387096774193548 0.5204 0.4989 0.4227 0.3461 0.3345 0.1197

0.419354838709677 0.4923 0.478 0.4079 0.316 0.2596 0.101

0.451612903225806 0.4626 0.4477 0.3989 0.3094 0.2567 0.09259

0.483870967741936 0.4451 0.4288 0.3942 0.3048 0.2508 0.08877

0.516129032258065 0.437 0.4253 0.3793 0.29 0.2507 0.08577
86

0.548387096774194 0.4076 0.3972 0.3541 0.2809 0.2289 0.0825

0.580645161290323 0.3286 0.3167 0.2734 0.2388 0.2003 0.0719

0.612903225806452 0.2375 0.2282 0.208 0.1551 0.1324 0.0518

0.645161290322581 0.2269 0.2179 0.1849 0.147 0.1292 0.04984

0.67741935483871 0.2124 0.2054 0.1785 0.1336 0.1086 0.04983

0.709677419354839 0.1497 0.1449 0.1268 0.1008 0.0861 0.0371

0.741935483870968 0.1368 0.1327 0.1171 0.09949 0.08396 0.03001

0.774193548387097 0.1336 0.1282 0.1132 0.09393 0.08094 0.02919

0.806451612903226 0.1271 0.1228 0.1071 0.08945 0.07504 0.02735

0.838709677419355 0.126 0.1209 0.1034 0.08643 0.07332 0.02596

0.870967741935484 0.1231 0.1184 0.1016 0.08048 0.06786 0.02529

0.903225806451613 0.1176 0.1133 0.09689 0.07229 0.0655 0.02393

0.935483870967742 0.1161 0.1117 0.09529 0.0718 0.05972 0.02249

0.967741935483871 0.1054 0.1012 0.08607 0.07134 0.05899 0.02176

0.1 1.4703 1.4134 1.2803 1.00468 0.83702 0.28468

Average of yearly averages: 0.116979333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTGRD

Metfile: w93193.dvf

PRZM scenario: CAcotton_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Grape

stored as CAGRAPAIR.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5171 0.4966 0.4228 0.3191 0.2657 0.09045

1962 1.361 1.32 1.168 0.8733 0.7171 0.2461

1963 0.7761 0.7483 0.676 0.5199 0.4457 0.1641

1964 0.529 0.5062 0.4257 0.321 0.2671 0.09333
87

1965 0.9447 0.9087 0.779 0.584 0.5202 0.2006

1966 0.5369 0.5166 0.4432 0.3354 0.2784 0.09653

1967 0.527 0.5078 0.4382 0.3538 0.3202 0.1209

1968 0.5319 0.5139 0.4481 0.3468 0.2935 0.102

1969 0.939 0.9083 0.78 0.6087 0.5194 0.1856

1970 0.6396 0.6175 0.5325 0.4526 0.3905 0.1395

1971 0.5285 0.5081 0.4346 0.327 0.273 0.09609

1972 0.5255 0.5052 0.4322 0.3229 0.2668 0.091

1973 0.9266 0.8949 0.7789 0.6029 0.5039 0.1763

1974 0.5318 0.5111 0.4364 0.335 0.2851 0.09971

1975 0.5264 0.5068 0.4359 0.3342 0.282 0.09792

1976 1.318 1.268 1.089 0.7993 0.6576 0.2272

1977 0.5345 0.5133 0.4413 0.3372 0.2808 0.09872

1978 1.195 1.167 1.035 0.8016 0.6729 0.2341

1979 0.5378 0.5184 0.4678 0.3681 0.3111 0.1086

1980 1.122 1.083 0.9424 0.7142 0.6064 0.2162

1981 0.5369 0.5175 0.447 0.356 0.3087 0.1096

1982 0.5274 0.5077 0.4365 0.3619 0.319 0.1153

1983 0.6622 0.6392 0.5555 0.464 0.3976 0.1414

1984 0.5286 0.5129 0.4384 0.3282 0.272 0.09254

1985 0.5308 0.5092 0.4314 0.3253 0.2707 0.09205

1986 1.059 1.02 0.8818 0.6783 0.5665 0.1971

1987 0.5341 0.5139 0.4713 0.3606 0.302 0.1049

1988 0.5217 0.4995 0.4206 0.3255 0.2722 0.09441

1989 0.5264 0.5073 0.4377 0.3474 0.2996 0.1049

1990 0.538 0.5168 0.4405 0.3316 0.2759 0.09468

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.361 1.32 1.168 0.8733 0.7171 0.2461

0.0645161290322581 1.318 1.268 1.089 0.8016 0.6729 0.2341

0.0967741935483871 1.195 1.167 1.035 0.7993 0.6576 0.2272

0.129032258064516 1.122 1.083 0.9424 0.7142 0.6064 0.2162

0.161290322580645 1.059 1.02 0.8818 0.6783 0.5665 0.2006

0.193548387096774 0.9447 0.9087 0.78 0.6087 0.5202 0.1971

0.225806451612903 0.939 0.9083 0.779 0.6029 0.5194 0.1856

0.258064516129032 0.9266 0.8949 0.7789 0.584 0.5039 0.1763

0.290322580645161 0.7761 0.7483 0.676 0.5199 0.4457 0.1641

0.32258064516129 0.6622 0.6392 0.5555 0.464 0.3976 0.1414

0.354838709677419 0.6396 0.6175 0.5325 0.4526 0.3905 0.1395

0.387096774193548 0.538 0.5184 0.4713 0.3681 0.3202 0.1209

0.419354838709677 0.5378 0.5175 0.4678 0.3619 0.319 0.1153

0.451612903225806 0.5369 0.5168 0.4481 0.3606 0.3111 0.1096

0.483870967741936 0.5369 0.5166 0.447 0.356 0.3087 0.1086

0.516129032258065 0.5345 0.5139 0.4432 0.3538 0.302 0.1049

0.548387096774194 0.5341 0.5139 0.4413 0.3474 0.2996 0.1049

0.580645161290323 0.5319 0.5133 0.4405 0.3468 0.2935 0.102

0.612903225806452 0.5318 0.5129 0.4384 0.3372 0.2851 0.09971

0.645161290322581 0.5308 0.5111 0.4382 0.3354 0.282 0.09872

0.67741935483871 0.529 0.5092 0.4377 0.335 0.2808 0.09792

0.709677419354839 0.5286 0.5081 0.4365 0.3342 0.2784 0.09653

0.741935483870968 0.5285 0.5078 0.4364 0.3316 0.2759 0.09609

0.774193548387097 0.5274 0.5077 0.4359 0.3282 0.273 0.09468

0.806451612903226 0.527 0.5073 0.4346 0.327 0.2722 0.09441

0.838709677419355 0.5264 0.5068 0.4322 0.3255 0.272 0.09333

0.870967741935484 0.5264 0.5062 0.4314 0.3253 0.2707 0.09254

0.903225806451613 0.5255 0.5052 0.4257 0.3229 0.2671 0.09205

0.935483870967742 0.5217 0.4995 0.4228 0.321 0.2668 0.091

0.967741935483871 0.5171 0.4966 0.4206 0.3191 0.2657 0.09045

0.1 1.1877 1.1586 1.02574 0.79079 0.65248 0.2261

Average of yearly averages: 0.134394333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPAIR

Metfile: w93193.dvf

PRZM scenario: CAgrapes_WirrigSTD.txt

EXAMS environment file: pond298.exv
88

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CAGRAPGRD.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1034 0.09932 0.08456 0.06478 0.05474 0.01885

1962 0.9943 0.9627 0.8516 0.6331 0.5173 0.174

1963 0.3897 0.376 0.3411 0.2688 0.2347 0.08744

1964 0.1113 0.1067 0.09059 0.07059 0.05928 0.02158

1965 0.7439 0.7144 0.6086 0.4512 0.3683 0.1295

1966 0.1171 0.1129 0.09755 0.07514 0.06285 0.02316

1967 0.1292 0.1251 0.1144 0.106 0.09732 0.04123

1968 0.1084 0.1048 0.09161 0.07522 0.06652 0.02421

1969 0.6358 0.6143 0.5253 0.3853 0.3181 0.1112

1970 0.3651 0.3534 0.3059 0.2226 0.1821 0.06729

1971 0.1092 0.1051 0.09016 0.06832 0.05838 0.02184

1972 0.1054 0.1014 0.08673 0.06504 0.05393 0.01853

1973 0.543 0.5241 0.4553 0.3491 0.289 0.09917

1974 0.1118 0.1076 0.09228 0.07264 0.06491 0.02413

1975 0.1057 0.1018 0.08757 0.0675 0.05707 0.01991

1976 0.9393 0.9037 0.7748 0.5656 0.4627 0.1575

1977 0.116 0.1116 0.1002 0.0815 0.06917 0.02575

1978 0.8144 0.8 0.7097 0.5549 0.4653 0.1588

1979 0.1474 0.1424 0.1239 0.1024 0.08789 0.03217

1980 0.8037 0.775 0.6743 0.5031 0.4135 0.1432

1981 0.125 0.1209 0.1054 0.09219 0.08497 0.0331

1982 0.1476 0.1429 0.1308 0.1023 0.09557 0.0372

1983 0.2541 0.2458 0.2164 0.198 0.1712 0.06133

1984 0.1139 0.1098 0.09503 0.07144 0.05955 0.02072

1985 0.1132 0.1086 0.09202 0.07014 0.05887 0.02018

1986 0.693 0.6671 0.5767 0.4449 0.3681 0.1251

1987 0.1568 0.151 0.1298 0.1022 0.08649 0.03116

1988 0.1095 0.1049 0.08898 0.07897 0.06869 0.02485

1989 0.1059 0.102 0.08809 0.08526 0.07785 0.02919

1990 0.1199 0.1152 0.09826 0.07422 0.06195 0.02158
89

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.9943 0.9627 0.8516 0.6331 0.5173 0.174

0.0645161290322581 0.9393 0.9037 0.7748 0.5656 0.4653 0.1588

0.0967741935483871 0.8144 0.8 0.7097 0.5549 0.4627 0.1575

0.129032258064516 0.8037 0.775 0.6743 0.5031 0.4135 0.1432

0.161290322580645 0.7439 0.7144 0.6086 0.4512 0.3683 0.1295

0.193548387096774 0.693 0.6671 0.5767 0.4449 0.3681 0.1251

0.225806451612903 0.6358 0.6143 0.5253 0.3853 0.3181 0.1112

0.258064516129032 0.543 0.5241 0.4553 0.3491 0.289 0.09917

0.290322580645161 0.3897 0.376 0.3411 0.2688 0.2347 0.08744

0.32258064516129 0.3651 0.3534 0.3059 0.2226 0.1821 0.06729

0.354838709677419 0.2541 0.2458 0.2164 0.198 0.1712 0.06133

0.387096774193548 0.1568 0.151 0.1308 0.106 0.09732 0.04123

0.419354838709677 0.1476 0.1429 0.1298 0.1024 0.09557 0.0372

0.451612903225806 0.1474 0.1424 0.1239 0.1023 0.08789 0.0331

0.483870967741936 0.1292 0.1251 0.1144 0.1022 0.08649 0.03217

0.516129032258065 0.125 0.1209 0.1054 0.09219 0.08497 0.03116

0.548387096774194 0.1199 0.1152 0.1002 0.08526 0.07785 0.02919

0.580645161290323 0.1171 0.1129 0.09826 0.0815 0.06917 0.02575

0.612903225806452 0.116 0.1116 0.09755 0.07897 0.06869 0.02485

0.645161290322581 0.1139 0.1098 0.09503 0.07522 0.06652 0.02421

0.67741935483871 0.1132 0.1086 0.09228 0.07514 0.06491 0.02413

0.709677419354839 0.1118 0.1076 0.09202 0.07422 0.06285 0.02316

0.741935483870968 0.1113 0.1067 0.09161 0.07264 0.06195 0.02184

0.774193548387097 0.1095 0.1051 0.09059 0.07144 0.05955 0.02158

0.806451612903226 0.1092 0.1049 0.09016 0.07059 0.05928 0.02158

0.838709677419355 0.1084 0.1048 0.08898 0.07014 0.05887 0.02072

0.870967741935484 0.1059 0.102 0.08809 0.06832 0.05838 0.02018

0.903225806451613 0.1057 0.1018 0.08757 0.0675 0.05707 0.01991

0.935483870967742 0.1054 0.1014 0.08673 0.06504 0.05474 0.01885

0.967741935483871 0.1034 0.09932 0.08456 0.06478 0.05393 0.01853

0.1 0.81333 0.7975 0.70616 0.54972 0.45778 0.15607

Average of yearly averages: 0.060129

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPGRD

Metfile: w93193.dvf

PRZM scenario: CAgrapes_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5
90

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Lettuce

stored as CALETAIR.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt modified Tueday, 21 February 2006 at 14:38:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23273.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.977 1.918 1.641 1.011 0.6815 0.2533

1962 1.971 1.909 1.722 1.352 1.207 0.5421

1963 2.49 2.393 2.191 1.805 1.535 0.6179

1964 0.8977 0.864 0.7851 0.6179 0.557 0.2997

1965 0.8491 0.8213 0.7284 0.57 0.5516 0.264

1966 1.336 1.283 1.114 0.8178 0.555 0.2434

1967 0.9966 0.9629 0.8842 0.8193 0.763 0.3745

1968 1.086 1.044 0.9011 0.6981 0.614 0.2889

1969 3.597 3.464 3.012 2.203 1.821 0.6793

1970 4.304 4.123 3.68 2.663 2.162 0.8057

1971 0.7059 0.682 0.5902 0.4532 0.4033 0.268

1972 1.527 1.469 1.275 0.9252 0.6943 0.2896

1973 1.287 1.244 1.151 1.013 0.8807 0.408

1974 3.971 3.84 3.423 2.621 2.162 0.7964

1975 1.64 1.579 1.362 1.02 0.8678 0.3528

1976 0.855 0.8208 0.6979 0.5678 0.502 0.3292

1977 1.509 1.446 1.223 0.9779 0.9656 0.4509

1978 3.038 2.926 2.565 1.94 1.618 0.6222

1979 1.474 1.417 1.231 1.016 0.86 0.3235

1980 1.828 1.759 1.613 1.279 1.067 0.398

1981 3.37 3.267 2.861 2.203 1.829 0.6772

1982 0.8822 0.8507 0.7991 0.659 0.5925 0.2482

1983 2.214 2.139 1.891 1.457 1.212 0.4408

1984 0.5706 0.55 0.486 0.3694 0.3024 0.1725

1985 0.715 0.6882 0.6244 0.5076 0.4318 0.2534

1986 2.047 1.974 1.754 1.399 1.167 0.4756

1987 3.416 3.294 2.813 2.058 1.692 0.6385

1988 2.088 1.997 1.668 1.248 1.098 0.437

1989 0.5816 0.5607 0.486 0.3728 0.3122 0.1368

1990 0.7601 0.7309 0.6365 0.4911 0.4105 0.1818

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.304 4.123 3.68 2.663 2.162 0.8057

0.0645161290322581 3.971 3.84 3.423 2.621 2.162 0.7964

0.0967741935483871 3.597 3.464 3.012 2.203 1.829 0.6793

0.129032258064516 3.416 3.294 2.861 2.203 1.821 0.6772

0.161290322580645 3.37 3.267 2.813 2.058 1.692 0.6385

0.193548387096774 3.038 2.926 2.565 1.94 1.618 0.6222

0.225806451612903 2.49 2.393 2.191 1.805 1.535 0.6179

0.258064516129032 2.214 2.139 1.891 1.457 1.212 0.5421

0.290322580645161 2.088 1.997 1.754 1.399 1.207 0.4756

0.32258064516129 2.047 1.974 1.722 1.352 1.167 0.4509

0.354838709677419 1.977 1.918 1.668 1.279 1.098 0.4408

0.387096774193548 1.971 1.909 1.641 1.248 1.067 0.437

0.419354838709677 1.828 1.759 1.613 1.02 0.9656 0.408

0.451612903225806 1.64 1.579 1.362 1.016 0.8807 0.398

0.483870967741936 1.527 1.469 1.275 1.013 0.8678 0.3745

0.516129032258065 1.509 1.446 1.231 1.011 0.86 0.3528

0.548387096774194 1.474 1.417 1.223 0.9779 0.763 0.3292

0.580645161290323 1.336 1.283 1.151 0.9252 0.6943 0.3235

0.612903225806452 1.287 1.244 1.114 0.8193 0.6815 0.2997

0.645161290322581 1.086 1.044 0.9011 0.8178 0.614 0.2896

0.67741935483871 0.9966 0.9629 0.8842 0.6981 0.5925 0.2889
91

0.709677419354839 0.8977 0.864 0.7991 0.659 0.557 0.268

0.741935483870968 0.8822 0.8507 0.7851 0.6179 0.555 0.264

0.774193548387097 0.855 0.8213 0.7284 0.57 0.5516 0.2534

0.806451612903226 0.8491 0.8208 0.6979 0.5678 0.502 0.2533

0.838709677419355 0.7601 0.7309 0.6365 0.5076 0.4318 0.2482

0.870967741935484 0.715 0.6882 0.6244 0.4911 0.4105 0.2434

0.903225806451613 0.7059 0.682 0.5902 0.4532 0.4033 0.1818

0.935483870967742 0.5816 0.5607 0.486 0.3728 0.3122 0.1725

0.967741935483871 0.5706 0.55 0.486 0.3694 0.3024 0.1368

0.1 3.5789 3.447 2.9969 2.203 1.8282 0.67909

Average of yearly averages: 0.408973333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETAIR

Metfile: w23273.dvf

PRZM scenario: CAlettuceSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CALETGRD.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt modified Tueday, 21 February 2006 at 14:38:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23273.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 2.049 1.987 1.699 1.041 0.6957 0.1896

1962 1.627 1.595 1.43 1.159 1.1 0.4827

1963 2.365 2.272 2.046 1.701 1.446 0.5613

1964 0.7311 0.7028 0.6176 0.4908 0.4108 0.2346

1965 0.6878 0.6645 0.5862 0.4449 0.3777 0.1906

1966 1.378 1.323 1.147 0.8372 0.5611 0.1717

1967 0.8345 0.8063 0.7031 0.6576 0.6375 0.3064

1968 0.8235 0.7915 0.682 0.5217 0.4323 0.2187
92

1969 3.323 3.201 2.792 2.042 1.685 0.6278

1970 4.128 3.954 3.519 2.547 2.067 0.7627

1971 0.6414 0.6187 0.5318 0.3943 0.3257 0.2001

1972 1.575 1.515 1.313 0.95 0.7072 0.2232

1973 1.036 1.007 0.9023 0.797 0.6897 0.3428

1974 3.762 3.638 3.251 2.493 2.057 0.7475

1975 1.367 1.315 1.135 0.8495 0.7046 0.2846

1976 0.83 0.8048 0.693 0.5594 0.4961 0.2639

1977 1.302 1.26 1.089 0.8519 0.8669 0.3937

1978 2.801 2.698 2.368 1.79 1.482 0.5654

1979 1.096 1.054 0.9213 0.7858 0.6723 0.2558

1980 1.464 1.434 1.321 1.064 0.8889 0.3346

1981 3.158 3.057 2.678 2.059 1.702 0.6245

1982 0.6891 0.666 0.5989 0.5069 0.4308 0.1771

1983 1.925 1.855 1.639 1.255 1.045 0.3737

1984 0.5841 0.5628 0.4961 0.3729 0.2601 0.104

1985 0.5222 0.5022 0.4547 0.3469 0.3006 0.1837

1986 1.839 1.773 1.566 1.244 1.039 0.4129

1987 3.207 3.094 2.64 1.929 1.584 0.5842

1988 1.801 1.723 1.438 1.084 0.9592 0.3801

1989 0.1661 0.1609 0.1456 0.1169 0.1079 0.06223

1990 0.3537 0.3408 0.3118 0.2604 0.239 0.109

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.128 3.954 3.519 2.547 2.067 0.7627

0.0645161290322581 3.762 3.638 3.251 2.493 2.057 0.7475

0.0967741935483871 3.323 3.201 2.792 2.059 1.702 0.6278

0.129032258064516 3.207 3.094 2.678 2.042 1.685 0.6245

0.161290322580645 3.158 3.057 2.64 1.929 1.584 0.5842

0.193548387096774 2.801 2.698 2.368 1.79 1.482 0.5654

0.225806451612903 2.365 2.272 2.046 1.701 1.446 0.5613

0.258064516129032 2.049 1.987 1.699 1.255 1.1 0.4827

0.290322580645161 1.925 1.855 1.639 1.244 1.045 0.4129

0.32258064516129 1.839 1.773 1.566 1.159 1.039 0.3937

0.354838709677419 1.801 1.723 1.438 1.084 0.9592 0.3801

0.387096774193548 1.627 1.595 1.43 1.064 0.8889 0.3737

0.419354838709677 1.575 1.515 1.321 1.041 0.8669 0.3428

0.451612903225806 1.464 1.434 1.313 0.95 0.7072 0.3346

0.483870967741936 1.378 1.323 1.147 0.8519 0.7046 0.3064

0.516129032258065 1.367 1.315 1.135 0.8495 0.6957 0.2846

0.548387096774194 1.302 1.26 1.089 0.8372 0.6897 0.2639

0.580645161290323 1.096 1.054 0.9213 0.797 0.6723 0.2558

0.612903225806452 1.036 1.007 0.9023 0.7858 0.6375 0.2346

0.645161290322581 0.8345 0.8063 0.7031 0.6576 0.5611 0.2232

0.67741935483871 0.83 0.8048 0.693 0.5594 0.4961 0.2187

0.709677419354839 0.8235 0.7915 0.682 0.5217 0.4323 0.2001

0.741935483870968 0.7311 0.7028 0.6176 0.5069 0.4308 0.1906

0.774193548387097 0.6891 0.666 0.5989 0.4908 0.4108 0.1896

0.806451612903226 0.6878 0.6645 0.5862 0.4449 0.3777 0.1837

0.838709677419355 0.6414 0.6187 0.5318 0.3943 0.3257 0.1771

0.870967741935484 0.5841 0.5628 0.4961 0.3729 0.3006 0.1717

0.903225806451613 0.5222 0.5022 0.4547 0.3469 0.2601 0.109

0.935483870967742 0.3537 0.3408 0.3118 0.2604 0.239 0.104

0.967741935483871 0.1661 0.1609 0.1456 0.1169 0.1079 0.06223

0.1 3.3114 3.1903 2.7806 2.0573 1.7003 0.62747

Average of yearly averages: 0.345637666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETGRD

Metfile: w23273.dvf

PRZM scenario: CAlettuceSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol
93

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Tomato

stored as CATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:43:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5216 0.5007 0.4283 0.3209 0.2639 0.08737

1962 0.5291 0.5082 0.4439 0.3419 0.2825 0.09535

1963 0.7165 0.6896 0.6333 0.5658 0.4951 0.179

1964 0.5382 0.5168 0.4407 0.3285 0.2707 0.09458

1965 2.011 1.931 1.648 1.237 1.014 0.3468

1966 0.5505 0.5285 0.4499 0.3341 0.274 0.09759

1967 0.8163 0.7864 0.6849 0.5703 0.484 0.1691

1968 0.7195 0.6943 0.6039 0.4846 0.4053 0.1397

1969 0.6117 0.5872 0.5136 0.447 0.3822 0.1344

1970 1.133 1.086 0.938 0.7028 0.5725 0.1898

1971 0.5343 0.5124 0.4598 0.3493 0.2943 0.1032

1972 0.5273 0.5042 0.423 0.3107 0.2541 0.08587

1973 0.6907 0.6673 0.5775 0.4681 0.3935 0.135

1974 0.5813 0.56 0.483 0.3975 0.3328 0.1136

1975 0.5326 0.5131 0.4645 0.3548 0.2944 0.09991

1976 0.5303 0.5084 0.4299 0.3189 0.262 0.0888

1977 0.5279 0.5063 0.4714 0.3638 0.3021 0.1035

1978 0.8467 0.8185 0.7138 0.6387 0.5434 0.1869

1979 0.5623 0.5414 0.4854 0.3781 0.3129 0.107

1980 1.079 1.036 0.8806 0.6416 0.528 0.1781

1981 0.6689 0.6451 0.5563 0.4561 0.3845 0.1321

1982 0.8655 0.8461 0.7656 0.6014 0.5022 0.1747

1983 0.9613 0.929 0.8814 0.7307 0.6131 0.2104

1984 0.5366 0.514 0.4344 0.3216 0.2635 0.09011

1985 0.5283 0.5074 0.4409 0.3271 0.2676 0.08931

1986 1.08 1.039 0.9267 0.7012 0.5778 0.1948

1987 0.7124 0.6848 0.6154 0.4735 0.3926 0.1344

1988 0.5282 0.5047 0.4212 0.3171 0.2667 0.0918

1989 0.7747 0.7465 0.6379 0.5678 0.4791 0.1629

1990 0.533 0.5116 0.4346 0.3238 0.2677 0.09148
94

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.011 1.931 1.648 1.237 1.014 0.3468

0.0645161290322581 1.133 1.086 0.938 0.7307 0.6131 0.2104

0.0967741935483871 1.08 1.039 0.9267 0.7028 0.5778 0.1948

0.129032258064516 1.079 1.036 0.8814 0.7012 0.5725 0.1898

0.161290322580645 0.9613 0.929 0.8806 0.6416 0.5434 0.1869

0.193548387096774 0.8655 0.8461 0.7656 0.6387 0.528 0.179

0.225806451612903 0.8467 0.8185 0.7138 0.6014 0.5022 0.1781

0.258064516129032 0.8163 0.7864 0.6849 0.5703 0.4951 0.1747

0.290322580645161 0.7747 0.7465 0.6379 0.5678 0.484 0.1691

0.32258064516129 0.7195 0.6943 0.6333 0.5658 0.4791 0.1629

0.354838709677419 0.7165 0.6896 0.6154 0.4846 0.4053 0.1397

0.387096774193548 0.7124 0.6848 0.6039 0.4735 0.3935 0.135

0.419354838709677 0.6907 0.6673 0.5775 0.4681 0.3926 0.1344

0.451612903225806 0.6689 0.6451 0.5563 0.4561 0.3845 0.1344

0.483870967741936 0.6117 0.5872 0.5136 0.447 0.3822 0.1321

0.516129032258065 0.5813 0.56 0.4854 0.3975 0.3328 0.1136

0.548387096774194 0.5623 0.5414 0.483 0.3781 0.3129 0.107

0.580645161290323 0.5505 0.5285 0.4714 0.3638 0.3021 0.1035

0.612903225806452 0.5382 0.5168 0.4645 0.3548 0.2944 0.1032

0.645161290322581 0.5366 0.514 0.4598 0.3493 0.2943 0.09991

0.67741935483871 0.5343 0.5131 0.4499 0.3419 0.2825 0.09759

0.709677419354839 0.533 0.5124 0.4439 0.3341 0.274 0.09535

0.741935483870968 0.5326 0.5116 0.4409 0.3285 0.2707 0.09458

0.774193548387097 0.5303 0.5084 0.4407 0.3271 0.2677 0.0918

0.806451612903226 0.5291 0.5082 0.4346 0.3238 0.2676 0.09148

0.838709677419355 0.5283 0.5074 0.4344 0.3216 0.2667 0.09011

0.870967741935484 0.5282 0.5063 0.4299 0.3209 0.2639 0.08931

0.903225806451613 0.5279 0.5047 0.4283 0.3189 0.2635 0.0888

0.935483870967742 0.5273 0.5042 0.423 0.3171 0.262 0.08737

0.967741935483871 0.5216 0.5007 0.4212 0.3107 0.2541 0.08587

0.1 1.0799 1.0387 0.92217 0.70264 0.57727 0.1943

Average of yearly averages: 0.136919

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMAIR

Metfile: w93193.dvf

PRZM scenario: CAtomato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-3 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5
95

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CATOMGRD.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:43:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1043 0.1001 0.08797 0.06987 0.05825 0.01951

1962 0.1285 0.1236 0.1052 0.08715 0.0736 0.02528

1963 0.4573 0.4395 0.4167 0.352 0.3027 0.1079

1964 0.1151 0.1107 0.09566 0.07252 0.06018 0.02302

1965 1.701 1.633 1.392 1.046 0.8545 0.2838

1966 0.1289 0.1241 0.1074 0.08226 0.06831 0.02879

1967 0.4518 0.435 0.381 0.3263 0.2748 0.09517

1968 0.3624 0.3509 0.3103 0.2464 0.2032 0.07117

1969 0.3248 0.3115 0.2641 0.2068 0.181 0.06597

1970 0.7371 0.7094 0.6368 0.4669 0.3792 0.125

1971 0.1447 0.1389 0.1198 0.0998 0.08748 0.03309

1972 0.1066 0.102 0.0863 0.06391 0.05238 0.01808

1973 0.3691 0.3562 0.3067 0.2204 0.1804 0.06249

1974 0.185 0.1811 0.1593 0.1361 0.1167 0.04125

1975 0.1342 0.1294 0.113 0.0892 0.07471 0.02582

1976 0.1087 0.1042 0.08815 0.06551 0.05385 0.01838

1977 0.1752 0.1681 0.1511 0.115 0.09637 0.03352

1978 0.4866 0.4697 0.4387 0.3855 0.3355 0.1158

1979 0.1578 0.1522 0.1393 0.1177 0.09928 0.03562

1980 0.6797 0.6524 0.5541 0.4031 0.3291 0.1097

1981 0.3459 0.3333 0.2863 0.2093 0.1739 0.06147

1982 0.5298 0.5188 0.4703 0.3637 0.2969 0.1026

1983 0.6055 0.5855 0.5683 0.4755 0.4017 0.1384

1984 0.1152 0.1105 0.09504 0.07174 0.0592 0.02223

1985 0.11 0.1057 0.09604 0.07189 0.05903 0.0198

1986 0.7505 0.7219 0.6249 0.4737 0.3862 0.1274

1987 0.317 0.3053 0.2761 0.2274 0.1881 0.06547

1988 0.1087 0.1039 0.08693 0.07114 0.06358 0.02354

1989 0.4968 0.4783 0.4073 0.3199 0.276 0.09481

1990 0.1114 0.1071 0.09147 0.06944 0.05873 0.02164

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.701 1.633 1.392 1.046 0.8545 0.2838

0.0645161290322581 0.7505 0.7219 0.6368 0.4755 0.4017 0.1384

0.0967741935483871 0.7371 0.7094 0.6249 0.4737 0.3862 0.1274

0.129032258064516 0.6797 0.6524 0.5683 0.4669 0.3792 0.125

0.161290322580645 0.6055 0.5855 0.5541 0.4031 0.3355 0.1158

0.193548387096774 0.5298 0.5188 0.4703 0.3855 0.3291 0.1097

0.225806451612903 0.4968 0.4783 0.4387 0.3637 0.3027 0.1079

0.258064516129032 0.4866 0.4697 0.4167 0.352 0.2969 0.1026

0.290322580645161 0.4573 0.4395 0.4073 0.3263 0.276 0.09517

0.32258064516129 0.4518 0.435 0.381 0.3199 0.2748 0.09481

0.354838709677419 0.3691 0.3562 0.3103 0.2464 0.2032 0.07117

0.387096774193548 0.3624 0.3509 0.3067 0.2274 0.1881 0.06597

0.419354838709677 0.3459 0.3333 0.2863 0.2204 0.181 0.06547

0.451612903225806 0.3248 0.3115 0.2761 0.2093 0.1804 0.06249

0.483870967741936 0.317 0.3053 0.2641 0.2068 0.1739 0.06147

0.516129032258065 0.185 0.1811 0.1593 0.1361 0.1167 0.04125

0.548387096774194 0.1752 0.1681 0.1511 0.1177 0.09928 0.03562

0.580645161290323 0.1578 0.1522 0.1393 0.115 0.09637 0.03352

0.612903225806452 0.1447 0.1389 0.1198 0.0998 0.08748 0.03309

0.645161290322581 0.1342 0.1294 0.113 0.0892 0.07471 0.02879

0.67741935483871 0.1289 0.1241 0.1074 0.08715 0.0736 0.02582

0.709677419354839 0.1285 0.1236 0.1052 0.08226 0.06831 0.02528

0.741935483870968 0.1152 0.1107 0.09604 0.07252 0.06358 0.02354

0.774193548387097 0.1151 0.1105 0.09566 0.07189 0.06018 0.02302

0.806451612903226 0.1114 0.1071 0.09504 0.07174 0.0592 0.02223

0.838709677419355 0.11 0.1057 0.09147 0.07114 0.05903 0.02164
96

0.870967741935484 0.1087 0.1042 0.08815 0.06987 0.05873 0.0198

0.903225806451613 0.1087 0.1039 0.08797 0.06944 0.05825 0.01951

0.935483870967742 0.1066 0.102 0.08693 0.06551 0.05385 0.01838

0.967741935483871 0.1043 0.1001 0.0863 0.06391 0.05238 0.01808

0.1 0.73136 0.7037 0.61924 0.47302 0.3855 0.12716

Average of yearly averages: 0.067224

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMGRD

Metfile: w93193.dvf

PRZM scenario: CAtomato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-3 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Turf

stored as CATURFGRD.out

Chemical: DPXE2Y45

PRZM environment: CATurfRLF.txt modified Tueday, 20 February 2007 at 12:03:48

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23234.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.2703 0.2588 0.2394 0.193 0.1656 0.06767

1962 0.6401 0.6158 0.5279 0.3945 0.3238 0.1582

1963 0.4295 0.416 0.3885 0.3141 0.2704 0.1458

1964 0.3227 0.3102 0.2655 0.2072 0.1782 0.09411

1965 0.5031 0.4856 0.4219 0.3171 0.2665 0.1155

1966 0.3178 0.3057 0.262 0.2029 0.1706 0.09447

1967 0.7069 0.6908 0.6217 0.4831 0.4179 0.2076

1968 0.3342 0.3209 0.2736 0.2142 0.184 0.0964

1969 0.354 0.3408 0.2942 0.2297 0.1967 0.1057

1970 0.3121 0.3005 0.2587 0.2046 0.1771 0.09475

1971 0.3008 0.2924 0.2536 0.1974 0.1713 0.08037

1972 0.2814 0.2713 0.2338 0.1876 0.1622 0.09582

1973 0.3263 0.3134 0.2696 0.2101 0.1789 0.1039
97

1974 0.4784 0.4602 0.3984 0.3132 0.261 0.1166

1975 0.3493 0.3369 0.2921 0.2322 0.2012 0.09315

1976 0.2995 0.288 0.2467 0.19 0.1602 0.06683

1977 0.3426 0.3297 0.2851 0.2241 0.1907 0.1155

1978 0.5854 0.5661 0.4963 0.4156 0.3568 0.1652

1979 0.3394 0.3292 0.2893 0.2281 0.1951 0.1045

1980 0.3352 0.3234 0.2812 0.222 0.1892 0.09895

1981 0.3244 0.3116 0.266 0.2096 0.1801 0.1039

1982 1.077 1.036 0.8919 0.6637 0.5546 0.2677

1983 0.3661 0.3539 0.3119 0.2703 0.2343 0.1284

1984 0.2991 0.288 0.246 0.1933 0.1673 0.08856

1985 0.3015 0.2896 0.249 0.1941 0.1653 0.078

1986 0.3255 0.313 0.2696 0.2089 0.1763 0.0802

1987 0.3152 0.3031 0.2647 0.2087 0.1784 0.08277

1988 0.6554 0.6359 0.5571 0.4155 0.3562 0.1418

1989 0.301 0.291 0.2513 0.1949 0.1658 0.08203

1990 0.3001 0.2889 0.2489 0.2095 0.1962 0.0882

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.077 1.036 0.8919 0.6637 0.5546 0.2677

0.0645161290322581 0.7069 0.6908 0.6217 0.4831 0.4179 0.2076

0.0967741935483871 0.6554 0.6359 0.5571 0.4156 0.3568 0.1652

0.129032258064516 0.6401 0.6158 0.5279 0.4155 0.3562 0.1582

0.161290322580645 0.5854 0.5661 0.4963 0.3945 0.3238 0.1458

0.193548387096774 0.5031 0.4856 0.4219 0.3171 0.2704 0.1418

0.225806451612903 0.4784 0.4602 0.3984 0.3141 0.2665 0.1284

0.258064516129032 0.4295 0.416 0.3885 0.3132 0.261 0.1166

0.290322580645161 0.3661 0.3539 0.3119 0.2703 0.2343 0.1155

0.32258064516129 0.354 0.3408 0.2942 0.2322 0.2012 0.1155

0.354838709677419 0.3493 0.3369 0.2921 0.2297 0.1967 0.1057

0.387096774193548 0.3426 0.3297 0.2893 0.2281 0.1962 0.1045

0.419354838709677 0.3394 0.3292 0.2851 0.2241 0.1951 0.1039

0.451612903225806 0.3352 0.3234 0.2812 0.222 0.1907 0.1039

0.483870967741936 0.3342 0.3209 0.2736 0.2142 0.1892 0.09895

0.516129032258065 0.3263 0.3134 0.2696 0.2101 0.184 0.0964

0.548387096774194 0.3255 0.313 0.2696 0.2096 0.1801 0.09582

0.580645161290323 0.3244 0.3116 0.266 0.2095 0.1789 0.09475

0.612903225806452 0.3227 0.3102 0.2655 0.2089 0.1784 0.09447

0.645161290322581 0.3178 0.3057 0.2647 0.2087 0.1782 0.09411

0.67741935483871 0.3152 0.3031 0.262 0.2072 0.1771 0.09315

0.709677419354839 0.3121 0.3005 0.2587 0.2046 0.1763 0.08856

0.741935483870968 0.3015 0.2924 0.2536 0.2029 0.1713 0.0882

0.774193548387097 0.301 0.291 0.2513 0.1974 0.1706 0.08277

0.806451612903226 0.3008 0.2896 0.249 0.1949 0.1673 0.08203

0.838709677419355 0.3001 0.2889 0.2489 0.1941 0.1658 0.08037

0.870967741935484 0.2995 0.288 0.2467 0.1933 0.1656 0.0802

0.903225806451613 0.2991 0.288 0.246 0.193 0.1653 0.078

0.935483870967742 0.2814 0.2713 0.2394 0.19 0.1622 0.06767

0.967741935483871 0.2703 0.2588 0.2338 0.1876 0.1602 0.06683

0.1 0.65387 0.63389 0.55418 0.41559 0.35674 0.1645

Average of yearly averages: 0.112086

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATURFGRD

Metfile: w23234.dvf

PRZM scenario: CATurfRLF.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life
98

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.2912 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.2912 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CATF19GRD.out

Chemical: DPXE2Y45

PRZM environment: CATurfRLF.txt modified Tueday, 20 February 2007 at 11:03:48

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 15:33:30

Metfile: w23234.dvf modified Wedday, 3 July 2002 at 08:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.2136 0.2083 0.1838 0.1115 0.1003 0.06133

1962 1.326 1.276 1.093 0.8147 0.6703 0.2772

1963 0.5564 0.5408 0.4948 0.4247 0.3982 0.2315

1964 0.3724 0.3643 0.3172 0.2316 0.1964 0.1316

1965 0.3174 0.3102 0.1608 0.1326 0.1288 0.1038

1966 0.3015 0.2934 0.26 0.2231 0.1938 0.1403

1967 0.7896 0.765 0.7218 0.5572 0.4875 0.2536

1968 0.2864 0.2774 0.2487 0.2075 0.1891 0.1355

1969 0.2854 0.2792 0.2688 0.2442 0.2151 0.1537

1970 0.2739 0.2662 0.2475 0.1993 0.1735 0.1376

1971 0.1915 0.1856 0.1643 0.1445 0.1393 0.1019

1972 0.4698 0.4541 0.4064 0.3704 0.3154 0.1307

1973 0.4113 0.3983 0.3508 0.2644 0.2343 0.1785

1974 0.3579 0.3472 0.3128 0.2477 0.2171 0.1393

1975 0.1793 0.1735 0.1608 0.1543 0.153 0.1153

1976 0.364 0.1976 0.121 0.1184 0.1148 0.0765

1977 0.5114 0.4923 0.4232 0.3189 0.2731 0.1729

1978 0.3741 0.3648 0.3323 0.3012 0.2805 0.1719

1979 0.3512 0.3389 0.2943 0.2722 0.2493 0.1669

1980 0.371 0.3596 0.3216 0.2847 0.2606 0.1547

1981 0.4383 0.4232 0.3683 0.2899 0.2179 0.1555

1982 0.9669 0.9316 0.8036 0.6201 0.5336 0.3125

1983 0.4098 0.3978 0.3693 0.3394 0.3085 0.1943

1984 0.3107 0.3005 0.2722 0.2156 0.177 0.1336

1985 0.179 0.1729 0.1547 0.1333 0.1305 0.1097

1986 0.2724 0.2634 0.233 0.2049 0.1904 0.1218

1987 0.2068 0.1995 0.1743 0.139 0.1323 0.1053

1988 0.1591 0.1538 0.1479 0.1433 0.1433 0.09436

1989 0.1689 0.1629 0.1409 0.1221 0.117 0.09671

1990 0.1821 0.176 0.1652 0.157 0.1496 0.09281

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.326 1.276 1.093 0.8147 0.6703 0.3125

0.0645161290322581 0.9669 0.9316 0.8036 0.6201 0.5336 0.2772

0.0967741935483871 0.7896 0.765 0.7218 0.5572 0.4875 0.2536

0.129032258064516 0.5564 0.5408 0.4948 0.4247 0.3982 0.2315

0.161290322580645 0.5114 0.4923 0.4232 0.3704 0.3154 0.1943

0.193548387096774 0.4698 0.4541 0.4064 0.3394 0.3085 0.1785

0.225806451612903 0.4383 0.4232 0.3693 0.3189 0.2805 0.1729
99

0.258064516129032 0.4113 0.3983 0.3683 0.3012 0.2731 0.1719

0.290322580645161 0.4098 0.3978 0.3508 0.2899 0.2606 0.1669

0.32258064516129 0.3741 0.3648 0.3323 0.2847 0.2493 0.1555

0.354838709677419 0.3724 0.3643 0.3216 0.2722 0.2343 0.1547

0.387096774193548 0.371 0.3596 0.3172 0.2644 0.2179 0.1537

0.419354838709677 0.364 0.3472 0.3128 0.2477 0.2171 0.1403

0.451612903225806 0.3579 0.3389 0.2943 0.2442 0.2151 0.1393

0.483870967741936 0.3512 0.3102 0.2722 0.2316 0.1964 0.1376

0.516129032258065 0.3174 0.3005 0.2688 0.2231 0.1938 0.1355

0.548387096774194 0.3107 0.2934 0.26 0.2156 0.1904 0.1336

0.580645161290323 0.3015 0.2792 0.2487 0.2075 0.1891 0.1316

0.612903225806452 0.2864 0.2774 0.2475 0.2049 0.177 0.1307

0.645161290322581 0.2854 0.2662 0.233 0.1993 0.1735 0.1218

0.67741935483871 0.2739 0.2634 0.1838 0.157 0.153 0.1153

0.709677419354839 0.2724 0.2083 0.1743 0.1543 0.1496 0.1097

0.741935483870968 0.2136 0.1995 0.1652 0.1445 0.1433 0.1053

0.774193548387097 0.2068 0.1976 0.1643 0.1433 0.1393 0.1038

0.806451612903226 0.1915 0.1856 0.1608 0.139 0.1323 0.1019

0.838709677419355 0.1821 0.176 0.1608 0.1333 0.1305 0.09671

0.870967741935484 0.1793 0.1735 0.1547 0.1326 0.1288 0.09436

0.903225806451613 0.179 0.1729 0.1479 0.1221 0.117 0.09281

0.935483870967742 0.1689 0.1629 0.1409 0.1184 0.1148 0.0765

0.967741935483871 0.1591 0.1538 0.121 0.1115 0.1003 0.06133

0.1 0.76628 0.74258 0.6991 0.54395 0.47857 0.25139

Average of yearly averages: 0.148377

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATF19GRD

Metfile: w23234.dvf

PRZM scenario: CATurfRLF.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.029 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.029 kg/ha

Interval 2 interval 7 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.029 kg/ha

Interval 3 interval 7 days Set to 0 or delete line for single app.

app. rate 3 apprate 0.029 kg/ha

Interval 4 interval 7 days Set to 0 or delete line for single app.

app. rate 4 apprate 0.029 kg/ha

Interval 5 interval 7 days Set to 0 or delete line for single app.

app. rate 5 apprate 0.029 kg/ha

Interval 6 interval 7 days Set to 0 or delete line for single app.

app. rate 6 apprate 0.029 kg/ha

Interval 7 interval 7 days Set to 0 or delete line for single app.

app. rate 7 apprate 0.029 kg/ha

Interval 8 interval 7 days Set to 0 or delete line for single app.

app. rate 8 apprate 0.029 kg/ha

Interval 9 interval 7 days Set to 0 or delete line for single app.
100

app. rate 9 apprate 0.029 kg/ha

Interval 10 interval 7 days Set to 0 or delete line for single app.

app. rate 10 apprate 0.029 kg/ha

Interval 11 interval 7 days Set to 0 or delete line for single app.

app. rate 11 apprate 0.029 kg/ha

Interval 12 interval 7 days Set to 0 or delete line for single app.

app. rate 12 apprate 0.029 kg/ha

Interval 13 interval 7 days Set to 0 or delete line for single app.

app. rate 13 apprate 0.029 kg/ha

Interval 14 interval 7 days Set to 0 or delete line for single app.

app. rate 14 apprate 0.029 kg/ha

Interval 15 interval 7 days Set to 0 or delete line for single app.

app. rate 15 apprate 0.029 kg/ha

Interval 16 interval 7 days Set to 0 or delete line for single app.

app. rate 16 apprate 0.029 kg/ha

Interval 17 interval 7 days Set to 0 or delete line for single app.

app. rate 17 apprate 0.029 kg/ha

Interval 18 interval 7 days Set to 0 or delete line for single app.

app. rate 18 apprate 0.029 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Nursey

stored as FLnursey.out

Chemical: DPXE2Y45

PRZM environment: FLnurserySTD.txt modified Wedday, 24 January 2007 at 09:18:06

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12839.dvf modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 2.519 2.429 2.224 1.837 1.532 0.6908

1962 1.426 1.38 1.258 0.9451 0.7806 0.4549

1963 2.805 2.69 2.281 1.823 1.522 0.8256

1964 1.755 1.686 1.458 1.264 1.113 0.4965

1965 3.097 2.964 2.489 2.01 1.739 0.7263

1966 11.38 10.91 9.375 7.136 5.955 2.191

1967 2.415 2.328 2.044 1.523 1.314 0.7161

1968 2.888 2.808 2.616 2.088 1.743 0.7756

1969 3.539 3.391 2.866 2.235 2.081 0.9048

1970 3.17 3.073 2.668 2.022 1.67 0.8217

1971 2.775 2.666 2.393 2.103 1.842 0.702

1972 1.583 1.518 1.294 1.129 1.045 0.5567

1973 1.096 1.053 0.9011 0.7454 0.6782 0.3778

1974 2.675 2.599 2.257 1.754 1.731 0.8377

1975 0.7701 0.7393 0.6349 0.5708 0.5098 0.254

1976 2.605 2.496 2.099 1.743 1.737 0.8241

1977 9.968 9.565 8.27 6.273 5.151 2.031

1978 2.487 2.394 2.182 1.838 1.63 0.69

1979 26.6 25.43 21.55 15.56 12.58 4.136

1980 8.136 7.866 6.933 5.458 5.12 2.045

1981 5.438 5.211 4.389 3.147 2.679 1.071

1982 5.104 4.993 4.32 3.167 2.58 1.008

1983 6.137 5.897 5.139 4.349 3.672 1.336

1984 7.769 7.42 6.19 5.568 4.844 1.774

1985 1.177 1.129 0.9598 0.8162 0.7716 0.3966

1986 4.494 4.309 3.763 3.047 2.592 0.973

1987 2.691 2.584 2.196 1.969 1.691 0.6992

1988 2.201 2.12 1.927 1.58 1.329 0.5402

1989 1.259 1.221 1.083 0.8204 0.7084 0.3

1990 4.786 4.581 3.9 2.937 2.461 0.8867
101

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 26.6 25.43 21.55 15.56 12.58 4.136

0.0645161290322581 11.38 10.91 9.375 7.136 5.955 2.191

0.0967741935483871 9.968 9.565 8.27 6.273 5.151 2.045

0.129032258064516 8.136 7.866 6.933 5.568 5.12 2.031

0.161290322580645 7.769 7.42 6.19 5.458 4.844 1.774

0.193548387096774 6.137 5.897 5.139 4.349 3.672 1.336

0.225806451612903 5.438 5.211 4.389 3.167 2.679 1.071

0.258064516129032 5.104 4.993 4.32 3.147 2.592 1.008

0.290322580645161 4.786 4.581 3.9 3.047 2.58 0.973

0.32258064516129 4.494 4.309 3.763 2.937 2.461 0.9048

0.354838709677419 3.539 3.391 2.866 2.235 2.081 0.8867

0.387096774193548 3.17 3.073 2.668 2.103 1.842 0.8377

0.419354838709677 3.097 2.964 2.616 2.088 1.743 0.8256

0.451612903225806 2.888 2.808 2.489 2.022 1.739 0.8241

0.483870967741936 2.805 2.69 2.393 2.01 1.737 0.8217

0.516129032258065 2.775 2.666 2.281 1.969 1.731 0.7756

0.548387096774194 2.691 2.599 2.257 1.838 1.691 0.7263

0.580645161290323 2.675 2.584 2.224 1.837 1.67 0.7161

0.612903225806452 2.605 2.496 2.196 1.823 1.63 0.702

0.645161290322581 2.519 2.429 2.182 1.754 1.532 0.6992

0.67741935483871 2.487 2.394 2.099 1.743 1.522 0.6908

0.709677419354839 2.415 2.328 2.044 1.58 1.329 0.69

0.741935483870968 2.201 2.12 1.927 1.523 1.314 0.5567

0.774193548387097 1.755 1.686 1.458 1.264 1.113 0.5402

0.806451612903226 1.583 1.518 1.294 1.129 1.045 0.4965

0.838709677419355 1.426 1.38 1.258 0.9451 0.7806 0.4549

0.870967741935484 1.259 1.221 1.083 0.8204 0.7716 0.3966

0.903225806451613 1.177 1.129 0.9598 0.8162 0.7084 0.3778

0.935483870967742 1.096 1.053 0.9011 0.7454 0.6782 0.3

0.967741935483871 0.7701 0.7393 0.6349 0.5708 0.5098 0.254

0.1 9.7848 9.3951 8.1363 6.2025 5.1479 2.0436

Average of yearly averages: 1.00141

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLnursey

Metfile: w12839.dvf

PRZM scenario: FLnurserySTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.5591 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval days Set to 0 or delete line for single app.

app. rate 1 apprate kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5
102

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Cabbage

stored as FLCABAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt modified Thuday, 24 May 2007 at 09:40:46

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12842.dvf modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.57 1.504 0.9523 0.5357 0.4295 0.1059

1962 1.237 1.19 1.024 0.7657 0.6498 0.3023

1963 4.429 4.292 3.634 2.51 1.749 0.4925

1964 1.796 1.747 1.626 1.329 1.141 0.5567

1965 0.952 0.917 0.799 0.6196 0.5475 0.2825

1966 0.6769 0.6544 0.5866 0.4964 0.4386 0.2236

1967 0.5583 0.5369 0.4595 0.3566 0.3104 0.165

1968 1.967 1.886 1.637 1.382 1.073 0.3693

1969 1.179 1.143 0.9789 0.7889 0.6218 0.366

1970 0.7665 0.7517 0.6723 0.5257 0.4473 0.2274

1971 1.018 0.9754 0.8503 0.6403 0.494 0.2548

1972 1.114 1.066 0.933 0.8296 0.6451 0.3019

1973 1.319 1.259 1.061 0.8634 0.6583 0.2942

1974 0.9926 0.9586 0.7198 0.4394 0.3725 0.2192

1975 1.595 1.524 1.274 0.9137 0.6984 0.3149

1976 0.6341 0.6193 0.5358 0.4467 0.3525 0.2272

1977 0.7478 0.7187 0.663 0.5103 0.4182 0.1963

1978 1.457 1.397 1.188 0.8622 0.6682 0.2707

1979 0.7743 0.7489 0.7076 0.5756 0.4955 0.2446

1980 0.9727 0.9362 0.8462 0.6225 0.493 0.2119

1981 1.41 1.36 0.6545 0.4951 0.4502 0.2581

1982 1.271 1.218 1.069 0.8186 0.6956 0.3322

1983 1.002 0.9802 0.857 0.589 0.4734 0.2531

1984 0.7922 0.7665 0.673 0.5206 0.4387 0.2126

1985 4.224 4.086 3.438 2.456 1.737 0.5007

1986 2.343 2.265 1.916 1.452 1.089 0.5599

1987 1.829 1.754 1.52 1.169 0.8622 0.4056

1988 2.686 2.57 2.172 1.467 1.059 0.4289

1989 1.352 1.294 1.13 0.9166 0.7426 0.4266

1990 0.689 0.6655 0.5797 0.4508 0.3828 0.1949

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.429 4.292 3.634 2.51 1.749 0.5599

0.0645161290322581 4.224 4.086 3.438 2.456 1.737 0.5567

0.0967741935483871 2.686 2.57 2.172 1.467 1.141 0.5007

0.129032258064516 2.343 2.265 1.916 1.452 1.089 0.4925

0.161290322580645 1.967 1.886 1.637 1.382 1.073 0.4289

0.193548387096774 1.829 1.754 1.626 1.329 1.059 0.4266

0.225806451612903 1.796 1.747 1.52 1.169 0.8622 0.4056

0.258064516129032 1.595 1.524 1.274 0.9166 0.7426 0.3693

0.290322580645161 1.57 1.504 1.188 0.9137 0.6984 0.366

0.32258064516129 1.457 1.397 1.13 0.8634 0.6956 0.3322

0.354838709677419 1.41 1.36 1.069 0.8622 0.6682 0.3149

0.387096774193548 1.352 1.294 1.061 0.8296 0.6583 0.3023

0.419354838709677 1.319 1.259 1.024 0.8186 0.6498 0.3019

0.451612903225806 1.271 1.218 0.9789 0.7889 0.6451 0.2942

0.483870967741936 1.237 1.19 0.9523 0.7657 0.6218 0.2825

0.516129032258065 1.179 1.143 0.933 0.6403 0.5475 0.2707

0.548387096774194 1.114 1.066 0.857 0.6225 0.4955 0.2581

0.580645161290323 1.018 0.9802 0.8503 0.6196 0.494 0.2548

0.612903225806452 1.002 0.9754 0.8462 0.589 0.493 0.2531

0.645161290322581 0.9926 0.9586 0.799 0.5756 0.4734 0.2446

0.67741935483871 0.9727 0.9362 0.7198 0.5357 0.4502 0.2274

0.709677419354839 0.952 0.917 0.7076 0.5257 0.4473 0.2272
103

0.741935483870968 0.7922 0.7665 0.673 0.5206 0.4387 0.2236

0.774193548387097 0.7743 0.7517 0.6723 0.5103 0.4386 0.2192

0.806451612903226 0.7665 0.7489 0.663 0.4964 0.4295 0.2126

0.838709677419355 0.7478 0.7187 0.6545 0.4951 0.4182 0.2119

0.870967741935484 0.689 0.6655 0.5866 0.4508 0.3828 0.1963

0.903225806451613 0.6769 0.6544 0.5797 0.4467 0.3725 0.1949

0.935483870967742 0.6341 0.6193 0.5358 0.4394 0.3525 0.165

0.967741935483871 0.5583 0.5369 0.4595 0.3566 0.3104 0.1059

0.1 2.6517 2.5395 2.1464 1.4655 1.1358 0.49988

Average of yearly averages: 0.30665

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABAIR

Metfile: w12842.dvf

PRZM scenario: FLcabbageSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as FLCABGRD.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt modified Thuday, 24 May 2007 at 09:40:46

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12842.dvf modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.498 1.434 0.859 0.3601 0.2545 0.06276

1962 1.177 1.132 0.9691 0.7203 0.6103 0.2414

1963 4.329 4.197 3.55 2.412 1.624 0.4375

1964 1.748 1.7 1.585 1.295 1.112 0.5009

1965 0.8685 0.8358 0.7266 0.5615 0.4977 0.2177

1966 0.6139 0.5925 0.5299 0.4327 0.3839 0.1566

1967 0.4246 0.4073 0.3451 0.2234 0.1835 0.09855

1968 1.766 1.692 1.464 1.183 0.9204 0.3109

1969 1.055 1.02 0.8715 0.6098 0.4922 0.3041
104

1970 0.6782 0.6658 0.5945 0.4619 0.3915 0.16

1971 0.6281 0.6108 0.5491 0.4084 0.3165 0.1923

1972 0.782 0.7477 0.6785 0.6343 0.469 0.2394

1973 1.028 0.981 0.8289 0.7007 0.4932 0.2308

1974 0.8899 0.8567 0.6145 0.3556 0.2999 0.1566

1975 1.284 1.227 1.024 0.726 0.5342 0.256

1976 0.358 0.3468 0.3055 0.2383 0.2301 0.1631

1977 0.5492 0.5269 0.4975 0.3226 0.2334 0.1262

1978 1.143 1.095 0.9278 0.675 0.4976 0.2045

1979 0.6928 0.6698 0.6343 0.5171 0.4454 0.1807

1980 0.755 0.7258 0.6646 0.439 0.3114 0.1454

1981 1.351 1.3 0.6188 0.4642 0.3986 0.1957

1982 1.214 1.162 1.02 0.7783 0.6608 0.2736

1983 0.8856 0.863 0.7501 0.4091 0.3007 0.1886

1984 0.7023 0.6787 0.5931 0.4552 0.3823 0.147

1985 4.05 3.921 3.297 2.353 1.616 0.4507

1986 2.054 1.981 1.678 1.284 0.9378 0.5109

1987 1.576 1.511 1.313 1.016 0.7014 0.3481

1988 2.584 2.471 2.086 1.335 0.9129 0.3747

1989 1.232 1.185 1.019 0.7868 0.6618 0.3749

1990 0.6054 0.5843 0.5073 0.3938 0.3344 0.1328

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.329 4.197 3.55 2.412 1.624 0.5109

0.0645161290322581 4.05 3.921 3.297 2.353 1.616 0.5009

0.0967741935483871 2.584 2.471 2.086 1.335 1.112 0.4507

0.129032258064516 2.054 1.981 1.678 1.295 0.9378 0.4375

0.161290322580645 1.766 1.7 1.585 1.284 0.9204 0.3749

0.193548387096774 1.748 1.692 1.464 1.183 0.9129 0.3747

0.225806451612903 1.576 1.511 1.313 1.016 0.7014 0.3481

0.258064516129032 1.498 1.434 1.024 0.7868 0.6618 0.3109

0.290322580645161 1.351 1.3 1.02 0.7783 0.6608 0.3041

0.32258064516129 1.284 1.227 1.019 0.726 0.6103 0.2736

0.354838709677419 1.232 1.185 0.9691 0.7203 0.5342 0.256

0.387096774193548 1.214 1.162 0.9278 0.7007 0.4977 0.2414

0.419354838709677 1.177 1.132 0.8715 0.675 0.4976 0.2394

0.451612903225806 1.143 1.095 0.859 0.6343 0.4932 0.2308

0.483870967741936 1.055 1.02 0.8289 0.6098 0.4922 0.2177

0.516129032258065 1.028 0.981 0.7501 0.5615 0.469 0.2045

0.548387096774194 0.8899 0.863 0.7266 0.5171 0.4454 0.1957

0.580645161290323 0.8856 0.8567 0.6785 0.4642 0.3986 0.1923

0.612903225806452 0.8685 0.8358 0.6646 0.4619 0.3915 0.1886

0.645161290322581 0.782 0.7477 0.6343 0.4552 0.3839 0.1807

0.67741935483871 0.755 0.7258 0.6188 0.439 0.3823 0.1631

0.709677419354839 0.7023 0.6787 0.6145 0.4327 0.3344 0.16

0.741935483870968 0.6928 0.6698 0.5945 0.4091 0.3165 0.1566

0.774193548387097 0.6782 0.6658 0.5931 0.4084 0.3114 0.1566

0.806451612903226 0.6281 0.6108 0.5491 0.3938 0.3007 0.147

0.838709677419355 0.6139 0.5925 0.5299 0.3601 0.2999 0.1454

0.870967741935484 0.6054 0.5843 0.5073 0.3556 0.2545 0.1328

0.903225806451613 0.5492 0.5269 0.4975 0.3226 0.2334 0.1262

0.935483870967742 0.4246 0.4073 0.3451 0.2383 0.2301 0.09855

0.967741935483871 0.358 0.3468 0.3055 0.2234 0.1835 0.06276

0.1 2.531 2.422 2.0452 1.331 1.09458 0.44938

Average of yearly averages: 0.246080333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABGRD

Metfile: w12842.dvf

PRZM scenario: FLcabbageSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr
105

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Cucumber

stored as FLCUCAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt modified Wedday, 13 June 2007 at 11:19:24

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.957 1.876 1.591 1.186 0.9082 0.2239

1962 1.165 1.116 0.9448 0.695 0.5566 0.2812

1963 1.693 1.629 1.425 1.251 1.048 0.3982

1964 3.226 3.098 2.647 2.379 1.741 0.7633

1965 7.096 6.872 5.832 4.3 3.212 1.102

1966 3.957 3.815 3.265 2.396 1.802 1.008

1967 2.335 2.242 1.9 1.406 1.056 0.5401

1968 1.96 1.882 1.642 1.337 1.034 0.4253

1969 4.387 4.258 3.681 2.765 2.102 0.7688

1970 1.36 1.323 1.19 0.9648 0.8372 0.3925

1971 3.1 2.98 2.595 1.954 1.486 0.4604

1972 8.095 7.776 6.626 4.65 3.187 1.017

1973 3.059 2.967 2.66 2.121 1.811 0.7887

1974 1.607 1.543 1.327 1.006 0.8165 0.4213

1975 1.039 0.9971 0.9272 0.7697 0.5958 0.3096

1976 2.845 2.738 2.349 1.797 1.312 0.4253

1977 2.245 2.18 1.892 1.266 0.9322 0.5128

1978 3.82 3.731 3.265 2.548 1.899 0.7031

1979 1.486 1.442 1.276 0.9987 0.8462 0.5064

1980 0.8746 0.8516 0.7737 0.6597 0.53 0.2741

1981 4.912 4.691 3.91 2.737 1.902 0.5653

1982 5.694 5.501 4.952 3.771 2.652 1.117

1983 3.939 3.785 3.502 2.685 2.011 0.9462

1984 4.937 4.747 4.068 2.997 2.143 0.8185

1985 2.257 2.174 1.876 1.417 1.193 0.5269

1986 3.206 3.095 2.885 2.32 1.772 0.741

1987 5.685 5.493 4.826 3.541 2.447 0.8523

1988 2.038 1.989 1.783 1.415 1.205 0.6471

1989 1.419 1.362 1.151 0.8318 0.674 0.3106

1990 1.511 1.445 1.21 0.8619 0.6534 0.323

Sorted results
106

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 8.095 7.776 6.626 4.65 3.212 1.117

0.0645161290322581 7.096 6.872 5.832 4.3 3.187 1.102

0.0967741935483871 5.694 5.501 4.952 3.771 2.652 1.017

0.129032258064516 5.685 5.493 4.826 3.541 2.447 1.008

0.161290322580645 4.937 4.747 4.068 2.997 2.143 0.9462

0.193548387096774 4.912 4.691 3.91 2.765 2.102 0.8523

0.225806451612903 4.387 4.258 3.681 2.737 2.011 0.8185

0.258064516129032 3.957 3.815 3.502 2.685 1.902 0.7887

0.290322580645161 3.939 3.785 3.265 2.548 1.899 0.7688

0.32258064516129 3.82 3.731 3.265 2.396 1.811 0.7633

0.354838709677419 3.226 3.098 2.885 2.379 1.802 0.741

0.387096774193548 3.206 3.095 2.66 2.32 1.772 0.7031

0.419354838709677 3.1 2.98 2.647 2.121 1.741 0.6471

0.451612903225806 3.059 2.967 2.595 1.954 1.486 0.5653

0.483870967741936 2.845 2.738 2.349 1.797 1.312 0.5401

0.516129032258065 2.335 2.242 1.9 1.417 1.205 0.5269

0.548387096774194 2.257 2.18 1.892 1.415 1.193 0.5128

0.580645161290323 2.245 2.174 1.876 1.406 1.056 0.5064

0.612903225806452 2.038 1.989 1.783 1.337 1.048 0.4604

0.645161290322581 1.96 1.882 1.642 1.266 1.034 0.4253

0.67741935483871 1.957 1.876 1.591 1.251 0.9322 0.4253

0.709677419354839 1.693 1.629 1.425 1.186 0.9082 0.4213

0.741935483870968 1.607 1.543 1.327 1.006 0.8462 0.3982

0.774193548387097 1.511 1.445 1.276 0.9987 0.8372 0.3925

0.806451612903226 1.486 1.442 1.21 0.9648 0.8165 0.323

0.838709677419355 1.419 1.362 1.19 0.8619 0.674 0.3106

0.870967741935484 1.36 1.323 1.151 0.8318 0.6534 0.3096

0.903225806451613 1.165 1.116 0.9448 0.7697 0.5958 0.2812

0.935483870967742 1.039 0.9971 0.9272 0.695 0.5566 0.2741

0.967741935483871 0.8746 0.8516 0.7737 0.6597 0.53 0.2239

0.1 5.6931 5.5002 4.9394 3.748 2.6315 1.0161

Average of yearly averages: 0.605663333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCAIR

Metfile: w12844.dvf

PRZM scenario: FLcucumberSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804
107

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as FLCUCGRD.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt modified Wedday, 13 June 2007 at 11:19:24

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.669 1.599 1.357 0.9868 0.75 0.1849

1962 0.7889 0.7554 0.6399 0.4701 0.377 0.2176

1963 1.554 1.421 1.22 1.056 0.8879 0.337

1964 2.996 2.876 2.452 2.246 1.607 0.7155

1965 7.044 6.817 5.789 4.232 3.15 1.072

1966 3.686 3.556 3.047 2.238 1.676 0.9728

1967 2.014 1.933 1.638 1.216 0.8961 0.4857

1968 1.614 1.55 1.358 1.129 0.8736 0.3655

1969 4.183 4.063 3.518 2.628 1.987 0.7223

1970 1.301 1.266 1.139 0.9231 0.8008 0.333

1971 2.901 2.787 2.421 1.801 1.343 0.405

1972 8.124 7.803 6.646 4.635 3.117 0.9831

1973 3.064 2.971 2.664 2.123 1.813 0.7447

1974 1.423 1.365 1.173 0.8411 0.6494 0.3648

1975 0.7975 0.765 0.6635 0.5467 0.4224 0.248

1976 2.628 2.528 2.167 1.657 1.161 0.3674

1977 2.114 2.055 1.784 1.115 0.7733 0.457

1978 3.679 3.586 3.146 2.411 1.778 0.6572

1979 1.43 1.387 1.226 0.9578 0.8118 0.4523

1980 0.6931 0.6763 0.5828 0.4659 0.3494 0.21

1981 4.8 4.584 3.817 2.654 1.788 0.5157

1982 5.627 5.438 4.872 3.719 2.562 1.09

1983 3.679 3.536 3.305 2.55 1.895 0.9107

1984 4.922 4.728 4.051 2.923 2.038 0.7791

1985 2.24 2.158 1.86 1.403 1.18 0.4781

1986 2.938 2.891 2.66 2.162 1.651 0.7001

1987 5.599 5.399 4.751 3.481 2.348 0.8137

1988 2.004 1.955 1.753 1.39 1.183 0.5997

1989 1.065 1.023 0.8664 0.6273 0.5054 0.2526

1990 1.141 1.091 0.9133 0.6506 0.4854 0.264

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 8.124 7.803 6.646 4.635 3.15 1.09

0.0645161290322581 7.044 6.817 5.789 4.232 3.117 1.072

0.0967741935483871 5.627 5.438 4.872 3.719 2.562 0.9831

0.129032258064516 5.599 5.399 4.751 3.481 2.348 0.9728

0.161290322580645 4.922 4.728 4.051 2.923 2.038 0.9107

0.193548387096774 4.8 4.584 3.817 2.654 1.987 0.8137

0.225806451612903 4.183 4.063 3.518 2.628 1.895 0.7791

0.258064516129032 3.686 3.586 3.305 2.55 1.813 0.7447

0.290322580645161 3.679 3.556 3.146 2.411 1.788 0.7223

0.32258064516129 3.679 3.536 3.047 2.246 1.778 0.7155

0.354838709677419 3.064 2.971 2.664 2.238 1.676 0.7001

0.387096774193548 2.996 2.891 2.66 2.162 1.651 0.6572

0.419354838709677 2.938 2.876 2.452 2.123 1.607 0.5997

0.451612903225806 2.901 2.787 2.421 1.801 1.343 0.5157

0.483870967741936 2.628 2.528 2.167 1.657 1.183 0.4857

0.516129032258065 2.24 2.158 1.86 1.403 1.18 0.4781

0.548387096774194 2.114 2.055 1.784 1.39 1.161 0.457

0.580645161290323 2.014 1.955 1.753 1.216 0.8961 0.4523

0.612903225806452 2.004 1.933 1.638 1.129 0.8879 0.405

0.645161290322581 1.669 1.599 1.358 1.115 0.8736 0.3674

0.67741935483871 1.614 1.55 1.357 1.056 0.8118 0.3655

0.709677419354839 1.554 1.421 1.226 0.9868 0.8008 0.3648

0.741935483870968 1.43 1.387 1.22 0.9578 0.7733 0.337

0.774193548387097 1.423 1.365 1.173 0.9231 0.75 0.333
108

0.806451612903226 1.301 1.266 1.139 0.8411 0.6494 0.264

0.838709677419355 1.141 1.091 0.9133 0.6506 0.5054 0.2526

0.870967741935484 1.065 1.023 0.8664 0.6273 0.4854 0.248

0.903225806451613 0.7975 0.765 0.6635 0.5467 0.4224 0.2176

0.935483870967742 0.7889 0.7554 0.6399 0.4701 0.377 0.21

0.967741935483871 0.6931 0.6763 0.5828 0.4659 0.3494 0.1849

0.1 5.6242 5.4341 4.8599 3.6952 2.5406 0.98207

Average of yearly averages: 0.55665

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCGRD

Metfile: w12844.dvf

PRZM scenario: FLcucumberSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Pepper

stored as FLPEPAIR.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt modified Thuday, 24 May 2007 at 09:44:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.316 1.26 1.093 0.9206 0.7992 0.2289

1962 4.773 4.594 4.026 2.921 2.398 0.7324

1963 3.28 3.212 2.969 2.431 2.029 0.7821

1964 5.151 5.019 4.583 3.591 2.98 1.01

1965 4.786 4.586 3.983 2.925 2.372 0.9019

1966 3.556 3.458 3.324 2.707 2.291 0.9386

1967 4.095 3.949 3.624 3.075 2.567 0.8872

1968 3.835 3.756 3.374 2.55 2.175 0.855

1969 3.961 3.81 3.619 2.826 2.359 0.8713
109

1970 3.606 3.458 3.243 2.555 2.1 0.7771

1971 2.835 2.723 2.379 1.942 1.668 0.6312

1972 3.69 3.551 3.046 2.201 1.776 0.6878

1973 2.699 2.629 2.325 1.805 1.509 0.738

1974 2.806 2.694 2.315 1.86 1.655 0.5912

1975 6.81 6.519 5.704 4.208 3.454 1.091

1976 5.799 5.561 4.792 3.595 2.992 1.105

1977 6.199 5.965 5.491 4.449 3.698 1.304

1978 2.007 1.932 1.677 1.377 1.23 0.641

1979 8.948 8.59 7.512 5.532 4.545 1.383

1980 2.795 2.676 2.263 1.829 1.579 0.798

1981 4.804 4.634 3.957 3.112 2.617 0.8516

1982 2.733 2.625 2.336 1.894 1.603 0.6676

1983 4.467 4.276 3.627 2.656 2.173 0.7597

1984 3.618 3.471 3.082 2.348 1.964 0.7407

1985 5.276 5.05 4.468 3.34 2.717 0.9128

1986 1.766 1.718 1.479 1.214 1.149 0.5519

1987 4.138 3.966 3.509 2.855 2.379 0.78

1988 2.402 2.294 1.912 1.523 1.264 0.5688

1989 2.09 1.997 1.76 1.497 1.264 0.4898

1990 7.377 7.052 6.316 4.64 3.767 1.138

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 8.948 8.59 7.512 5.532 4.545 1.383

0.0645161290322581 7.377 7.052 6.316 4.64 3.767 1.304

0.0967741935483871 6.81 6.519 5.704 4.449 3.698 1.138

0.129032258064516 6.199 5.965 5.491 4.208 3.454 1.105

0.161290322580645 5.799 5.561 4.792 3.595 2.992 1.091

0.193548387096774 5.276 5.05 4.583 3.591 2.98 1.01

0.225806451612903 5.151 5.019 4.468 3.34 2.717 0.9386

0.258064516129032 4.804 4.634 4.026 3.112 2.617 0.9128

0.290322580645161 4.786 4.594 3.983 3.075 2.567 0.9019

0.32258064516129 4.773 4.586 3.957 2.925 2.398 0.8872

0.354838709677419 4.467 4.276 3.627 2.921 2.379 0.8713

0.387096774193548 4.138 3.966 3.624 2.855 2.372 0.855

0.419354838709677 4.095 3.949 3.619 2.826 2.359 0.8516

0.451612903225806 3.961 3.81 3.509 2.707 2.291 0.798

0.483870967741936 3.835 3.756 3.374 2.656 2.175 0.7821

0.516129032258065 3.69 3.551 3.324 2.555 2.173 0.78

0.548387096774194 3.618 3.471 3.243 2.55 2.1 0.7771

0.580645161290323 3.606 3.458 3.082 2.431 2.029 0.7597

0.612903225806452 3.556 3.458 3.046 2.348 1.964 0.7407

0.645161290322581 3.28 3.212 2.969 2.201 1.776 0.738

0.67741935483871 2.835 2.723 2.379 1.942 1.668 0.7324

0.709677419354839 2.806 2.694 2.336 1.894 1.655 0.6878

0.741935483870968 2.795 2.676 2.325 1.86 1.603 0.6676

0.774193548387097 2.733 2.629 2.315 1.829 1.579 0.641

0.806451612903226 2.699 2.625 2.263 1.805 1.509 0.6312

0.838709677419355 2.402 2.294 1.912 1.523 1.264 0.5912

0.870967741935484 2.09 1.997 1.76 1.497 1.264 0.5688

0.903225806451613 2.007 1.932 1.677 1.377 1.23 0.5519

0.935483870967742 1.766 1.718 1.479 1.214 1.149 0.4898

0.967741935483871 1.316 1.26 1.093 0.9206 0.7992 0.2289

0.1 6.7489 6.4636 5.6827 4.4249 3.6736 1.1347

Average of yearly averages: 0.813853333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPAIR

Metfile: w12844.dvf

PRZM scenario: FLpeppersSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr
110

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-9 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Interval 2 interval 5 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as FLPEPGRD.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt modified Thuday, 24 May 2007 at 09:44:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.8142 0.7789 0.6798 0.6246 0.5451 0.1511

1962 4.479 4.298 3.774 2.734 2.24 0.65

1963 2.903 2.831 2.638 2.15 1.8 0.6962

1964 4.869 4.732 4.297 3.388 2.813 0.9318

1965 4.659 4.462 3.872 2.841 2.264 0.8237

1966 3.15 3.046 2.947 2.425 2.056 0.8599

1967 3.865 3.727 3.354 2.861 2.393 0.8057

1968 3.569 3.497 3.129 2.357 1.959 0.7732

1969 3.626 3.49 3.29 2.577 2.135 0.7869

1970 3.289 3.153 2.9 2.314 1.905 0.6946

1971 2.333 2.241 1.97 1.639 1.419 0.5424

1972 3.634 3.495 2.992 2.14 1.648 0.6029

1973 2.262 2.182 1.949 1.528 1.263 0.6549

1974 2.547 2.445 2.1 1.629 1.409 0.5045

1975 6.555 6.274 5.504 4.041 3.319 1.025

1976 5.437 5.213 4.49 3.383 2.818 1.038

1977 6.014 5.789 5.215 4.255 3.538 1.246

1978 1.693 1.628 1.408 1.098 0.9637 0.555

1979 8.728 8.378 7.329 5.39 4.424 1.326

1980 2.35 2.25 1.893 1.527 1.331 0.72

1981 4.496 4.328 3.699 2.87 2.425 0.777

1982 2.456 2.358 2.058 1.689 1.433 0.5844

1983 4.179 3.999 3.39 2.476 2.021 0.6794

1984 3.32 3.185 2.781 2.139 1.795 0.6617

1985 4.969 4.756 4.218 3.154 2.567 0.8435

1986 1.563 1.523 1.311 0.9701 0.8959 0.4688

1987 3.866 3.704 3.261 2.632 2.197 0.7028

1988 2.148 2.05 1.703 1.375 1.132 0.4855

1989 1.645 1.571 1.406 1.252 1.053 0.4054

1990 7.161 6.845 6.157 4.529 3.676 1.078

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 8.728 8.378 7.329 5.39 4.424 1.326
111

0.0645161290322581 7.161 6.845 6.157 4.529 3.676 1.246

0.0967741935483871 6.555 6.274 5.504 4.255 3.538 1.078

0.129032258064516 6.014 5.789 5.215 4.041 3.319 1.038

0.161290322580645 5.437 5.213 4.49 3.388 2.818 1.025

0.193548387096774 4.969 4.756 4.297 3.383 2.813 0.9318

0.225806451612903 4.869 4.732 4.218 3.154 2.567 0.8599

0.258064516129032 4.659 4.462 3.872 2.87 2.425 0.8435

0.290322580645161 4.496 4.328 3.774 2.861 2.393 0.8237

0.32258064516129 4.479 4.298 3.699 2.841 2.264 0.8057

0.354838709677419 4.179 3.999 3.39 2.734 2.24 0.7869

0.387096774193548 3.866 3.727 3.354 2.632 2.197 0.777

0.419354838709677 3.865 3.704 3.29 2.577 2.135 0.7732

0.451612903225806 3.634 3.497 3.261 2.476 2.056 0.72

0.483870967741936 3.626 3.495 3.129 2.425 2.021 0.7028

0.516129032258065 3.569 3.49 2.992 2.357 1.959 0.6962

0.548387096774194 3.32 3.185 2.947 2.314 1.905 0.6946

0.580645161290323 3.289 3.153 2.9 2.15 1.8 0.6794

0.612903225806452 3.15 3.046 2.781 2.14 1.795 0.6617

0.645161290322581 2.903 2.831 2.638 2.139 1.648 0.6549

0.67741935483871 2.547 2.445 2.1 1.689 1.433 0.65

0.709677419354839 2.456 2.358 2.058 1.639 1.419 0.6029

0.741935483870968 2.35 2.25 1.97 1.629 1.409 0.5844

0.774193548387097 2.333 2.241 1.949 1.528 1.331 0.555

0.806451612903226 2.262 2.182 1.893 1.527 1.263 0.5424

0.838709677419355 2.148 2.05 1.703 1.375 1.132 0.5045

0.870967741935484 1.693 1.628 1.408 1.252 1.053 0.4855

0.903225806451613 1.645 1.571 1.406 1.098 0.9637 0.4688

0.935483870967742 1.563 1.523 1.311 0.9701 0.8959 0.4054

0.967741935483871 0.8142 0.7789 0.6798 0.6246 0.5451 0.1511

0.1 6.5009 6.2255 5.4751 4.2336 3.5161 1.074

Average of yearly averages: 0.73581

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPGRD

Metfile: w12844.dvf

PRZM scenario: FLpeppersSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-9 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Interval 2 interval 5 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond
112

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Tomato

stored as FLTOMAIR.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt modified Tueday, 29 May 2007 at 12:54:10

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.534 1.472 1.389 1.076 0.8949 0.3531

1962 1.586 1.523 1.327 1.022 0.8514 0.3713

1963 0.8275 0.7959 0.6812 0.5225 0.4605 0.2431

1964 1.929 1.85 1.612 1.198 1.035 0.4031

1965 1.217 1.177 1.005 0.785 0.6706 0.2794

1966 4.861 4.671 3.995 2.995 2.46 0.8862

1967 1.952 1.876 1.592 1.34 1.143 0.4809

1968 1.176 1.128 0.9564 0.7444 0.6382 0.2554

1969 1.641 1.583 1.39 1.165 1.033 0.407

1970 2.673 2.572 2.382 1.845 1.524 0.597

1971 0.8983 0.8674 0.7374 0.5635 0.4665 0.2417

1972 1.144 1.098 0.9347 0.7631 0.7171 0.2905

1973 0.847 0.8151 0.7179 0.5996 0.5369 0.2247

1974 1.628 1.558 1.306 0.9668 0.8058 0.3301

1975 0.5509 0.5285 0.4482 0.3331 0.2735 0.1611

1976 2.65 2.555 2.266 1.668 1.37 0.5002

1977 1.654 1.587 1.46 1.17 0.962 0.396

1978 0.8772 0.8431 0.7262 0.5754 0.4826 0.1822

1979 4.03 3.86 3.265 2.364 1.909 0.6883

1980 1.775 1.703 1.484 1.132 0.9456 0.3614

1981 1.651 1.582 1.333 1.012 0.8467 0.3175

1982 1.94 1.861 1.63 1.353 1.137 0.4349

1983 1.979 1.912 1.757 1.345 1.122 0.3937

1984 3.769 3.617 3.07 2.379 2.011 0.7126

1985 2.194 2.1 1.765 1.484 1.257 0.4856

1986 1.346 1.292 1.164 0.9305 0.8126 0.3166

1987 2.125 2.042 1.873 1.415 1.156 0.4231

1988 0.8595 0.8261 0.7485 0.6793 0.609 0.239

1989 1.105 1.081 0.9269 0.6584 0.5858 0.2607

1990 1.07 1.024 0.8643 0.6427 0.5633 0.2283

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.861 4.671 3.995 2.995 2.46 0.8862

0.0645161290322581 4.03 3.86 3.265 2.379 2.011 0.7126

0.0967741935483871 3.769 3.617 3.07 2.364 1.909 0.6883

0.129032258064516 2.673 2.572 2.382 1.845 1.524 0.597

0.161290322580645 2.65 2.555 2.266 1.668 1.37 0.5002

0.193548387096774 2.194 2.1 1.873 1.484 1.257 0.4856

0.225806451612903 2.125 2.042 1.765 1.415 1.156 0.4809

0.258064516129032 1.979 1.912 1.757 1.353 1.143 0.4349

0.290322580645161 1.952 1.876 1.63 1.345 1.137 0.4231

0.32258064516129 1.94 1.861 1.612 1.34 1.122 0.407

0.354838709677419 1.929 1.85 1.592 1.198 1.035 0.4031

0.387096774193548 1.775 1.703 1.484 1.17 1.033 0.396

0.419354838709677 1.654 1.587 1.46 1.165 0.962 0.3937

0.451612903225806 1.651 1.583 1.39 1.132 0.9456 0.3713

0.483870967741936 1.641 1.582 1.389 1.076 0.8949 0.3614

0.516129032258065 1.628 1.558 1.333 1.022 0.8514 0.3531

0.548387096774194 1.586 1.523 1.327 1.012 0.8467 0.3301
113

0.580645161290323 1.534 1.472 1.306 0.9668 0.8126 0.3175

0.612903225806452 1.346 1.292 1.164 0.9305 0.8058 0.3166

0.645161290322581 1.217 1.177 1.005 0.785 0.7171 0.2905

0.67741935483871 1.176 1.128 0.9564 0.7631 0.6706 0.2794

0.709677419354839 1.144 1.098 0.9347 0.7444 0.6382 0.2607

0.741935483870968 1.105 1.081 0.9269 0.6793 0.609 0.2554

0.774193548387097 1.07 1.024 0.8643 0.6584 0.5858 0.2431

0.806451612903226 0.8983 0.8674 0.7485 0.6427 0.5633 0.2417

0.838709677419355 0.8772 0.8431 0.7374 0.5996 0.5369 0.239

0.870967741935484 0.8595 0.8261 0.7262 0.5754 0.4826 0.2283

0.903225806451613 0.847 0.8151 0.7179 0.5635 0.4665 0.2247

0.935483870967742 0.8275 0.7959 0.6812 0.5225 0.4605 0.1822

0.967741935483871 0.5509 0.5285 0.4482 0.3331 0.2735 0.1611

0.1 3.6594 3.5125 3.0012 2.3121 1.8705 0.67917

Average of yearly averages: 0.382156666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMAIR

Metfile: w12844.dvf

PRZM scenario: FLtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as FLTOMGRD.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt modified Tueday, 29 May 2007 at 12:54:10

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.434 1.374 1.283 0.9973 0.8287 0.2941

1962 1.484 1.423 1.239 0.9516 0.7921 0.3129

1963 0.691 0.6692 0.5747 0.424 0.3485 0.1772

1964 1.576 1.538 1.327 0.9841 0.8619 0.343

1965 0.9527 0.9222 0.7872 0.5688 0.4807 0.2164

1966 4.746 4.56 3.894 2.921 2.398 0.8443

1967 1.711 1.643 1.392 1.201 1.032 0.4259

1968 0.9146 0.8772 0.7418 0.5602 0.4681 0.1904
114

1969 1.465 1.412 1.239 0.9861 0.8869 0.3438

1970 2.547 2.45 2.267 1.761 1.451 0.5431

1971 0.8616 0.8304 0.703 0.5344 0.4398 0.1786

1972 0.7846 0.7529 0.6395 0.5522 0.5461 0.2268

1973 0.5384 0.5177 0.4434 0.3972 0.3582 0.1559

1974 1.492 1.426 1.192 0.8806 0.734 0.2717

1975 0.398 0.3815 0.3389 0.2576 0.2145 0.09435

1976 2.488 2.394 2.132 1.563 1.283 0.4476

1977 1.639 1.571 1.442 1.156 0.9484 0.3377

1978 0.4972 0.4782 0.4097 0.3389 0.2856 0.1145

1979 4.094 3.92 3.311 2.391 1.929 0.6441

1980 1.581 1.516 1.298 0.9959 0.8245 0.3029

1981 1.385 1.326 1.116 0.856 0.7025 0.2583

1982 1.797 1.723 1.512 1.254 1.055 0.3794

1983 1.699 1.632 1.514 1.166 0.9583 0.3358

1984 3.535 3.392 2.878 2.247 1.908 0.6688

1985 2.103 2.011 1.686 1.431 1.213 0.4345

1986 1.177 1.129 1.025 0.805 0.6837 0.259

1987 1.963 1.885 1.741 1.318 1.075 0.3667

1988 0.6825 0.6553 0.5862 0.4917 0.4369 0.1757

1989 1.039 1.014 0.8669 0.6108 0.4944 0.2025

1990 0.8114 0.7761 0.6527 0.4824 0.4062 0.1659

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.746 4.56 3.894 2.921 2.398 0.8443

0.0645161290322581 4.094 3.92 3.311 2.391 1.929 0.6688

0.0967741935483871 3.535 3.392 2.878 2.247 1.908 0.6441

0.129032258064516 2.547 2.45 2.267 1.761 1.451 0.5431

0.161290322580645 2.488 2.394 2.132 1.563 1.283 0.4476

0.193548387096774 2.103 2.011 1.741 1.431 1.213 0.4345

0.225806451612903 1.963 1.885 1.686 1.318 1.075 0.4259

0.258064516129032 1.797 1.723 1.514 1.254 1.055 0.3794

0.290322580645161 1.711 1.643 1.512 1.201 1.032 0.3667

0.32258064516129 1.699 1.632 1.442 1.166 0.9583 0.3438

0.354838709677419 1.639 1.571 1.392 1.156 0.9484 0.343

0.387096774193548 1.581 1.538 1.327 0.9973 0.8869 0.3377

0.419354838709677 1.576 1.516 1.298 0.9959 0.8619 0.3358

0.451612903225806 1.492 1.426 1.283 0.9861 0.8287 0.3129

0.483870967741936 1.484 1.423 1.239 0.9841 0.8245 0.3029

0.516129032258065 1.465 1.412 1.239 0.9516 0.7921 0.2941

0.548387096774194 1.434 1.374 1.192 0.8806 0.734 0.2717

0.580645161290323 1.385 1.326 1.116 0.856 0.7025 0.259

0.612903225806452 1.177 1.129 1.025 0.805 0.6837 0.2583

0.645161290322581 1.039 1.014 0.8669 0.6108 0.5461 0.2268

0.67741935483871 0.9527 0.9222 0.7872 0.5688 0.4944 0.2164

0.709677419354839 0.9146 0.8772 0.7418 0.5602 0.4807 0.2025

0.741935483870968 0.8616 0.8304 0.703 0.5522 0.4681 0.1904

0.774193548387097 0.8114 0.7761 0.6527 0.5344 0.4398 0.1786

0.806451612903226 0.7846 0.7529 0.6395 0.4917 0.4369 0.1772

0.838709677419355 0.691 0.6692 0.5862 0.4824 0.4062 0.1757

0.870967741935484 0.6825 0.6553 0.5747 0.424 0.3582 0.1659

0.903225806451613 0.5384 0.5177 0.4434 0.3972 0.3485 0.1559

0.935483870967742 0.4972 0.4782 0.4097 0.3389 0.2856 0.1145

0.967741935483871 0.398 0.3815 0.3389 0.2576 0.2145 0.09435

0.1 3.4362 3.2978 2.8169 2.1984 1.8623 0.634

Average of yearly averages: 0.323728333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMGRD

Metfile: w12844.dvf

PRZM scenario: FLtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol
115

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Turf

stored as FLTURFGRD.out

Chemical: DPXE2Y45

PRZM environment: FLturfSTD.txt modified Tueday, 21 February 2006 at 14:38:26

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12834.dvf modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3042 0.292 0.248 0.184 0.1522 0.05619

1962 0.2756 0.2644 0.224 0.1687 0.1403 0.0804

1963 0.3138 0.302 0.2591 0.1966 0.1632 0.06292

1964 0.2777 0.2672 0.2289 0.1733 0.1509 0.07009

1965 0.2786 0.2679 0.2292 0.1743 0.1456 0.05886

1966 0.2787 0.2685 0.2442 0.2043 0.1995 0.08819

1967 0.28 0.269 0.2291 0.1719 0.1421 0.06219

1968 0.2937 0.283 0.2478 0.1849 0.1524 0.09058

1969 0.2852 0.2744 0.2354 0.1801 0.151 0.06719

1970 0.3967 0.3813 0.3256 0.2513 0.21 0.07387

1971 1.286 1.232 1.04 0.7549 0.6394 0.231

1972 0.3977 0.382 0.3253 0.241 0.2269 0.1013

1973 0.2814 0.2702 0.23 0.174 0.1448 0.05184

1974 0.2737 0.2622 0.2209 0.1647 0.1359 0.04858

1975 0.2749 0.264 0.2247 0.1682 0.1516 0.05927

1976 1.351 1.292 1.08 0.7859 0.648 0.2463

1977 0.328 0.3153 0.2695 0.2058 0.1704 0.07419

1978 0.3865 0.3718 0.3196 0.2377 0.2132 0.08487

1979 0.4489 0.43 0.3653 0.2801 0.2462 0.09866

1980 0.2803 0.2697 0.2313 0.1754 0.1476 0.05238

1981 0.8062 0.7737 0.6558 0.4731 0.3945 0.1383

1982 0.3456 0.3324 0.2848 0.2089 0.2055 0.09071

1983 0.4123 0.3967 0.3593 0.3184 0.2835 0.1045

1984 0.5425 0.5202 0.4403 0.3359 0.2939 0.1382

1985 0.2841 0.2727 0.2318 0.173 0.1472 0.05542

1986 0.2749 0.2637 0.2236 0.1665 0.1364 0.05373

1987 0.8409 0.8089 0.7123 0.5376 0.444 0.1532

1988 0.2814 0.2702 0.2295 0.1735 0.1439 0.05056

1989 0.2724 0.2605 0.2179 0.1616 0.134 0.05133

1990 0.7528 0.7275 0.6182 0.4394 0.3664 0.13

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly
116

0.032258064516129 1.351 1.292 1.08 0.7859 0.648 0.2463

0.0645161290322581 1.286 1.232 1.04 0.7549 0.6394 0.231

0.0967741935483871 0.8409 0.8089 0.7123 0.5376 0.444 0.1532

0.129032258064516 0.8062 0.7737 0.6558 0.4731 0.3945 0.1383

0.161290322580645 0.7528 0.7275 0.6182 0.4394 0.3664 0.1382

0.193548387096774 0.5425 0.5202 0.4403 0.3359 0.2939 0.13

0.225806451612903 0.4489 0.43 0.3653 0.3184 0.2835 0.1045

0.258064516129032 0.4123 0.3967 0.3593 0.2801 0.2462 0.1013

0.290322580645161 0.3977 0.382 0.3256 0.2513 0.2269 0.09866

0.32258064516129 0.3967 0.3813 0.3253 0.241 0.2132 0.09071

0.354838709677419 0.3865 0.3718 0.3196 0.2377 0.21 0.09058

0.387096774193548 0.3456 0.3324 0.2848 0.2089 0.2055 0.08819

0.419354838709677 0.328 0.3153 0.2695 0.2058 0.1995 0.08487

0.451612903225806 0.3138 0.302 0.2591 0.2043 0.1704 0.0804

0.483870967741936 0.3042 0.292 0.248 0.1966 0.1632 0.07419

0.516129032258065 0.2937 0.283 0.2478 0.1849 0.1524 0.07387

0.548387096774194 0.2852 0.2744 0.2442 0.184 0.1522 0.07009

0.580645161290323 0.2841 0.2727 0.2354 0.1801 0.1516 0.06719

0.612903225806452 0.2814 0.2702 0.2318 0.1754 0.151 0.06292

0.645161290322581 0.2814 0.2702 0.2313 0.1743 0.1509 0.06219

0.67741935483871 0.2803 0.2697 0.23 0.174 0.1476 0.05927

0.709677419354839 0.28 0.269 0.2295 0.1735 0.1472 0.05886

0.741935483870968 0.2787 0.2685 0.2292 0.1733 0.1456 0.05619

0.774193548387097 0.2786 0.2679 0.2291 0.173 0.1448 0.05542

0.806451612903226 0.2777 0.2672 0.2289 0.1719 0.1439 0.05373

0.838709677419355 0.2756 0.2644 0.2247 0.1687 0.1421 0.05238

0.870967741935484 0.2749 0.264 0.224 0.1682 0.1403 0.05184

0.903225806451613 0.2749 0.2637 0.2236 0.1665 0.1364 0.05133

0.935483870967742 0.2737 0.2622 0.2209 0.1647 0.1359 0.05056

0.967741935483871 0.2724 0.2605 0.2179 0.1616 0.134 0.04858

0.1 0.83743 0.80538 0.70665 0.53115 0.43905 0.15171

Average of yearly averages: 0.0908273333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTURFGRD

Metfile: w12834.dvf

PRZM scenario: FLturfSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.2912 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.2912 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)
117

stored as FLTF19GRD.out

Chemical: DPXE2Y45

PRZM environment: FLturfSTD.txt modified Tueday, 21 February 2006 at 13:38:26

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 15:33:30

Metfile: w12834.dvf modified Wedday, 3 July 2002 at 08:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.2069 0.1995 0.1706 0.1294 0.1186 0.06416

1962 0.3577 0.3443 0.2956 0.2465 0.2082 0.09847

1963 0.4252 0.4087 0.3514 0.2613 0.2306 0.1115

1964 0.415 0.3984 0.3584 0.2845 0.2708 0.126

1965 0.2586 0.249 0.2176 0.17 0.1478 0.07985

1966 0.5722 0.5517 0.5084 0.4391 0.3785 0.1814

1967 0.2199 0.2123 0.1941 0.1543 0.1386 0.08019

1968 0.7728 0.7506 0.659 0.4937 0.4052 0.1595

1969 0.2794 0.2721 0.2397 0.2093 0.1799 0.09624

1970 0.1152 0.1112 0.1073 0.1049 0.1017 0.05311

1971 0.305 0.2939 0.2539 0.2153 0.2037 0.1164

1972 0.5046 0.4836 0.4246 0.3401 0.3216 0.1547

1973 0.1162 0.1124 0.108 0.1041 0.1005 0.0555

1974 0.1137 0.1098 0.1032 0.09852 0.09491 0.05044

1975 0.1388 0.1333 0.1268 0.1226 0.1156 0.05526

1976 1.013 0.9679 0.8226 0.646 0.5972 0.2292

1977 0.1971 0.1893 0.176 0.1373 0.1284 0.08563

1978 0.4537 0.4398 0.38 0.3111 0.2791 0.117

1979 0.4116 0.4017 0.3548 0.2755 0.2525 0.1202

1980 0.1129 0.1088 0.1051 0.1019 0.0987 0.05299

1981 0.159 0.1527 0.1459 0.1344 0.1291 0.06668

1982 0.5367 0.5149 0.4547 0.3565 0.3437 0.1504

1983 0.495 0.4758 0.4091 0.3247 0.2723 0.1407

1984 1.095 1.06 0.9081 0.6616 0.5415 0.2354

1985 0.16 0.1542 0.1329 0.1198 0.1175 0.06582

1986 0.1616 0.1552 0.1349 0.1116 0.1053 0.06136

1987 0.1791 0.1726 0.1599 0.1439 0.1353 0.066

1988 0.1073 0.1034 0.09857 0.09406 0.08995 0.04502

1989 0.1393 0.1334 0.1267 0.1146 0.1038 0.05085

1990 0.193 0.1865 0.1715 0.151 0.1417 0.0654

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.095 1.06 0.9081 0.6616 0.5972 0.2354

0.0645161290322581 1.013 0.9679 0.8226 0.646 0.5415 0.2292

0.0967741935483871 0.7728 0.7506 0.659 0.4937 0.4052 0.1814

0.129032258064516 0.5722 0.5517 0.5084 0.4391 0.3785 0.1595

0.161290322580645 0.5367 0.5149 0.4547 0.3565 0.3437 0.1547

0.193548387096774 0.5046 0.4836 0.4246 0.3401 0.3216 0.1504

0.225806451612903 0.495 0.4758 0.4091 0.3247 0.2791 0.1407

0.258064516129032 0.4537 0.4398 0.38 0.3111 0.2723 0.126

0.290322580645161 0.4252 0.4087 0.3584 0.2845 0.2708 0.1202

0.32258064516129 0.415 0.4017 0.3548 0.2755 0.2525 0.117

0.354838709677419 0.4116 0.3984 0.3514 0.2613 0.2306 0.1164

0.387096774193548 0.3577 0.3443 0.2956 0.2465 0.2082 0.1115

0.419354838709677 0.305 0.2939 0.2539 0.2153 0.2037 0.09847

0.451612903225806 0.2794 0.2721 0.2397 0.2093 0.1799 0.09624

0.483870967741936 0.2586 0.249 0.2176 0.17 0.1478 0.08563

0.516129032258065 0.2199 0.2123 0.1941 0.1543 0.1417 0.08019

0.548387096774194 0.2069 0.1995 0.176 0.151 0.1386 0.07985

0.580645161290323 0.1971 0.1893 0.1715 0.1439 0.1353 0.06668

0.612903225806452 0.193 0.1865 0.1706 0.1373 0.1291 0.066

0.645161290322581 0.1791 0.1726 0.1599 0.1344 0.1284 0.06582

0.67741935483871 0.1616 0.1552 0.1459 0.1294 0.1186 0.0654

0.709677419354839 0.16 0.1542 0.1349 0.1226 0.1175 0.06416

0.741935483870968 0.159 0.1527 0.1329 0.1198 0.1156 0.06136

0.774193548387097 0.1393 0.1334 0.1268 0.1146 0.1053 0.0555

0.806451612903226 0.1388 0.1333 0.1267 0.1116 0.1038 0.05526

0.838709677419355 0.1162 0.1124 0.108 0.1049 0.1017 0.05311

0.870967741935484 0.1152 0.1112 0.1073 0.1041 0.1005 0.05299
118

0.903225806451613 0.1137 0.1098 0.1051 0.1019 0.0987 0.05085

0.935483870967742 0.1129 0.1088 0.1032 0.09852 0.09491 0.05044

0.967741935483871 0.1073 0.1034 0.09857 0.09406 0.08995 0.04502

0.1 0.75274 0.73071 0.64394 0.48824 0.40253 0.17921

Average of yearly averages: 0.101179

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTF19GRD

Metfile: w12834.dvf

PRZM scenario: FLturfSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.029 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.029 kg/ha

Interval 2 interval 7 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.029 kg/ha

Interval 3 interval 7 days Set to 0 or delete line for single app.

app. rate 3 apprate 0.029 kg/ha

Interval 4 interval 7 days Set to 0 or delete line for single app.

app. rate 4 apprate 0.029 kg/ha

Interval 5 interval 7 days Set to 0 or delete line for single app.

app. rate 5 apprate 0.029 kg/ha

Interval 6 interval 7 days Set to 0 or delete line for single app.

app. rate 6 apprate 0.029 kg/ha

Interval 7 interval 7 days Set to 0 or delete line for single app.

app. rate 7 apprate 0.029 kg/ha

Interval 8 interval 7 days Set to 0 or delete line for single app.

app. rate 8 apprate 0.029 kg/ha

Interval 9 interval 7 days Set to 0 or delete line for single app.

app. rate 9 apprate 0.029 kg/ha

Interval 10 interval 7 days Set to 0 or delete line for single app.

app. rate 10 apprate 0.029 kg/ha

Interval 11 interval 7 days Set to 0 or delete line for single app.

app. rate 11 apprate 0.029 kg/ha

Interval 12 interval 7 days Set to 0 or delete line for single app.

app. rate 12 apprate 0.029 kg/ha

Interval 13 interval 7 days Set to 0 or delete line for single app.

app. rate 13 apprate 0.029 kg/ha

Interval 14 interval 7 days Set to 0 or delete line for single app.

app. rate 14 apprate 0.029 kg/ha

Interval 15 interval 7 days Set to 0 or delete line for single app.

app. rate 15 apprate 0.029 kg/ha

Interval 16 interval 7 days Set to 0 or delete line for single app.

app. rate 16 apprate 0.029 kg/ha

Interval 17 interval 7 days Set to 0 or delete line for single app.

app. rate 17 apprate 0.029 kg/ha

Interval 18 interval 7 days Set to 0 or delete line for single app.

app. rate 18 apprate 0.029 kg/ha

Record 17:FILTRA
119

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

GA Peach

stored as GAPEACHAIR.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt modified Tueday, 29 May 2007 at 12:54:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03813.dvf modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5362 0.5148 0.4376 0.3302 0.2745 0.09233

1962 0.8173 0.7837 0.6708 0.517 0.4537 0.1685

1963 0.5601 0.5383 0.4606 0.4085 0.3523 0.1324

1964 1.243 1.191 1.056 0.7884 0.6506 0.2286

1965 0.5353 0.5123 0.4303 0.3303 0.2811 0.111

1966 0.6999 0.6747 0.587 0.4515 0.3784 0.1355

1967 0.5879 0.5638 0.4773 0.4116 0.3565 0.1334

1968 1.116 1.071 0.9094 0.6699 0.5576 0.201

1969 0.5378 0.5173 0.4434 0.3341 0.2775 0.1066

1970 0.5252 0.5039 0.4273 0.3214 0.2674 0.09638

1971 0.7467 0.7165 0.6079 0.4684 0.3957 0.1441

1972 0.5332 0.5134 0.4417 0.3393 0.2879 0.1073

1973 0.6639 0.6385 0.5482 0.459 0.3982 0.1472

1974 0.6317 0.6073 0.5189 0.434 0.3709 0.138

1975 0.5502 0.5288 0.4597 0.3494 0.2933 0.1089

1976 2.06 1.999 1.721 1.263 1.033 0.3588

1977 0.5491 0.5269 0.4469 0.3349 0.2763 0.1149

1978 0.5308 0.5097 0.4339 0.324 0.2683 0.09541

1979 0.5631 0.5416 0.4852 0.3663 0.3074 0.1102

1980 0.5265 0.5053 0.4293 0.3206 0.2638 0.09269

1981 0.7037 0.6745 0.5702 0.4571 0.4063 0.1523

1982 0.5306 0.5085 0.4333 0.3256 0.2713 0.1018

1983 0.5239 0.5023 0.4246 0.3759 0.3276 0.1183

1984 0.6495 0.6231 0.524 0.4403 0.3783 0.137

1985 0.5266 0.5046 0.4261 0.3175 0.2627 0.09595

1986 0.5218 0.4998 0.4213 0.3122 0.2557 0.08914

1987 0.5235 0.5022 0.4319 0.3244 0.2682 0.09282

1988 0.5194 0.4963 0.414 0.3035 0.2496 0.08741

1989 0.7574 0.7261 0.6221 0.4661 0.3887 0.1362

1990 0.5269 0.5105 0.4331 0.3211 0.2637 0.09329

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.06 1.999 1.721 1.263 1.033 0.3588

0.0645161290322581 1.243 1.191 1.056 0.7884 0.6506 0.2286

0.0967741935483871 1.116 1.071 0.9094 0.6699 0.5576 0.201

0.129032258064516 0.8173 0.7837 0.6708 0.517 0.4537 0.1685

0.161290322580645 0.7574 0.7261 0.6221 0.4684 0.4063 0.1523

0.193548387096774 0.7467 0.7165 0.6079 0.4661 0.3982 0.1472

0.225806451612903 0.7037 0.6747 0.587 0.459 0.3957 0.1441

0.258064516129032 0.6999 0.6745 0.5702 0.4571 0.3887 0.138

0.290322580645161 0.6639 0.6385 0.5482 0.4515 0.3784 0.137

0.32258064516129 0.6495 0.6231 0.524 0.4403 0.3783 0.1362

0.354838709677419 0.6317 0.6073 0.5189 0.434 0.3709 0.1355

0.387096774193548 0.5879 0.5638 0.4852 0.4116 0.3565 0.1334

0.419354838709677 0.5631 0.5416 0.4773 0.4085 0.3523 0.1324

0.451612903225806 0.5601 0.5383 0.4606 0.3759 0.3276 0.1183

0.483870967741936 0.5502 0.5288 0.4597 0.3663 0.3074 0.1149

0.516129032258065 0.5491 0.5269 0.4469 0.3494 0.2933 0.111

0.548387096774194 0.5378 0.5173 0.4434 0.3393 0.2879 0.1102
120

0.580645161290323 0.5362 0.5148 0.4417 0.3349 0.2811 0.1089

0.612903225806452 0.5353 0.5134 0.4376 0.3341 0.2775 0.1073

0.645161290322581 0.5332 0.5123 0.4339 0.3303 0.2763 0.1066

0.67741935483871 0.5308 0.5105 0.4333 0.3302 0.2745 0.1018

0.709677419354839 0.5306 0.5097 0.4331 0.3256 0.2713 0.09638

0.741935483870968 0.5269 0.5085 0.4319 0.3244 0.2683 0.09595

0.774193548387097 0.5266 0.5053 0.4303 0.324 0.2682 0.09541

0.806451612903226 0.5265 0.5046 0.4293 0.3214 0.2674 0.09329

0.838709677419355 0.5252 0.5039 0.4273 0.3211 0.2638 0.09282

0.870967741935484 0.5239 0.5023 0.4261 0.3206 0.2637 0.09269

0.903225806451613 0.5235 0.5022 0.4246 0.3175 0.2627 0.09233

0.935483870967742 0.5218 0.4998 0.4213 0.3122 0.2557 0.08914

0.967741935483871 0.5194 0.4963 0.414 0.3035 0.2496 0.08741

0.1 1.08613 1.04227 0.88554 0.65461 0.54721 0.19775

Average of yearly averages: 0.130914

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHAIR

Metfile: w03813.dvf

PRZM scenario: GAPeachesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as GAPEACHGRD.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt modified Tueday, 29 May 2007 at 12:54:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03813.dvf modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1237 0.1187 0.101 0.07746 0.06444 0.02168

1962 0.5923 0.5672 0.4827 0.3521 0.2873 0.1003

1963 0.2909 0.2792 0.2375 0.1742 0.1474 0.05991

1964 0.9096 0.8712 0.7674 0.5572 0.4578 0.1582

1965 0.1179 0.1131 0.09579 0.07907 0.07049 0.03472

1966 0.3234 0.3116 0.2728 0.1993 0.1641 0.05807
121

1967 0.2504 0.2411 0.2075 0.1642 0.1473 0.05741

1968 0.7817 0.7498 0.6355 0.458 0.3742 0.13

1969 0.1171 0.1128 0.09753 0.07509 0.0631 0.03013

1970 0.1055 0.1012 0.08597 0.06548 0.05464 0.02

1971 0.3967 0.3804 0.3217 0.2332 0.1927 0.06877

1972 0.111 0.107 0.0924 0.07774 0.07032 0.03005

1973 0.399 0.3831 0.3267 0.2399 0.1969 0.07199

1974 0.3314 0.3183 0.2706 0.1976 0.1645 0.06339

1975 0.1305 0.1255 0.116 0.09091 0.07718 0.03078

1976 1.761 1.704 1.469 1.075 0.877 0.2923

1977 0.1316 0.1267 0.1091 0.08459 0.07067 0.04266

1978 0.1113 0.1069 0.09108 0.06788 0.05649 0.02066

1979 0.1777 0.1708 0.146 0.1094 0.09141 0.03265

1980 0.1064 0.1021 0.08685 0.0651 0.05372 0.01961

1981 0.4944 0.4729 0.3971 0.2837 0.2316 0.08282

1982 0.113 0.1085 0.09641 0.07473 0.06289 0.02776

1983 0.2442 0.2345 0.2007 0.1451 0.123 0.04639

1984 0.3881 0.3718 0.3108 0.2216 0.1828 0.068

1985 0.1094 0.1049 0.08892 0.06684 0.05552 0.02292

1986 0.1045 0.1001 0.08439 0.06257 0.05124 0.01797

1987 0.1047 0.1004 0.09168 0.07002 0.05858 0.02036

1988 0.1041 0.09943 0.08296 0.06083 0.05135 0.0185

1989 0.368 0.3527 0.2977 0.2195 0.1839 0.06352

1990 0.114 0.1097 0.09432 0.07011 0.05777 0.02246

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.761 1.704 1.469 1.075 0.877 0.2923

0.0645161290322581 0.9096 0.8712 0.7674 0.5572 0.4578 0.1582

0.0967741935483871 0.7817 0.7498 0.6355 0.458 0.3742 0.13

0.129032258064516 0.5923 0.5672 0.4827 0.3521 0.2873 0.1003

0.161290322580645 0.4944 0.4729 0.3971 0.2837 0.2316 0.08282

0.193548387096774 0.399 0.3831 0.3267 0.2399 0.1969 0.07199

0.225806451612903 0.3967 0.3804 0.3217 0.2332 0.1927 0.06877

0.258064516129032 0.3881 0.3718 0.3108 0.2216 0.1839 0.068

0.290322580645161 0.368 0.3527 0.2977 0.2195 0.1828 0.06352

0.32258064516129 0.3314 0.3183 0.2728 0.1993 0.1645 0.06339

0.354838709677419 0.3234 0.3116 0.2706 0.1976 0.1641 0.05991

0.387096774193548 0.2909 0.2792 0.2375 0.1742 0.1474 0.05807

0.419354838709677 0.2504 0.2411 0.2075 0.1642 0.1473 0.05741

0.451612903225806 0.2442 0.2345 0.2007 0.1451 0.123 0.04639

0.483870967741936 0.1777 0.1708 0.146 0.1094 0.09141 0.04266

0.516129032258065 0.1316 0.1267 0.116 0.09091 0.07718 0.03472

0.548387096774194 0.1305 0.1255 0.1091 0.08459 0.07067 0.03265

0.580645161290323 0.1237 0.1187 0.101 0.07907 0.07049 0.03078

0.612903225806452 0.1179 0.1131 0.09753 0.07774 0.07032 0.03013

0.645161290322581 0.1171 0.1128 0.09641 0.07746 0.06444 0.03005

0.67741935483871 0.114 0.1097 0.09579 0.07509 0.0631 0.02776

0.709677419354839 0.113 0.1085 0.09432 0.07473 0.06289 0.02292

0.741935483870968 0.1113 0.107 0.0924 0.07011 0.05858 0.02246

0.774193548387097 0.111 0.1069 0.09168 0.07002 0.05777 0.02168

0.806451612903226 0.1094 0.1049 0.09108 0.06788 0.05649 0.02066

0.838709677419355 0.1064 0.1021 0.08892 0.06684 0.05552 0.02036

0.870967741935484 0.1055 0.1012 0.08685 0.06548 0.05464 0.02

0.903225806451613 0.1047 0.1004 0.08597 0.0651 0.05372 0.01961

0.935483870967742 0.1045 0.1001 0.08439 0.06257 0.05135 0.0185

0.967741935483871 0.1041 0.09943 0.08296 0.06083 0.05124 0.01797

0.1 0.76276 0.73154 0.62022 0.44741 0.36551 0.12703

Average of yearly averages: 0.0577993333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHGRD

Metfile: w03813.dvf

PRZM scenario: GAPeachesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments
122

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

ID Potato

stored as IDPOTAIR.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:55:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24156.dvf modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5304 0.5133 0.45 0.4127 0.3814 0.151

1962 0.5702 0.5503 0.478 0.3766 0.323 0.1362

1963 0.8465 0.8218 0.7477 0.6448 0.5756 0.231

1964 0.6386 0.619 0.55 0.5136 0.4575 0.1983

1965 0.5788 0.5611 0.496 0.3932 0.3376 0.1459

1966 0.5614 0.5422 0.472 0.3978 0.3499 0.1494

1967 0.5895 0.5708 0.5245 0.4788 0.4367 0.1836

1968 0.5653 0.5465 0.4779 0.4025 0.378 0.1683

1969 0.5915 0.5711 0.4967 0.3833 0.3733 0.185

1970 1.075 1.039 0.9097 0.7119 0.6025 0.28

1971 0.9403 0.9198 0.8144 0.6616 0.5852 0.2558

1972 0.8809 0.8547 0.7477 0.5844 0.4984 0.21

1973 0.5818 0.5628 0.4929 0.3835 0.3432 0.1589

1974 1.025 0.9908 0.8625 0.7789 0.7156 0.2956

1975 0.6148 0.5966 0.534 0.5009 0.4454 0.1988

1976 1.191 1.152 1.01 0.7617 0.6662 0.2707

1977 0.6051 0.588 0.5355 0.4667 0.4416 0.2022

1978 0.671 0.6503 0.5725 0.4732 0.4507 0.1969

1979 0.5907 0.5714 0.5006 0.3926 0.3342 0.1503

1980 0.5593 0.5399 0.4689 0.3983 0.357 0.1504

1981 0.7069 0.6861 0.6112 0.5212 0.4981 0.2128

1982 0.6613 0.6392 0.5741 0.4945 0.4356 0.1937

1983 0.58 0.5617 0.4942 0.4438 0.4018 0.1786

1984 0.9759 0.9449 0.8296 0.6558 0.5806 0.2411

1985 0.9184 0.8841 0.7763 0.6105 0.5167 0.2161

1986 0.6673 0.6456 0.5844 0.4699 0.4001 0.1657

1987 0.5536 0.5326 0.4566 0.3924 0.3546 0.1486

1988 0.5537 0.5346 0.4648 0.361 0.307 0.1233

1989 0.5543 0.5346 0.4631 0.3583 0.3095 0.1258

1990 0.5543 0.5351 0.4629 0.3637 0.3309 0.139
123

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.191 1.152 1.01 0.7789 0.7156 0.2956

0.0645161290322581 1.075 1.039 0.9097 0.7617 0.6662 0.28

0.0967741935483871 1.025 0.9908 0.8625 0.7119 0.6025 0.2707

0.129032258064516 0.9759 0.9449 0.8296 0.6616 0.5852 0.2558

0.161290322580645 0.9403 0.9198 0.8144 0.6558 0.5806 0.2411

0.193548387096774 0.9184 0.8841 0.7763 0.6448 0.5756 0.231

0.225806451612903 0.8809 0.8547 0.7477 0.6105 0.5167 0.2161

0.258064516129032 0.8465 0.8218 0.7477 0.5844 0.4984 0.2128

0.290322580645161 0.7069 0.6861 0.6112 0.5212 0.4981 0.21

0.32258064516129 0.671 0.6503 0.5844 0.5136 0.4575 0.2022

0.354838709677419 0.6673 0.6456 0.5741 0.5009 0.4507 0.1988

0.387096774193548 0.6613 0.6392 0.5725 0.4945 0.4454 0.1983

0.419354838709677 0.6386 0.619 0.55 0.4788 0.4416 0.1969

0.451612903225806 0.6148 0.5966 0.5355 0.4732 0.4367 0.1937

0.483870967741936 0.6051 0.588 0.534 0.4699 0.4356 0.185

0.516129032258065 0.5915 0.5714 0.5245 0.4667 0.4018 0.1836

0.548387096774194 0.5907 0.5711 0.5006 0.4438 0.4001 0.1786

0.580645161290323 0.5895 0.5708 0.4967 0.4127 0.3814 0.1683

0.612903225806452 0.5818 0.5628 0.496 0.4025 0.378 0.1657

0.645161290322581 0.58 0.5617 0.4942 0.3983 0.3733 0.1589

0.67741935483871 0.5788 0.5611 0.4929 0.3978 0.357 0.151

0.709677419354839 0.5702 0.5503 0.478 0.3932 0.3546 0.1504

0.741935483870968 0.5653 0.5465 0.4779 0.3926 0.3499 0.1503

0.774193548387097 0.5614 0.5422 0.472 0.3924 0.3432 0.1494

0.806451612903226 0.5593 0.5399 0.4689 0.3835 0.3376 0.1486

0.838709677419355 0.5543 0.5351 0.4648 0.3833 0.3342 0.1459

0.870967741935484 0.5543 0.5346 0.4631 0.3766 0.3309 0.139

0.903225806451613 0.5537 0.5346 0.4629 0.3637 0.323 0.1362

0.935483870967742 0.5536 0.5326 0.4566 0.361 0.3095 0.1258

0.967741935483871 0.5304 0.5133 0.45 0.3583 0.307 0.1233

0.1 1.02009 0.98621 0.85921 0.70687 0.60077 0.26921

Average of yearly averages: 0.188766666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTAIR

Metfile: w24156.dvf

PRZM scenario: IDNpotato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0739 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0739 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0739 kg/ha

Record 17:FILTRA

IPSCND

UPTKF
124

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as IDPOTGRD.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:55:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24156.dvf modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3156 0.3047 0.2643 0.204 0.1704 0.06977

1962 0.1297 0.1254 0.1098 0.08802 0.07781 0.03973

1963 0.5369 0.5206 0.4815 0.3962 0.3378 0.135

1964 0.3396 0.3288 0.289 0.2314 0.2076 0.0987

1965 0.134 0.1301 0.1158 0.09306 0.08287 0.04402

1966 0.1763 0.1699 0.1468 0.1237 0.1117 0.0543

1967 0.3255 0.3145 0.2744 0.2309 0.2006 0.08584

1968 0.2231 0.2156 0.2003 0.1703 0.1445 0.07255

1969 0.3271 0.3162 0.2799 0.224 0.1867 0.08956

1970 0.8811 0.85 0.7403 0.5777 0.4803 0.1887

1971 0.6306 0.6144 0.5437 0.4194 0.3534 0.1599

1972 0.4799 0.4671 0.4086 0.3102 0.2632 0.115

1973 0.1752 0.1691 0.1511 0.1184 0.1021 0.06278

1974 0.8312 0.8024 0.6947 0.5238 0.5031 0.2068

1975 0.3296 0.3192 0.2807 0.2195 0.1975 0.1019

1976 0.9034 0.8729 0.7611 0.5684 0.474 0.1809

1977 0.3976 0.3856 0.3454 0.2731 0.2303 0.1121

1978 0.4498 0.4349 0.3793 0.2852 0.2357 0.1035

1979 0.1437 0.1394 0.1236 0.09925 0.08661 0.05064

1980 0.1708 0.1671 0.1534 0.1229 0.1119 0.05156

1981 0.4962 0.4805 0.4261 0.3222 0.2781 0.1174

1982 0.2916 0.2821 0.2473 0.217 0.1987 0.09701

1983 0.2345 0.2269 0.2115 0.1781 0.1564 0.07845

1984 0.6345 0.6138 0.5366 0.4151 0.357 0.1436

1985 0.4806 0.463 0.4286 0.3332 0.2827 0.1216

1986 0.2401 0.2326 0.2149 0.1837 0.1595 0.07051

1987 0.2261 0.2184 0.1967 0.1535 0.1295 0.06034

1988 0.1188 0.1148 0.1003 0.07867 0.07028 0.03437

1989 0.114 0.11 0.09546 0.07412 0.07115 0.03346

1990 0.1533 0.1477 0.1287 0.1073 0.0953 0.0469

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.9034 0.8729 0.7611 0.5777 0.5031 0.2068

0.0645161290322581 0.8811 0.85 0.7403 0.5684 0.4803 0.1887

0.0967741935483871 0.8312 0.8024 0.6947 0.5238 0.474 0.1809

0.129032258064516 0.6345 0.6144 0.5437 0.4194 0.357 0.1599

0.161290322580645 0.6306 0.6138 0.5366 0.4151 0.3534 0.1436

0.193548387096774 0.5369 0.5206 0.4815 0.3962 0.3378 0.135

0.225806451612903 0.4962 0.4805 0.4286 0.3332 0.2827 0.1216

0.258064516129032 0.4806 0.4671 0.4261 0.3222 0.2781 0.1174

0.290322580645161 0.4799 0.463 0.4086 0.3102 0.2632 0.115

0.32258064516129 0.4498 0.4349 0.3793 0.2852 0.2357 0.1121

0.354838709677419 0.3976 0.3856 0.3454 0.2731 0.2303 0.1035

0.387096774193548 0.3396 0.3288 0.289 0.2314 0.2076 0.1019

0.419354838709677 0.3296 0.3192 0.2807 0.2309 0.2006 0.0987

0.451612903225806 0.3271 0.3162 0.2799 0.224 0.1987 0.09701

0.483870967741936 0.3255 0.3145 0.2744 0.2195 0.1975 0.08956

0.516129032258065 0.3156 0.3047 0.2643 0.217 0.1867 0.08584

0.548387096774194 0.2916 0.2821 0.2473 0.204 0.1704 0.07845

0.580645161290323 0.2401 0.2326 0.2149 0.1837 0.1595 0.07255

0.612903225806452 0.2345 0.2269 0.2115 0.1781 0.1564 0.07051

0.645161290322581 0.2261 0.2184 0.2003 0.1703 0.1445 0.06977

0.67741935483871 0.2231 0.2156 0.1967 0.1535 0.1295 0.06278

0.709677419354839 0.1763 0.1699 0.1534 0.1237 0.1119 0.06034
125

0.741935483870968 0.1752 0.1691 0.1511 0.1229 0.1117 0.0543

0.774193548387097 0.1708 0.1671 0.1468 0.1184 0.1021 0.05156

0.806451612903226 0.1533 0.1477 0.1287 0.1073 0.0953 0.05064

0.838709677419355 0.1437 0.1394 0.1236 0.09925 0.08661 0.0469

0.870967741935484 0.134 0.1301 0.1158 0.09306 0.08287 0.04402

0.903225806451613 0.1297 0.1254 0.1098 0.08802 0.07781 0.03973

0.935483870967742 0.1188 0.1148 0.1003 0.07867 0.07115 0.03437

0.967741935483871 0.114 0.11 0.09546 0.07412 0.07028 0.03346

0.1 0.81153 0.7836 0.6796 0.51336 0.4623 0.1788

Average of yearly averages: 0.0942296666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTGRD

Metfile: w24156.dvf

PRZM scenario: IDNpotato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0739 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0739 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0739 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

MI Nursery

stored as MInursey.out

Chemical: DPXE2Y45

PRZM environment: MInurserySTD.txt modified Wedday, 24 January 2007 at 09:17:52

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14840.dvf modified Wedday, 3 July 2002 at 09:05:38

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.4 1.359 1.245 1.12 0.998 0.5059

1962 1.112 1.101 1.013 0.9055 0.8346 0.4227

1963 2.017 1.964 1.789 1.504 1.365 0.6415

1964 0.8871 0.8672 0.8182 0.7761 0.7328 0.3946

1965 1.808 1.756 1.606 1.489 1.439 0.6982

1966 1.344 1.317 1.239 1.106 1.057 0.5308

1967 1.872 1.817 1.629 1.462 1.337 0.6372
126

1968 2.569 2.524 2.332 2.094 2.023 0.9688

1969 1.953 1.9 1.76 1.538 1.386 0.6641

1970 1.498 1.456 1.37 1.152 1.035 0.5365

1971 2.139 2.095 1.983 1.579 1.355 0.6412

1972 2.247 2.186 1.983 1.753 1.638 0.8035

1973 0.8999 0.8776 0.8246 0.7579 0.7444 0.465

1974 1.227 1.191 1.103 1.027 0.9687 0.5162

1975 0.8405 0.8359 0.7927 0.6986 0.6918 0.4157

1976 3.205 3.111 2.9 2.541 2.256 0.9482

1977 2.518 2.467 2.293 2.036 1.778 0.806

1978 2.419 2.351 2.198 1.834 1.655 0.7507

1979 2.414 2.352 2.188 2.008 1.869 0.8343

1980 1.892 1.838 1.648 1.357 1.2 0.5903

1981 2.042 1.987 1.8 1.498 1.305 0.6027

1982 2.198 2.135 2.04 1.871 1.73 0.815

1983 1.354 1.317 1.26 1.161 1.087 0.5589

1984 1.08 1.065 0.99 0.9319 0.8917 0.451

1985 1.201 1.181 1.121 1.004 0.9095 0.438

1986 1.171 1.137 1.087 1.034 1.002 0.5364

1987 1.116 1.087 1.031 0.9849 0.8962 0.4686

1988 0.9865 0.9554 0.9403 0.8969 0.8511 0.4509

1989 1.536 1.489 1.334 1.159 1.092 0.6157

1990 2.042 1.98 1.793 1.531 1.486 0.761

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 3.205 3.111 2.9 2.541 2.256 0.9688

0.0645161290322581 2.569 2.524 2.332 2.094 2.023 0.9482

0.0967741935483871 2.518 2.467 2.293 2.036 1.869 0.8343

0.129032258064516 2.419 2.352 2.198 2.008 1.778 0.815

0.161290322580645 2.414 2.351 2.188 1.871 1.73 0.806

0.193548387096774 2.247 2.186 2.04 1.834 1.655 0.8035

0.225806451612903 2.198 2.135 1.983 1.753 1.638 0.761

0.258064516129032 2.139 2.095 1.983 1.579 1.486 0.7507

0.290322580645161 2.042 1.987 1.8 1.538 1.439 0.6982

0.32258064516129 2.042 1.98 1.793 1.531 1.386 0.6641

0.354838709677419 2.017 1.964 1.789 1.504 1.365 0.6415

0.387096774193548 1.953 1.9 1.76 1.498 1.355 0.6412

0.419354838709677 1.892 1.838 1.648 1.489 1.337 0.6372

0.451612903225806 1.872 1.817 1.629 1.462 1.305 0.6157

0.483870967741936 1.808 1.756 1.606 1.357 1.2 0.6027

0.516129032258065 1.536 1.489 1.37 1.161 1.092 0.5903

0.548387096774194 1.498 1.456 1.334 1.159 1.087 0.5589

0.580645161290323 1.4 1.359 1.26 1.152 1.057 0.5365

0.612903225806452 1.354 1.317 1.245 1.12 1.035 0.5364

0.645161290322581 1.344 1.317 1.239 1.106 1.002 0.5308

0.67741935483871 1.227 1.191 1.121 1.034 0.998 0.5162

0.709677419354839 1.201 1.181 1.103 1.027 0.9687 0.5059

0.741935483870968 1.171 1.137 1.087 1.004 0.9095 0.4686

0.774193548387097 1.116 1.101 1.031 0.9849 0.8962 0.465

0.806451612903226 1.112 1.087 1.013 0.9319 0.8917 0.451

0.838709677419355 1.08 1.065 0.99 0.9055 0.8511 0.4509

0.870967741935484 0.9865 0.9554 0.9403 0.8969 0.8346 0.438

0.903225806451613 0.8999 0.8776 0.8246 0.7761 0.7444 0.4227

0.935483870967742 0.8871 0.8672 0.8182 0.7579 0.7328 0.4157

0.967741935483871 0.8405 0.8359 0.7927 0.6986 0.6918 0.3946

0.1 2.5081 2.4555 2.2835 2.0332 1.8599 0.83237

Average of yearly averages: 0.615653333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MInursey

Metfile: w14840.dvf

PRZM scenario: MInurserySTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol
127

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.5591 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval days Set to 0 or delete line for single app.

app. rate 1 apprate kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

MI Cherry

stored as MICHEAIR.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt modified Tueday, 29 May 2007 at 12:56:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14850.dvf modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5214 0.5033 0.4371 0.337 0.2905 0.1312

1962 0.6797 0.6581 0.5834 0.4971 0.4706 0.2338

1963 1.538 1.491 1.315 1.016 0.8609 0.3735

1964 0.6957 0.673 0.5898 0.4664 0.4356 0.2663

1965 0.6271 0.6072 0.5341 0.4273 0.3732 0.2176

1966 0.5993 0.5798 0.5084 0.3996 0.3447 0.2157

1967 0.7109 0.6878 0.6175 0.5089 0.4501 0.233

1968 0.587 0.5686 0.5006 0.405 0.3731 0.1892

1969 0.9807 0.9506 0.909 0.764 0.6584 0.3172

1970 0.665 0.6461 0.5759 0.4663 0.4101 0.2581

1971 0.6362 0.6155 0.5395 0.4281 0.37 0.2123

1972 0.6119 0.5912 0.5508 0.4466 0.4335 0.2369

1973 0.6115 0.5933 0.5266 0.4309 0.3913 0.2073

1974 0.6817 0.662 0.5936 0.5619 0.5057 0.2408

1975 0.6328 0.6116 0.5341 0.4601 0.402 0.232

1976 0.6129 0.5932 0.5208 0.4163 0.3562 0.199

1977 0.5765 0.5556 0.4797 0.4126 0.3668 0.202

1978 1.038 1.003 0.8867 0.7043 0.6067 0.2901

1979 0.7979 0.7737 0.6847 0.5705 0.5087 0.2772

1980 0.6363 0.6158 0.5406 0.4621 0.4219 0.2251

1981 0.7418 0.719 0.6526 0.5425 0.5071 0.2895

1982 1.005 0.9792 0.863 0.6746 0.582 0.3573

1983 0.9216 0.8943 0.8224 0.6703 0.6074 0.3286

1984 0.6535 0.6338 0.5614 0.4665 0.4133 0.2382

1985 0.8418 0.8134 0.7132 0.6115 0.549 0.314

1986 1.316 1.274 1.199 0.9566 0.8355 0.4567

1987 0.8883 0.8621 0.77 0.65 0.5824 0.3953

1988 0.7262 0.7025 0.6155 0.4908 0.435 0.2795

1989 0.9254 0.8971 0.7916 0.6856 0.625 0.3004

1990 0.6201 0.6097 0.5438 0.4931 0.4712 0.2556
128

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.538 1.491 1.315 1.016 0.8609 0.4567

0.0645161290322581 1.316 1.274 1.199 0.9566 0.8355 0.3953

0.0967741935483871 1.038 1.003 0.909 0.764 0.6584 0.3735

0.129032258064516 1.005 0.9792 0.8867 0.7043 0.625 0.3573

0.161290322580645 0.9807 0.9506 0.863 0.6856 0.6074 0.3286

0.193548387096774 0.9254 0.8971 0.8224 0.6746 0.6067 0.3172

0.225806451612903 0.9216 0.8943 0.7916 0.6703 0.5824 0.314

0.258064516129032 0.8883 0.8621 0.77 0.65 0.582 0.3004

0.290322580645161 0.8418 0.8134 0.7132 0.6115 0.549 0.2901

0.32258064516129 0.7979 0.7737 0.6847 0.5705 0.5087 0.2895

0.354838709677419 0.7418 0.719 0.6526 0.5619 0.5071 0.2795

0.387096774193548 0.7262 0.7025 0.6175 0.5425 0.5057 0.2772

0.419354838709677 0.7109 0.6878 0.6155 0.5089 0.4712 0.2663

0.451612903225806 0.6957 0.673 0.5936 0.4971 0.4706 0.2581

0.483870967741936 0.6817 0.662 0.5898 0.4931 0.4501 0.2556

0.516129032258065 0.6797 0.6581 0.5834 0.4908 0.4356 0.2408

0.548387096774194 0.665 0.6461 0.5759 0.4665 0.435 0.2382

0.580645161290323 0.6535 0.6338 0.5614 0.4664 0.4335 0.2369

0.612903225806452 0.6363 0.6158 0.5508 0.4663 0.4219 0.2338

0.645161290322581 0.6362 0.6155 0.5438 0.4621 0.4133 0.233

0.67741935483871 0.6328 0.6116 0.5406 0.4601 0.4101 0.232

0.709677419354839 0.6271 0.6097 0.5395 0.4466 0.402 0.2251

0.741935483870968 0.6201 0.6072 0.5341 0.4309 0.3913 0.2176

0.774193548387097 0.6129 0.5933 0.5341 0.4281 0.3732 0.2157

0.806451612903226 0.6119 0.5932 0.5266 0.4273 0.3731 0.2123

0.838709677419355 0.6115 0.5912 0.5208 0.4163 0.37 0.2073

0.870967741935484 0.5993 0.5798 0.5084 0.4126 0.3668 0.202

0.903225806451613 0.587 0.5686 0.5006 0.405 0.3562 0.199

0.935483870967742 0.5765 0.5556 0.4797 0.3996 0.3447 0.1892

0.967741935483871 0.5214 0.5033 0.4371 0.337 0.2905 0.1312

0.1 1.0347 1.00062 0.90677 0.75803 0.65506 0.37188

Average of yearly averages: 0.26578

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEAIR

Metfile: w14850.dvf

PRZM scenario: MICherriesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5
129

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as MICHEGRD.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt modified Tueday, 29 May 2007 at 12:56:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14850.dvf modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1449 0.1404 0.1255 0.102 0.08956 0.04741

1962 0.4561 0.4406 0.3859 0.3001 0.2565 0.1268

1963 1.139 1.105 0.9766 0.7572 0.6412 0.2711

1964 0.3433 0.3322 0.2913 0.2471 0.2171 0.1612

1965 0.1739 0.169 0.1508 0.1332 0.1262 0.1071

1966 0.2367 0.2296 0.2029 0.1769 0.161 0.1095

1967 0.2875 0.2787 0.2463 0.2215 0.1992 0.1239

1968 0.1703 0.165 0.1457 0.1342 0.1208 0.07815

1969 0.7821 0.7579 0.699 0.5984 0.5072 0.2087

1970 0.2381 0.2319 0.2084 0.192 0.1721 0.1465

1971 0.1832 0.178 0.1585 0.1313 0.1237 0.1022

1972 0.3404 0.3294 0.3069 0.2488 0.2173 0.1278

1973 0.1699 0.1649 0.151 0.1324 0.1313 0.09379

1974 0.4152 0.403 0.3546 0.2874 0.2608 0.128

1975 0.3182 0.3092 0.2847 0.2327 0.2011 0.1274

1976 0.1706 0.1651 0.1464 0.1263 0.1107 0.09531

1977 0.2094 0.2027 0.1795 0.1596 0.1455 0.09916

1978 0.651 0.6291 0.5542 0.4389 0.3768 0.1839

1979 0.3494 0.3395 0.3076 0.2743 0.2532 0.1656

1980 0.2581 0.2504 0.2216 0.1755 0.166 0.1107

1981 0.5131 0.4964 0.4534 0.3848 0.3711 0.1836

1982 0.8733 0.8483 0.7433 0.5732 0.4911 0.2507

1983 0.4883 0.4747 0.4545 0.3886 0.3726 0.2286

1984 0.2015 0.1963 0.177 0.1668 0.157 0.1286

1985 0.7262 0.7002 0.6086 0.5243 0.4716 0.2113

1986 1.128 1.104 1.036 0.8254 0.7071 0.3587

1987 0.81 0.785 0.6966 0.5774 0.5092 0.2983

1988 0.2815 0.2738 0.266 0.2656 0.2651 0.1792

1989 0.7006 0.6781 0.5949 0.4894 0.4234 0.1947

1990 0.3838 0.3721 0.3504 0.2807 0.2461 0.1479

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.139 1.105 1.036 0.8254 0.7071 0.3587

0.0645161290322581 1.128 1.104 0.9766 0.7572 0.6412 0.2983

0.0967741935483871 0.8733 0.8483 0.7433 0.5984 0.5092 0.2711

0.129032258064516 0.81 0.785 0.699 0.5774 0.5072 0.2507

0.161290322580645 0.7821 0.7579 0.6966 0.5732 0.4911 0.2286

0.193548387096774 0.7262 0.7002 0.6086 0.5243 0.4716 0.2113

0.225806451612903 0.7006 0.6781 0.5949 0.4894 0.4234 0.2087

0.258064516129032 0.651 0.6291 0.5542 0.4389 0.3768 0.1947

0.290322580645161 0.5131 0.4964 0.4545 0.3886 0.3726 0.1839

0.32258064516129 0.4883 0.4747 0.4534 0.3848 0.3711 0.1836

0.354838709677419 0.4561 0.4406 0.3859 0.3001 0.2651 0.1792

0.387096774193548 0.4152 0.403 0.3546 0.2874 0.2608 0.1656

0.419354838709677 0.3838 0.3721 0.3504 0.2807 0.2565 0.1612

0.451612903225806 0.3494 0.3395 0.3076 0.2743 0.2532 0.1479

0.483870967741936 0.3433 0.3322 0.3069 0.2656 0.2461 0.1465

0.516129032258065 0.3404 0.3294 0.2913 0.2488 0.2173 0.1286

0.548387096774194 0.3182 0.3092 0.2847 0.2471 0.2171 0.128

0.580645161290323 0.2875 0.2787 0.266 0.2327 0.2011 0.1278

0.612903225806452 0.2815 0.2738 0.2463 0.2215 0.1992 0.1274

0.645161290322581 0.2581 0.2504 0.2216 0.192 0.1721 0.1268

0.67741935483871 0.2381 0.2319 0.2084 0.1769 0.166 0.1239

0.709677419354839 0.2367 0.2296 0.2029 0.1755 0.161 0.1107

0.741935483870968 0.2094 0.2027 0.1795 0.1668 0.157 0.1095

0.774193548387097 0.2015 0.1963 0.177 0.1596 0.1455 0.1071

0.806451612903226 0.1832 0.178 0.1585 0.1342 0.1313 0.1022

0.838709677419355 0.1739 0.169 0.151 0.1332 0.1262 0.09916

0.870967741935484 0.1706 0.1651 0.1508 0.1324 0.1237 0.09531
130

0.903225806451613 0.1703 0.165 0.1464 0.1313 0.1208 0.09379

0.935483870967742 0.1699 0.1649 0.1457 0.1263 0.1107 0.07815

0.967741935483871 0.1449 0.1404 0.1255 0.102 0.08956 0.04741

0.1 0.86697 0.84197 0.73887 0.5963 0.509 0.26906

Average of yearly averages: 0.159860666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEGRD

Metfile: w14850.dvf

PRZM scenario: MICherriesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

MS Cotton

stored as MSCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt modified Tueday, 29 May 2007 at 12:57:52

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03940.dvf modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.974 1.892 1.597 1.282 1.124 0.4016

1962 0.6839 0.6537 0.5466 0.4961 0.4313 0.1991

1963 2.242 2.155 1.842 1.43 1.222 0.4955

1964 0.8521 0.8184 0.6968 0.6228 0.5736 0.2732

1965 0.5559 0.5334 0.4527 0.3884 0.3425 0.1576

1966 3.755 3.682 3.281 2.392 1.951 0.679

1967 3.374 3.242 2.836 2.418 2.076 0.786

1968 2.232 2.143 2.01 1.541 1.273 0.4852

1969 0.7063 0.6781 0.5848 0.4717 0.4321 0.203

1970 1.003 0.963 0.8314 0.7401 0.6385 0.253

1971 3.051 2.926 2.503 1.85 1.523 0.5344

1972 1.992 1.941 1.761 1.389 1.174 0.4367

1973 2.094 2.009 1.771 1.397 1.16 0.4259

1974 1.434 1.376 1.166 0.8785 0.7808 0.3225
131

1975 2.872 2.777 2.608 2.037 1.701 0.6114

1976 4.097 3.942 3.604 2.908 2.451 0.8715

1977 1.092 1.056 0.9396 0.8405 0.7855 0.3857

1978 3.476 3.347 3.179 2.435 2 0.7046

1979 2.947 2.83 2.444 2.276 2.087 0.8059

1980 2.573 2.483 2.249 1.66 1.405 0.5311

1981 2.282 2.193 2.018 1.553 1.283 0.4709

1982 3.032 2.907 2.494 1.948 1.611 0.5997

1983 5.422 5.251 4.533 3.486 2.873 1.014

1984 1.596 1.548 1.407 1.22 1.06 0.4402

1985 0.5903 0.5693 0.5159 0.4673 0.434 0.2266

1986 2.536 2.439 2.162 1.654 1.369 0.4917

1987 1.525 1.467 1.296 1.144 1.034 0.409

1988 0.7223 0.695 0.6052 0.518 0.5002 0.2734

1989 3.771 3.636 3.175 2.655 2.314 0.8542

1990 3.008 2.896 2.568 1.99 1.641 0.608

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 5.422 5.251 4.533 3.486 2.873 1.014

0.0645161290322581 4.097 3.942 3.604 2.908 2.451 0.8715

0.0967741935483871 3.771 3.682 3.281 2.655 2.314 0.8542

0.129032258064516 3.755 3.636 3.179 2.435 2.087 0.8059

0.161290322580645 3.476 3.347 3.175 2.418 2.076 0.786

0.193548387096774 3.374 3.242 2.836 2.392 2 0.7046

0.225806451612903 3.051 2.926 2.608 2.276 1.951 0.679

0.258064516129032 3.032 2.907 2.568 2.037 1.701 0.6114

0.290322580645161 3.008 2.896 2.503 1.99 1.641 0.608

0.32258064516129 2.947 2.83 2.494 1.948 1.611 0.5997

0.354838709677419 2.872 2.777 2.444 1.85 1.523 0.5344

0.387096774193548 2.573 2.483 2.249 1.66 1.405 0.5311

0.419354838709677 2.536 2.439 2.162 1.654 1.369 0.4955

0.451612903225806 2.282 2.193 2.018 1.553 1.283 0.4917

0.483870967741936 2.242 2.155 2.01 1.541 1.273 0.4852

0.516129032258065 2.232 2.143 1.842 1.43 1.222 0.4709

0.548387096774194 2.094 2.009 1.771 1.397 1.174 0.4402

0.580645161290323 1.992 1.941 1.761 1.389 1.16 0.4367

0.612903225806452 1.974 1.892 1.597 1.282 1.124 0.4259

0.645161290322581 1.596 1.548 1.407 1.22 1.06 0.409

0.67741935483871 1.525 1.467 1.296 1.144 1.034 0.4016

0.709677419354839 1.434 1.376 1.166 0.8785 0.7855 0.3857

0.741935483870968 1.092 1.056 0.9396 0.8405 0.7808 0.3225

0.774193548387097 1.003 0.963 0.8314 0.7401 0.6385 0.2734

0.806451612903226 0.8521 0.8184 0.6968 0.6228 0.5736 0.2732

0.838709677419355 0.7223 0.695 0.6052 0.518 0.5002 0.253

0.870967741935484 0.7063 0.6781 0.5848 0.4961 0.434 0.2266

0.903225806451613 0.6839 0.6537 0.5466 0.4717 0.4321 0.203

0.935483870967742 0.5903 0.5693 0.5159 0.4673 0.4313 0.1991

0.967741935483871 0.5559 0.5334 0.4527 0.3884 0.3425 0.1576

0.1 3.7694 3.6774 3.2708 2.633 2.2913 0.84937

Average of yearly averages: 0.498353333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTAIR

Metfile: w03940.dvf

PRZM scenario: MScottonSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife
132

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as MSCOTGRD.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt modified Tueday, 29 May 2007 at 12:57:52

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03940.dvf modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.634 1.566 1.323 1.087 0.9672 0.345

1962 0.3592 0.3466 0.3197 0.2576 0.2373 0.1339

1963 2.2 2.113 1.802 1.371 1.174 0.4407

1964 0.6208 0.5958 0.5266 0.485 0.4373 0.2082

1965 0.1979 0.1905 0.1722 0.1511 0.1367 0.08604

1966 3.575 3.511 3.128 2.279 1.858 0.6273

1967 3.187 3.062 2.686 2.256 1.942 0.7394

1968 1.927 1.851 1.762 1.36 1.125 0.4268

1969 0.3049 0.2933 0.2612 0.2389 0.24 0.1344

1970 0.6731 0.6555 0.5637 0.5025 0.4445 0.1851

1971 2.784 2.669 2.273 1.682 1.384 0.4784

1972 1.696 1.642 1.478 1.179 1.002 0.3773

1973 1.743 1.672 1.49 1.198 0.9964 0.3659

1974 1.242 1.191 1.007 0.7292 0.6122 0.2572

1975 2.598 2.503 2.348 1.854 1.553 0.5566

1976 3.885 3.738 3.439 2.767 2.339 0.8294

1977 1.007 0.9736 0.8662 0.7289 0.696 0.3256

1978 3.262 3.141 2.952 2.278 1.872 0.6575

1979 2.818 2.706 2.302 2.104 1.954 0.7615

1980 2.312 2.232 2.039 1.505 1.243 0.4777

1981 2.03 1.95 1.809 1.403 1.161 0.4131

1982 2.959 2.836 2.431 1.902 1.572 0.5478

1983 5.317 5.145 4.443 3.403 2.805 0.978

1984 1.247 1.2 1.112 1.009 0.891 0.3829

1985 0.4844 0.4663 0.4247 0.3678 0.3452 0.1587

1986 2.355 2.265 1.997 1.507 1.25 0.4336

1987 1.271 1.225 1.085 0.9272 0.8582 0.3467

1988 0.6819 0.6553 0.5685 0.4838 0.4526 0.2101

1989 3.572 3.445 3.011 2.49 2.182 0.8071

1990 2.733 2.631 2.344 1.833 1.513 0.555

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 5.317 5.145 4.443 3.403 2.805 0.978

0.0645161290322581 3.885 3.738 3.439 2.767 2.339 0.8294

0.0967741935483871 3.575 3.511 3.128 2.49 2.182 0.8071

0.129032258064516 3.572 3.445 3.011 2.279 1.954 0.7615

0.161290322580645 3.262 3.141 2.952 2.278 1.942 0.7394

0.193548387096774 3.187 3.062 2.686 2.256 1.872 0.6575

0.225806451612903 2.959 2.836 2.431 2.104 1.858 0.6273

0.258064516129032 2.818 2.706 2.348 1.902 1.572 0.5566

0.290322580645161 2.784 2.669 2.344 1.854 1.553 0.555
133

0.32258064516129 2.733 2.631 2.302 1.833 1.513 0.5478

0.354838709677419 2.598 2.503 2.273 1.682 1.384 0.4784

0.387096774193548 2.355 2.265 2.039 1.507 1.25 0.4777

0.419354838709677 2.312 2.232 1.997 1.505 1.243 0.4407

0.451612903225806 2.2 2.113 1.809 1.403 1.174 0.4336

0.483870967741936 2.03 1.95 1.802 1.371 1.161 0.4268

0.516129032258065 1.927 1.851 1.762 1.36 1.125 0.4131

0.548387096774194 1.743 1.672 1.49 1.198 1.002 0.3829

0.580645161290323 1.696 1.642 1.478 1.179 0.9964 0.3773

0.612903225806452 1.634 1.566 1.323 1.087 0.9672 0.3659

0.645161290322581 1.271 1.225 1.112 1.009 0.891 0.3467

0.67741935483871 1.247 1.2 1.085 0.9272 0.8582 0.345

0.709677419354839 1.242 1.191 1.007 0.7292 0.696 0.3256

0.741935483870968 1.007 0.9736 0.8662 0.7289 0.6122 0.2572

0.774193548387097 0.6819 0.6555 0.5685 0.5025 0.4526 0.2101

0.806451612903226 0.6731 0.6553 0.5637 0.485 0.4445 0.2082

0.838709677419355 0.6208 0.5958 0.5266 0.4838 0.4373 0.1851

0.870967741935484 0.4844 0.4663 0.4247 0.3678 0.3452 0.1587

0.903225806451613 0.3592 0.3466 0.3197 0.2576 0.24 0.1344

0.935483870967742 0.3049 0.2933 0.2612 0.2389 0.2373 0.1339

0.967741935483871 0.1979 0.1905 0.1722 0.1511 0.1367 0.08604

0.1 3.5747 3.5044 3.1163 2.4689 2.1592 0.80254

Average of yearly averages: 0.441564666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTGRD

Metfile: w03940.dvf

PRZM scenario: MScottonSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

NY Grape

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt modified Tueday, 29 May 2007 at 12:59:44

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30
134

Metfile: w14860.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.6227 0.601 0.522 0.4139 0.3586 0.1378

1962 1.601 1.553 1.413 1.127 1.042 0.467

1963 0.6865 0.6628 0.5766 0.475 0.4419 0.3278

1964 0.965 0.9339 0.8196 0.6472 0.583 0.3334

1965 0.7813 0.755 0.659 0.5772 0.5281 0.3087

1966 0.9513 0.9191 0.8551 0.6759 0.6125 0.3121

1967 1.391 1.347 1.198 0.9476 0.8383 0.4086

1968 0.6522 0.6315 0.5555 0.4478 0.3968 0.2587

1969 0.6483 0.628 0.5592 0.4722 0.4114 0.2128

1970 1.017 0.985 0.9071 0.7132 0.6446 0.3366

1971 0.7442 0.7217 0.6374 0.5544 0.5379 0.3441

1972 1.237 1.204 1.108 0.9193 0.8092 0.3947

1973 1.366 1.326 1.184 0.9757 0.8576 0.4227

1974 1.185 1.152 1.006 0.8182 0.7407 0.4068

1975 0.9142 0.8853 0.7819 0.6567 0.6344 0.4152

1976 0.7971 0.779 0.6907 0.6084 0.5495 0.3153

1977 0.8011 0.7746 0.6806 0.6506 0.6132 0.3332

1978 0.6798 0.659 0.6045 0.5284 0.4883 0.341

1979 0.8796 0.8525 0.7577 0.7281 0.6956 0.4361

1980 1.261 1.227 1.101 1.048 1.033 0.5739

1981 0.7703 0.7468 0.6927 0.6054 0.5599 0.3845

1982 1.231 1.197 1.07 0.8891 0.7937 0.386

1983 1.055 1.02 0.9309 0.8751 0.7917 0.4202

1984 1.225 1.188 1.06 0.839 0.7409 0.4251

1985 1.121 1.087 0.9643 0.8622 0.7647 0.4021

1986 1.826 1.774 1.593 1.272 1.102 0.5831

1987 0.8003 0.7751 0.707 0.6372 0.6114 0.3996

1988 0.6041 0.5815 0.4996 0.4028 0.3979 0.2646

1989 1.028 1.002 0.8867 0.7151 0.634 0.3272

1990 0.6992 0.6816 0.6521 0.5471 0.4814 0.2981

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.826 1.774 1.593 1.272 1.102 0.5831

0.0645161290322581 1.601 1.553 1.413 1.127 1.042 0.5739

0.0967741935483871 1.391 1.347 1.198 1.048 1.033 0.467

0.129032258064516 1.366 1.326 1.184 0.9757 0.8576 0.4361

0.161290322580645 1.261 1.227 1.108 0.9476 0.8383 0.4251

0.193548387096774 1.237 1.204 1.101 0.9193 0.8092 0.4227

0.225806451612903 1.231 1.197 1.07 0.8891 0.7937 0.4202

0.258064516129032 1.225 1.188 1.06 0.8751 0.7917 0.4152

0.290322580645161 1.185 1.152 1.006 0.8622 0.7647 0.4086

0.32258064516129 1.121 1.087 0.9643 0.839 0.7409 0.4068

0.354838709677419 1.055 1.02 0.9309 0.8182 0.7407 0.4021

0.387096774193548 1.028 1.002 0.9071 0.7281 0.6956 0.3996

0.419354838709677 1.017 0.985 0.8867 0.7151 0.6446 0.3947

0.451612903225806 0.965 0.9339 0.8551 0.7132 0.6344 0.386

0.483870967741936 0.9513 0.9191 0.8196 0.6759 0.634 0.3845

0.516129032258065 0.9142 0.8853 0.7819 0.6567 0.6132 0.3441

0.548387096774194 0.8796 0.8525 0.7577 0.6506 0.6125 0.341

0.580645161290323 0.8011 0.779 0.707 0.6472 0.6114 0.3366

0.612903225806452 0.8003 0.7751 0.6927 0.6372 0.583 0.3334

0.645161290322581 0.7971 0.7746 0.6907 0.6084 0.5599 0.3332

0.67741935483871 0.7813 0.755 0.6806 0.6054 0.5495 0.3278

0.709677419354839 0.7703 0.7468 0.659 0.5772 0.5379 0.3272

0.741935483870968 0.7442 0.7217 0.6521 0.5544 0.5281 0.3153

0.774193548387097 0.6992 0.6816 0.6374 0.5471 0.4883 0.3121

0.806451612903226 0.6865 0.6628 0.6045 0.5284 0.4814 0.3087

0.838709677419355 0.6798 0.659 0.5766 0.475 0.4419 0.2981

0.870967741935484 0.6522 0.6315 0.5592 0.4722 0.4114 0.2646

0.903225806451613 0.6483 0.628 0.5555 0.4478 0.3979 0.2587

0.935483870967742 0.6227 0.601 0.522 0.4139 0.3968 0.2128

0.967741935483871 0.6041 0.5815 0.4996 0.4028 0.3586 0.1378

0.1 1.3885 1.3449 1.1966 1.04077 1.01546 0.46391

Average of yearly averages: 0.3659
135

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile: w14860.dvf

PRZM scenario: NYGrapesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-6 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as CACOTGRD.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt modified Tueday, 29 May 2007 at 12:59:44

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14860.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.2116 0.2052 0.1819 0.1552 0.1404 0.06229

1962 1.252 1.215 1.107 0.9013 0.8587 0.3821

1963 0.3809 0.3809 0.3808 0.379 0.3624 0.2357

1964 0.8258 0.798 0.6966 0.5351 0.463 0.242

1965 0.5476 0.5289 0.4604 0.3654 0.322 0.2148

1966 0.6023 0.5836 0.5247 0.432 0.4124 0.2244

1967 1.196 1.158 1.03 0.816 0.7059 0.3256

1968 0.2714 0.2713 0.2703 0.2661 0.2557 0.1628

1969 0.226 0.2209 0.1976 0.1817 0.1648 0.1035

1970 0.7995 0.7732 0.7189 0.5652 0.5085 0.2292

1971 0.5538 0.5365 0.4723 0.3845 0.3437 0.2397

1972 0.9302 0.9037 0.835 0.6958 0.6025 0.2942

1973 0.9965 0.97 0.8706 0.7173 0.641 0.3275

1974 0.9102 0.886 0.7753 0.6127 0.5532 0.31

1975 0.6902 0.67 0.6174 0.5014 0.4652 0.3159

1976 0.5196 0.5097 0.4539 0.3837 0.3386 0.2193

1977 0.5921 0.5838 0.5487 0.4894 0.4522 0.2351

1978 0.5146 0.4981 0.4605 0.4139 0.3852 0.2377

1979 0.8021 0.7765 0.6855 0.6144 0.5992 0.3416

1980 1.126 1.096 0.9816 0.8966 0.831 0.4865

1981 0.4403 0.428 0.4105 0.4083 0.3899 0.2872

1982 0.8759 0.8539 0.7697 0.6385 0.5766 0.2893

1983 0.8861 0.8583 0.808 0.7118 0.6563 0.3349

1984 0.8871 0.8623 0.7791 0.624 0.5614 0.3368
136

1985 0.7437 0.7233 0.6701 0.6263 0.5647 0.3138

1986 1.471 1.432 1.29 1.045 0.9048 0.4954

1987 0.5436 0.5276 0.4709 0.4313 0.4072 0.3116

1988 0.3362 0.325 0.2944 0.2721 0.2579 0.1751

1989 0.699 0.6842 0.6095 0.4778 0.4307 0.2366

1990 0.6079 0.5908 0.5591 0.4688 0.4051 0.2067

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.471 1.432 1.29 1.045 0.9048 0.4954

0.0645161290322581 1.252 1.215 1.107 0.9013 0.8587 0.4865

0.0967741935483871 1.196 1.158 1.03 0.8966 0.831 0.3821

0.129032258064516 1.126 1.096 0.9816 0.816 0.7059 0.3416

0.161290322580645 0.9965 0.97 0.8706 0.7173 0.6563 0.3368

0.193548387096774 0.9302 0.9037 0.835 0.7118 0.641 0.3349

0.225806451612903 0.9102 0.886 0.808 0.6958 0.6025 0.3275

0.258064516129032 0.8871 0.8623 0.7791 0.6385 0.5992 0.3256

0.290322580645161 0.8861 0.8583 0.7753 0.6263 0.5766 0.3159

0.32258064516129 0.8759 0.8539 0.7697 0.624 0.5647 0.3138

0.354838709677419 0.8258 0.798 0.7189 0.6144 0.5614 0.3116

0.387096774193548 0.8021 0.7765 0.6966 0.6127 0.5532 0.31

0.419354838709677 0.7995 0.7732 0.6855 0.5652 0.5085 0.2942

0.451612903225806 0.7437 0.7233 0.6701 0.5351 0.4652 0.2893

0.483870967741936 0.699 0.6842 0.6174 0.5014 0.463 0.2872

0.516129032258065 0.6902 0.67 0.6095 0.4894 0.4522 0.242

0.548387096774194 0.6079 0.5908 0.5591 0.4778 0.4307 0.2397

0.580645161290323 0.6023 0.5838 0.5487 0.4688 0.4124 0.2377

0.612903225806452 0.5921 0.5836 0.5247 0.432 0.4072 0.2366

0.645161290322581 0.5538 0.5365 0.4723 0.4313 0.4051 0.2357

0.67741935483871 0.5476 0.5289 0.4709 0.4139 0.3899 0.2351

0.709677419354839 0.5436 0.5276 0.4605 0.4083 0.3852 0.2292

0.741935483870968 0.5196 0.5097 0.4604 0.3845 0.3624 0.2244

0.774193548387097 0.5146 0.4981 0.4539 0.3837 0.3437 0.2193

0.806451612903226 0.4403 0.428 0.4105 0.379 0.3386 0.2148

0.838709677419355 0.3809 0.3809 0.3808 0.3654 0.322 0.2067

0.870967741935484 0.3362 0.325 0.2944 0.2721 0.2579 0.1751

0.903225806451613 0.2714 0.2713 0.2703 0.2661 0.2557 0.1628

0.935483870967742 0.226 0.2209 0.1976 0.1817 0.1648 0.1035

0.967741935483871 0.2116 0.2052 0.1819 0.1552 0.1404 0.06229

0.1 1.189 1.1518 1.02516 0.88854 0.81849 0.37805

Average of yearly averages: 0.272576333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTGRD

Metfile: w14860.dvf

PRZM scenario: NYGrapesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-6 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.
137

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

OR Apple

stored as ORAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt modified Tueday, 29 May 2007 at 13:00:08

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24232.dvf modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5132 0.4972 0.4627 0.4047 0.353 0.1386

1962 0.6215 0.6032 0.5428 0.4781 0.42 0.1917

1963 1.02 0.9866 0.8716 0.6926 0.6318 0.2926

1964 0.5819 0.5645 0.5003 0.4024 0.3528 0.1865

1965 0.5918 0.581 0.5494 0.446 0.3906 0.2005

1966 0.5788 0.5601 0.4917 0.3907 0.3381 0.1861

1967 0.605 0.5871 0.5211 0.4213 0.3665 0.19

1968 0.5624 0.5447 0.4798 0.39 0.3533 0.1867

1969 0.5621 0.5456 0.4852 0.3856 0.3416 0.1958

1970 0.5729 0.5563 0.4948 0.3944 0.3417 0.1629

1971 1.021 0.9898 0.8743 0.6911 0.5961 0.2761

1972 0.6404 0.6238 0.5554 0.4741 0.4248 0.2025

1973 0.5686 0.5504 0.4839 0.3842 0.3336 0.1617

1974 0.556 0.5397 0.4794 0.3838 0.3346 0.1889

1975 0.6318 0.6137 0.5475 0.4673 0.4126 0.2204

1976 0.5588 0.5418 0.4792 0.3804 0.3304 0.1447

1977 0.5347 0.517 0.4521 0.3719 0.3309 0.1457

1978 0.6196 0.6011 0.5366 0.4837 0.4374 0.1977

1979 0.5633 0.5469 0.4862 0.4223 0.3731 0.1845

1980 0.7261 0.7028 0.6335 0.5097 0.4528 0.2097

1981 0.7922 0.768 0.6789 0.5424 0.4993 0.2495

1982 0.7236 0.7029 0.6287 0.491 0.4274 0.1934

1983 0.5745 0.5558 0.4873 0.3973 0.3496 0.1622

1984 0.7213 0.6999 0.6275 0.5595 0.5029 0.2192

1985 0.5535 0.5361 0.4719 0.3842 0.3799 0.1973

1986 0.5747 0.5574 0.495 0.4096 0.3595 0.1687

1987 0.6032 0.5839 0.5316 0.4222 0.3667 0.1951

1988 0.6195 0.6018 0.5672 0.4673 0.4147 0.2033

1989 0.5533 0.5357 0.4708 0.374 0.3246 0.1738

1990 0.6123 0.5941 0.5314 0.4379 0.3872 0.2107

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.021 0.9898 0.8743 0.6926 0.6318 0.2926

0.0645161290322581 1.02 0.9866 0.8716 0.6911 0.5961 0.2761

0.0967741935483871 0.7922 0.768 0.6789 0.5595 0.5029 0.2495

0.129032258064516 0.7261 0.7029 0.6335 0.5424 0.4993 0.2204

0.161290322580645 0.7236 0.7028 0.6287 0.5097 0.4528 0.2192

0.193548387096774 0.7213 0.6999 0.6275 0.491 0.4374 0.2107

0.225806451612903 0.6404 0.6238 0.5672 0.4837 0.4274 0.2097

0.258064516129032 0.6318 0.6137 0.5554 0.4781 0.4248 0.2033

0.290322580645161 0.6215 0.6032 0.5494 0.4741 0.42 0.2025

0.32258064516129 0.6196 0.6018 0.5475 0.4673 0.4147 0.2005

0.354838709677419 0.6195 0.6011 0.5428 0.4673 0.4126 0.1977

0.387096774193548 0.6123 0.5941 0.5366 0.446 0.3906 0.1973
138

0.419354838709677 0.605 0.5871 0.5316 0.4379 0.3872 0.1958

0.451612903225806 0.6032 0.5839 0.5314 0.4223 0.3799 0.1951

0.483870967741936 0.5918 0.581 0.5211 0.4222 0.3731 0.1934

0.516129032258065 0.5819 0.5645 0.5003 0.4213 0.3667 0.1917

0.548387096774194 0.5788 0.5601 0.495 0.4096 0.3665 0.19

0.580645161290323 0.5747 0.5574 0.4948 0.4047 0.3595 0.1889

0.612903225806452 0.5745 0.5563 0.4917 0.4024 0.3533 0.1867

0.645161290322581 0.5729 0.5558 0.4873 0.3973 0.353 0.1865

0.67741935483871 0.5686 0.5504 0.4862 0.3944 0.3528 0.1861

0.709677419354839 0.5633 0.5469 0.4852 0.3907 0.3496 0.1845

0.741935483870968 0.5624 0.5456 0.4839 0.39 0.3417 0.1738

0.774193548387097 0.5621 0.5447 0.4798 0.3856 0.3416 0.1687

0.806451612903226 0.5588 0.5418 0.4794 0.3842 0.3381 0.1629

0.838709677419355 0.556 0.5397 0.4792 0.3842 0.3346 0.1622

0.870967741935484 0.5535 0.5361 0.4719 0.3838 0.3336 0.1617

0.903225806451613 0.5533 0.5357 0.4708 0.3804 0.3309 0.1457

0.935483870967742 0.5347 0.517 0.4627 0.374 0.3304 0.1447

0.967741935483871 0.5132 0.4972 0.4521 0.3719 0.3246 0.1386

0.1 0.78559 0.76149 0.67436 0.55779 0.50254 0.24659

Average of yearly averages: 0.19455

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPAIR

Metfile: w24232.dvf

PRZM scenario: ORappleSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as ORAPPGRD.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt modified Tueday, 29 May 2007 at 13:00:08

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24232.dvf modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1958 0.1899 0.1681 0.1333 0.1174 0.04997

1962 0.2981 0.2891 0.2604 0.2071 0.1762 0.09175

1963 0.7417 0.7168 0.628 0.4889 0.4167 0.1922

1964 0.2058 0.2016 0.19 0.1584 0.1143 0.08408
139

1965 0.2241 0.2186 0.1974 0.1623 0.1435 0.1026

1966 0.2874 0.2817 0.2604 0.2042 0.1441 0.09132

1967 0.1903 0.1865 0.1719 0.1448 0.1286 0.09588

1968 0.165 0.1619 0.1439 0.1271 0.1173 0.08935

1969 0.1944 0.1887 0.1705 0.1524 0.1409 0.0961

1970 0.1466 0.1428 0.1288 0.107 0.09362 0.06485

1971 0.614 0.5952 0.5358 0.4192 0.3624 0.1793

1972 0.2641 0.2577 0.2278 0.1943 0.1816 0.1058

1973 0.1457 0.1415 0.1264 0.1044 0.09149 0.06517

1974 0.4132 0.4043 0.3692 0.3065 0.2105 0.08935

1975 0.2566 0.2515 0.2318 0.1967 0.1751 0.1241

1976 0.1336 0.1299 0.1161 0.09507 0.08319 0.0452

1977 0.1194 0.1162 0.1041 0.09271 0.08473 0.04667

1978 0.3652 0.3535 0.3115 0.2412 0.2032 0.09736

1979 0.1963 0.1911 0.1701 0.1383 0.124 0.08516

1980 0.3094 0.2997 0.2813 0.2333 0.2133 0.1123

1981 0.3766 0.3653 0.3238 0.2647 0.2635 0.1524

1982 0.3287 0.3185 0.2834 0.2214 0.19 0.09808

1983 0.1516 0.147 0.1299 0.1188 0.1075 0.06325

1984 0.3708 0.3597 0.3185 0.2781 0.2638 0.12

1985 0.3097 0.2989 0.2623 0.1966 0.1634 0.1022

1986 0.153 0.149 0.1344 0.1253 0.113 0.07091

1987 0.2705 0.2662 0.2499 0.1603 0.1279 0.1023

1988 0.2379 0.2319 0.2112 0.1826 0.1664 0.1064

1989 0.2974 0.2895 0.2603 0.2081 0.1556 0.07564

1990 0.2103 0.2058 0.1962 0.1659 0.1468 0.111

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.7417 0.7168 0.628 0.4889 0.4167 0.1922

0.0645161290322581 0.614 0.5952 0.5358 0.4192 0.3624 0.1793

0.0967741935483871 0.4132 0.4043 0.3692 0.3065 0.2638 0.1524

0.129032258064516 0.3766 0.3653 0.3238 0.2781 0.2635 0.1241

0.161290322580645 0.3708 0.3597 0.3185 0.2647 0.2133 0.12

0.193548387096774 0.3652 0.3535 0.3115 0.2412 0.2105 0.1123

0.225806451612903 0.3287 0.3185 0.2834 0.2333 0.2032 0.111

0.258064516129032 0.3097 0.2997 0.2813 0.2214 0.19 0.1064

0.290322580645161 0.3094 0.2989 0.2623 0.2081 0.1816 0.1058

0.32258064516129 0.2981 0.2895 0.2604 0.2071 0.1762 0.1026

0.354838709677419 0.2974 0.2891 0.2604 0.2042 0.1751 0.1023

0.387096774193548 0.2874 0.2817 0.2603 0.1967 0.1664 0.1022

0.419354838709677 0.2705 0.2662 0.2499 0.1966 0.1634 0.09808

0.451612903225806 0.2641 0.2577 0.2318 0.1943 0.1556 0.09736

0.483870967741936 0.2566 0.2515 0.2278 0.1826 0.1468 0.0961

0.516129032258065 0.2379 0.2319 0.2112 0.1659 0.1441 0.09588

0.548387096774194 0.2241 0.2186 0.1974 0.1623 0.1435 0.09175

0.580645161290323 0.2103 0.2058 0.1962 0.1603 0.1409 0.09132

0.612903225806452 0.2058 0.2016 0.19 0.1584 0.1286 0.08935

0.645161290322581 0.1963 0.1911 0.1719 0.1524 0.1279 0.08935

0.67741935483871 0.1958 0.1899 0.1705 0.1448 0.124 0.08516

0.709677419354839 0.1944 0.1887 0.1701 0.1383 0.1174 0.08408

0.741935483870968 0.1903 0.1865 0.1681 0.1333 0.1173 0.07564

0.774193548387097 0.165 0.1619 0.1439 0.1271 0.1143 0.07091

0.806451612903226 0.153 0.149 0.1344 0.1253 0.113 0.06517

0.838709677419355 0.1516 0.147 0.1299 0.1188 0.1075 0.06485

0.870967741935484 0.1466 0.1428 0.1288 0.107 0.09362 0.06325

0.903225806451613 0.1457 0.1415 0.1264 0.1044 0.09149 0.04997

0.935483870967742 0.1336 0.1299 0.1161 0.09507 0.08473 0.04667

0.967741935483871 0.1194 0.1162 0.1041 0.09271 0.08319 0.0452

0.1 0.40954 0.4004 0.36466 0.30366 0.26377 0.14957

Average of yearly averages: 0.097023

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPGRD

Metfile: w24232.dvf

PRZM scenario: ORappleSTD.txt

EXAMS environment file: pond298.exv
140

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

PA Apple

stored as PAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5156 0.4987 0.4348 0.3375 0.2992 0.1616

1962 0.5648 0.546 0.4811 0.3868 0.3526 0.1682

1963 0.5472 0.5276 0.4556 0.3622 0.3158 0.1411

1964 0.6947 0.6698 0.5816 0.4784 0.4227 0.1836

1965 0.5501 0.5324 0.4729 0.3769 0.3326 0.147

1966 0.7679 0.7417 0.6486 0.4962 0.421 0.2388

1967 0.7069 0.6845 0.619 0.5151 0.4586 0.2369

1968 1.233 1.204 1.054 0.8052 0.7347 0.3127

1969 0.688 0.6662 0.6033 0.4594 0.3863 0.2459

1970 0.5955 0.5758 0.5112 0.409 0.382 0.1931

1971 0.6312 0.6108 0.5381 0.4678 0.407 0.1741

1972 0.7282 0.7067 0.628 0.5435 0.5398 0.2454

1973 0.7558 0.7339 0.6462 0.6022 0.5366 0.2329

1974 0.9022 0.8716 0.7651 0.6056 0.5469 0.2409

1975 1.024 0.9905 0.8854 0.7366 0.6485 0.2689

1976 0.6597 0.6403 0.5938 0.5187 0.4618 0.207

1977 0.6427 0.6197 0.5352 0.4128 0.3677 0.1705

1978 0.843 0.8162 0.7315 0.5873 0.5253 0.2273

1979 0.637 0.6191 0.5524 0.4827 0.4469 0.2078

1980 0.9083 0.8776 0.8108 0.6902 0.5965 0.2423

1981 0.5602 0.5418 0.4717 0.3706 0.3377 0.1636

1982 1.246 1.208 1.095 0.8622 0.7223 0.3134

1983 0.9794 0.9482 0.8373 0.7841 0.6788 0.2794

1984 0.9339 0.9049 0.7971 0.6402 0.5909 0.2695

1985 1.307 1.263 1.157 0.9976 0.8574 0.3593

1986 1.064 1.03 0.9144 0.7923 0.6822 0.3248

1987 0.5819 0.5639 0.5244 0.4798 0.4472 0.2131

1988 0.5832 0.5644 0.5448 0.4747 0.4121 0.1769
141

1989 1.649 1.598 1.502 1.179 1.005 0.3943

1990 1.091 1.058 0.9257 0.789 0.7045 0.3207

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.649 1.598 1.502 1.179 1.005 0.3943

0.0645161290322581 1.307 1.263 1.157 0.9976 0.8574 0.3593

0.0967741935483871 1.246 1.208 1.095 0.8622 0.7347 0.3248

0.129032258064516 1.233 1.204 1.054 0.8052 0.7223 0.3207

0.161290322580645 1.091 1.058 0.9257 0.7923 0.7045 0.3134

0.193548387096774 1.064 1.03 0.9144 0.789 0.6822 0.3127

0.225806451612903 1.024 0.9905 0.8854 0.7841 0.6788 0.2794

0.258064516129032 0.9794 0.9482 0.8373 0.7366 0.6485 0.2695

0.290322580645161 0.9339 0.9049 0.8108 0.6902 0.5965 0.2689

0.32258064516129 0.9083 0.8776 0.7971 0.6402 0.5909 0.2459

0.354838709677419 0.9022 0.8716 0.7651 0.6056 0.5469 0.2454

0.387096774193548 0.843 0.8162 0.7315 0.6022 0.5398 0.2423

0.419354838709677 0.7679 0.7417 0.6486 0.5873 0.5366 0.2409

0.451612903225806 0.7558 0.7339 0.6462 0.5435 0.5253 0.2388

0.483870967741936 0.7282 0.7067 0.628 0.5187 0.4618 0.2369

0.516129032258065 0.7069 0.6845 0.619 0.5151 0.4586 0.2329

0.548387096774194 0.6947 0.6698 0.6033 0.4962 0.4472 0.2273

0.580645161290323 0.688 0.6662 0.5938 0.4827 0.4469 0.2131

0.612903225806452 0.6597 0.6403 0.5816 0.4798 0.4227 0.2078

0.645161290322581 0.6427 0.6197 0.5524 0.4784 0.421 0.207

0.67741935483871 0.637 0.6191 0.5448 0.4747 0.4121 0.1931

0.709677419354839 0.6312 0.6108 0.5381 0.4678 0.407 0.1836

0.741935483870968 0.5955 0.5758 0.5352 0.4594 0.3863 0.1769

0.774193548387097 0.5832 0.5644 0.5244 0.4128 0.382 0.1741

0.806451612903226 0.5819 0.5639 0.5112 0.409 0.3677 0.1705

0.838709677419355 0.5648 0.546 0.4811 0.3868 0.3526 0.1682

0.870967741935484 0.5602 0.5418 0.4729 0.3769 0.3377 0.1636

0.903225806451613 0.5501 0.5324 0.4717 0.3706 0.3326 0.1616

0.935483870967742 0.5472 0.5276 0.4556 0.3622 0.3158 0.147

0.967741935483871 0.5156 0.4987 0.4348 0.3375 0.2992 0.1411

0.1 1.2447 1.2076 1.0909 0.8565 0.73346 0.32439

Average of yearly averages: 0.235366666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPAIR

Metfile: w14751.dvf

PRZM scenario: PAappleSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF
142

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as PAPPGRD.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3645 0.3511 0.3128 0.2425 0.2028 0.08188

1962 0.1838 0.1777 0.1553 0.1227 0.1216 0.07592

1963 0.1217 0.1176 0.1022 0.08989 0.08388 0.04855

1964 0.3016 0.2906 0.2483 0.2263 0.2116 0.09417

1965 0.1306 0.1261 0.117 0.1072 0.1006 0.0568

1966 0.7373 0.7111 0.6185 0.4686 0.3952 0.1516

1967 0.3693 0.3581 0.3166 0.2527 0.2343 0.1487

1968 1.016 0.9928 0.8669 0.652 0.5436 0.2262

1969 0.6026 0.5823 0.5225 0.3929 0.327 0.1589

1970 0.2054 0.2008 0.1894 0.1624 0.1542 0.102

1971 0.3285 0.3177 0.2774 0.2157 0.1843 0.08483

1972 0.5723 0.5544 0.4879 0.3762 0.3405 0.1566

1973 0.5121 0.4966 0.435 0.3417 0.3126 0.1409

1974 0.6063 0.5851 0.5136 0.4113 0.3599 0.1547

1975 0.6823 0.6594 0.5959 0.4933 0.4362 0.1825

1976 0.4029 0.3892 0.3531 0.3022 0.2597 0.1188

1977 0.222 0.2143 0.1871 0.1439 0.1404 0.07652

1978 0.548 0.5295 0.4746 0.3725 0.3197 0.1325

1979 0.3781 0.3657 0.3261 0.2737 0.2418 0.1133

1980 0.6574 0.6345 0.5608 0.4502 0.3916 0.1572

1981 0.1505 0.1457 0.131 0.1159 0.1074 0.07102

1982 1.056 1.023 0.9187 0.7229 0.6033 0.2271

1983 0.7299 0.7061 0.6169 0.5308 0.4686 0.1958

1984 0.7029 0.68 0.5985 0.4832 0.4087 0.1785

1985 1.051 1.015 0.901 0.782 0.6725 0.2731

1986 0.6964 0.6736 0.6225 0.5325 0.4616 0.2357

1987 0.3545 0.3424 0.2974 0.2527 0.23 0.1234

1988 0.3017 0.2918 0.262 0.2158 0.1864 0.08728

1989 1.347 1.302 1.243 0.9778 0.8256 0.3109

1990 0.8701 0.8426 0.7342 0.5865 0.5211 0.2326

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.347 1.302 1.243 0.9778 0.8256 0.3109

0.0645161290322581 1.056 1.023 0.9187 0.782 0.6725 0.2731

0.0967741935483871 1.051 1.015 0.901 0.7229 0.6033 0.2357

0.129032258064516 1.016 0.9928 0.8669 0.652 0.5436 0.2326

0.161290322580645 0.8701 0.8426 0.7342 0.5865 0.5211 0.2271

0.193548387096774 0.7373 0.7111 0.6225 0.5325 0.4686 0.2262

0.225806451612903 0.7299 0.7061 0.6185 0.5308 0.4616 0.1958

0.258064516129032 0.7029 0.68 0.6169 0.4933 0.4362 0.1825

0.290322580645161 0.6964 0.6736 0.5985 0.4832 0.4087 0.1785

0.32258064516129 0.6823 0.6594 0.5959 0.4686 0.3952 0.1589

0.354838709677419 0.6574 0.6345 0.5608 0.4502 0.3916 0.1572

0.387096774193548 0.6063 0.5851 0.5225 0.4113 0.3599 0.1566

0.419354838709677 0.6026 0.5823 0.5136 0.3929 0.3405 0.1547

0.451612903225806 0.5723 0.5544 0.4879 0.3762 0.327 0.1516

0.483870967741936 0.548 0.5295 0.4746 0.3725 0.3197 0.1487

0.516129032258065 0.5121 0.4966 0.435 0.3417 0.3126 0.1409

0.548387096774194 0.4029 0.3892 0.3531 0.3022 0.2597 0.1325

0.580645161290323 0.3781 0.3657 0.3261 0.2737 0.2418 0.1234

0.612903225806452 0.3693 0.3581 0.3166 0.2527 0.2343 0.1188

0.645161290322581 0.3645 0.3511 0.3128 0.2527 0.23 0.1133

0.67741935483871 0.3545 0.3424 0.2974 0.2425 0.2116 0.102

0.709677419354839 0.3285 0.3177 0.2774 0.2263 0.2028 0.09417

0.741935483870968 0.3017 0.2918 0.262 0.2158 0.1864 0.08728
143

0.774193548387097 0.3016 0.2906 0.2483 0.2157 0.1843 0.08483

0.806451612903226 0.222 0.2143 0.1894 0.1624 0.1542 0.08188

0.838709677419355 0.2054 0.2008 0.1871 0.1439 0.1404 0.07652

0.870967741935484 0.1838 0.1777 0.1553 0.1227 0.1216 0.07592

0.903225806451613 0.1505 0.1457 0.131 0.1159 0.1074 0.07102

0.935483870967742 0.1306 0.1261 0.117 0.1072 0.1006 0.0568

0.967741935483871 0.1217 0.1176 0.1022 0.08989 0.08388 0.04855

0.1 1.0475 1.01278 0.89759 0.71581 0.59733 0.23539

Average of yearly averages: 0.146599

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPGRD

Metfile: w14751.dvf

PRZM scenario: PAappleSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

PA Tomato

stored as PATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.5779 0.5588 0.4892 0.3789 0.3258 0.1736

1962 0.5862 0.5665 0.5314 0.4455 0.4094 0.1944

1963 0.5752 0.5546 0.481 0.381 0.3322 0.1527

1964 0.7409 0.7146 0.6125 0.5322 0.483 0.2098

1965 0.5739 0.5554 0.5014 0.4201 0.3771 0.1721

1966 0.6966 0.6741 0.605 0.487 0.4128 0.2491

1967 0.7598 0.7356 0.6531 0.5664 0.4981 0.2456

1968 1.367 1.338 1.178 1.012 0.9216 0.3787

1969 0.7754 0.7508 0.6786 0.5174 0.4352 0.2779

1970 0.6433 0.6219 0.5642 0.4579 0.4233 0.2129
144

1971 0.6625 0.6422 0.5756 0.5047 0.4417 0.1906

1972 0.7365 0.712 0.6574 0.5801 0.575 0.2573

1973 0.8698 0.8417 0.7504 0.6937 0.6205 0.2613

1974 1.07 1.034 0.9218 0.7363 0.6492 0.2896

1975 1.325 1.281 1.163 0.9723 0.8423 0.3407

1976 0.8002 0.7823 0.731 0.6028 0.5553 0.2507

1977 0.8566 0.826 0.7135 0.5491 0.4761 0.2132

1978 0.9891 0.957 0.8554 0.6722 0.6143 0.2699

1979 0.7568 0.7342 0.662 0.5459 0.518 0.2468

1980 1.011 0.9769 0.9095 0.7696 0.6744 0.2757

1981 0.5854 0.5662 0.4948 0.3887 0.3504 0.1713

1982 1.463 1.421 1.291 1.028 0.8628 0.3688

1983 1.581 1.532 1.34 1.148 0.9798 0.3904

1984 0.8696 0.8431 0.7484 0.6102 0.581 0.2776

1985 1.519 1.468 1.308 1.151 0.9894 0.4147

1986 1.306 1.263 1.126 0.944 0.8121 0.3898

1987 0.6673 0.6457 0.5998 0.5546 0.5373 0.2596

1988 0.668 0.6468 0.6073 0.5408 0.4721 0.2062

1989 2.052 1.986 1.909 1.515 1.293 0.507

1990 1.241 1.204 1.054 0.8966 0.7962 0.3758

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.052 1.986 1.909 1.515 1.293 0.507

0.0645161290322581 1.581 1.532 1.34 1.151 0.9894 0.4147

0.0967741935483871 1.519 1.468 1.308 1.148 0.9798 0.3904

0.129032258064516 1.463 1.421 1.291 1.028 0.9216 0.3898

0.161290322580645 1.367 1.338 1.178 1.012 0.8628 0.3787

0.193548387096774 1.325 1.281 1.163 0.9723 0.8423 0.3758

0.225806451612903 1.306 1.263 1.126 0.944 0.8121 0.3688

0.258064516129032 1.241 1.204 1.054 0.8966 0.7962 0.3407

0.290322580645161 1.07 1.034 0.9218 0.7696 0.6744 0.2896

0.32258064516129 1.011 0.9769 0.9095 0.7363 0.6492 0.2779

0.354838709677419 0.9891 0.957 0.8554 0.6937 0.6205 0.2776

0.387096774193548 0.8698 0.8431 0.7504 0.6722 0.6143 0.2757

0.419354838709677 0.8696 0.8417 0.7484 0.6102 0.581 0.2699

0.451612903225806 0.8566 0.826 0.731 0.6028 0.575 0.2613

0.483870967741936 0.8002 0.7823 0.7135 0.5801 0.5553 0.2596

0.516129032258065 0.7754 0.7508 0.6786 0.5664 0.5373 0.2573

0.548387096774194 0.7598 0.7356 0.662 0.5546 0.518 0.2507

0.580645161290323 0.7568 0.7342 0.6574 0.5491 0.4981 0.2491

0.612903225806452 0.7409 0.7146 0.6531 0.5459 0.483 0.2468

0.645161290322581 0.7365 0.712 0.6125 0.5408 0.4761 0.2456

0.67741935483871 0.6966 0.6741 0.6073 0.5322 0.4721 0.2132

0.709677419354839 0.668 0.6468 0.605 0.5174 0.4417 0.2129

0.741935483870968 0.6673 0.6457 0.5998 0.5047 0.4352 0.2098

0.774193548387097 0.6625 0.6422 0.5756 0.487 0.4233 0.2062

0.806451612903226 0.6433 0.6219 0.5642 0.4579 0.4128 0.1944

0.838709677419355 0.5862 0.5665 0.5314 0.4455 0.4094 0.1906

0.870967741935484 0.5854 0.5662 0.5014 0.4201 0.3771 0.1736

0.903225806451613 0.5779 0.5588 0.4948 0.3887 0.3504 0.1721

0.935483870967742 0.5752 0.5554 0.4892 0.381 0.3322 0.1713

0.967741935483871 0.5739 0.5546 0.481 0.3789 0.3258 0.1527

0.1 1.5134 1.4633 1.3063 1.136 0.97398 0.39034

Average of yearly averages: 0.274126666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMAIR

Metfile: w14751.dvf

PRZM scenario: PAtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L
145

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.05 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as PATOMGRD.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3808 0.367 0.3271 0.254 0.2144 0.09472

1962 0.2751 0.2659 0.2322 0.1891 0.1824 0.104

1963 0.1358 0.1313 0.1165 0.1051 0.1002 0.06169

1964 0.3968 0.3828 0.332 0.2903 0.2732 0.1222

1965 0.2099 0.2026 0.1771 0.1547 0.1483 0.08356

1966 0.6415 0.6191 0.5405 0.4121 0.3494 0.1628

1967 0.4442 0.4302 0.3809 0.3023 0.2744 0.1588

1968 1.169 1.146 1.008 0.7746 0.7248 0.2962

1969 0.698 0.6746 0.6048 0.4563 0.3805 0.1932

1970 0.242 0.2369 0.2218 0.1938 0.1949 0.1236

1971 0.3789 0.3674 0.3232 0.259 0.2216 0.1031

1972 0.5546 0.5378 0.4756 0.376 0.3693 0.17

1973 0.5887 0.5713 0.502 0.441 0.3985 0.1714

1974 0.7995 0.7716 0.6915 0.5581 0.4883 0.2065

1975 1.016 0.9823 0.8802 0.7388 0.642 0.2582

1976 0.5704 0.551 0.5103 0.4317 0.3699 0.1656

1977 0.4554 0.4392 0.3799 0.2868 0.2539 0.1223

1978 0.7172 0.6931 0.6179 0.4895 0.4236 0.1781

1979 0.5167 0.5009 0.4517 0.3812 0.3375 0.155

1980 0.7788 0.7519 0.6779 0.5447 0.4748 0.1928

1981 0.1573 0.1524 0.1386 0.124 0.1169 0.07991

1982 1.294 1.256 1.143 0.904 0.7562 0.286

1983 1.212 1.174 1.027 0.9156 0.7856 0.312

1984 0.6482 0.6275 0.558 0.4594 0.3906 0.1877

1985 1.288 1.245 1.105 0.9544 0.8241 0.3318

1986 0.8952 0.8664 0.8034 0.6852 0.5955 0.3044

1987 0.4982 0.4814 0.4183 0.3537 0.3285 0.1724

1988 0.4076 0.3942 0.352 0.2914 0.2522 0.1186

1989 1.808 1.75 1.684 1.34 1.135 0.4294

1990 1.039 1.007 0.8782 0.7095 0.6342 0.291

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.808 1.75 1.684 1.34 1.135 0.4294

0.0645161290322581 1.294 1.256 1.143 0.9544 0.8241 0.3318

0.0967741935483871 1.288 1.245 1.105 0.9156 0.7856 0.312

0.129032258064516 1.212 1.174 1.027 0.904 0.7562 0.3044

0.161290322580645 1.169 1.146 1.008 0.7746 0.7248 0.2962
146

0.193548387096774 1.039 1.007 0.8802 0.7388 0.642 0.291

0.225806451612903 1.016 0.9823 0.8782 0.7095 0.6342 0.286

0.258064516129032 0.8952 0.8664 0.8034 0.6852 0.5955 0.2582

0.290322580645161 0.7995 0.7716 0.6915 0.5581 0.4883 0.2065

0.32258064516129 0.7788 0.7519 0.6779 0.5447 0.4748 0.1932

0.354838709677419 0.7172 0.6931 0.6179 0.4895 0.4236 0.1928

0.387096774193548 0.698 0.6746 0.6048 0.4594 0.3985 0.1877

0.419354838709677 0.6482 0.6275 0.558 0.4563 0.3906 0.1781

0.451612903225806 0.6415 0.6191 0.5405 0.441 0.3805 0.1724

0.483870967741936 0.5887 0.5713 0.5103 0.4317 0.3699 0.1714

0.516129032258065 0.5704 0.551 0.502 0.4121 0.3693 0.17

0.548387096774194 0.5546 0.5378 0.4756 0.3812 0.3494 0.1656

0.580645161290323 0.5167 0.5009 0.4517 0.376 0.3375 0.1628

0.612903225806452 0.4982 0.4814 0.4183 0.3537 0.3285 0.1588

0.645161290322581 0.4554 0.4392 0.3809 0.3023 0.2744 0.155

0.67741935483871 0.4442 0.4302 0.3799 0.2914 0.2732 0.1236

0.709677419354839 0.4076 0.3942 0.352 0.2903 0.2539 0.1223

0.741935483870968 0.3968 0.3828 0.332 0.2868 0.2522 0.1222

0.774193548387097 0.3808 0.3674 0.3271 0.259 0.2216 0.1186

0.806451612903226 0.3789 0.367 0.3232 0.254 0.2144 0.104

0.838709677419355 0.2751 0.2659 0.2322 0.1938 0.1949 0.1031

0.870967741935484 0.242 0.2369 0.2218 0.1891 0.1824 0.09472

0.903225806451613 0.2099 0.2026 0.1771 0.1547 0.1483 0.08356

0.935483870967742 0.1573 0.1524 0.1386 0.124 0.1169 0.07991

0.967741935483871 0.1358 0.1313 0.1165 0.1051 0.1002 0.06169

0.1 1.2804 1.2379 1.0972 0.91444 0.78266 0.31124

Average of yearly averages: 0.187899333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMGRD

Metfile: w14751.dvf

PRZM scenario: PAtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)
147

PA Turf

stored as PATURFGRD.out

Chemical: DPXE2Y45

PRZM environment: PAturfSTD.txt modified Thuday, 23 February 2006 at 17:55:08

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.4253 0.4114 0.3603 0.2833 0.2397 0.1146

1962 0.3165 0.3059 0.2674 0.2095 0.182 0.08824

1963 0.2965 0.2858 0.247 0.1907 0.1614 0.06915

1964 0.294 0.2844 0.2491 0.2024 0.1797 0.07783

1965 0.2913 0.2818 0.2469 0.1922 0.1637 0.06853

1966 0.8803 0.849 0.735 0.5503 0.4626 0.1854

1967 0.4118 0.3995 0.354 0.3106 0.2748 0.1773

1968 0.9551 0.9244 0.8029 0.6043 0.5078 0.2339

1969 0.924 0.8929 0.8017 0.6025 0.5013 0.2397

1970 1.136 1.097 1.015 0.7874 0.6631 0.2875

1971 0.3167 0.3059 0.2663 0.2183 0.1915 0.1098

1972 0.4512 0.4371 0.3836 0.2961 0.2489 0.1334

1973 0.3822 0.3699 0.3251 0.275 0.2613 0.1189

1974 0.3412 0.3302 0.2897 0.258 0.2368 0.1102

1975 0.475 0.4598 0.4085 0.3423 0.3126 0.1374

1976 0.3013 0.2901 0.2568 0.2327 0.2199 0.1037

1977 0.3274 0.3156 0.2741 0.2137 0.1815 0.07849

1978 0.3934 0.383 0.3369 0.2717 0.2547 0.1197

1979 0.3038 0.2939 0.2576 0.2138 0.1953 0.09628

1980 0.3223 0.3113 0.274 0.2568 0.2337 0.09964

1981 0.2976 0.2877 0.2514 0.1962 0.1672 0.07563

1982 0.9944 0.9606 0.8588 0.6763 0.5657 0.2356

1983 1.178 1.142 1.079 0.8658 0.7317 0.2887

1984 0.5239 0.5086 0.4485 0.3709 0.3746 0.1842

1985 0.576 0.5571 0.4877 0.4244 0.371 0.1712

1986 0.8135 0.7876 0.687 0.5181 0.4393 0.1963

1987 0.3207 0.3108 0.2745 0.2181 0.2075 0.1135

1988 0.3015 0.2915 0.2548 0.2006 0.1716 0.07746

1989 1.114 1.089 0.9985 0.7796 0.659 0.2633

1990 0.7021 0.6802 0.5934 0.4575 0.3989 0.2

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.178 1.142 1.079 0.8658 0.7317 0.2887

0.0645161290322581 1.136 1.097 1.015 0.7874 0.6631 0.2875

0.0967741935483871 1.114 1.089 0.9985 0.7796 0.659 0.2633

0.129032258064516 0.9944 0.9606 0.8588 0.6763 0.5657 0.2397

0.161290322580645 0.9551 0.9244 0.8029 0.6043 0.5078 0.2356

0.193548387096774 0.924 0.8929 0.8017 0.6025 0.5013 0.2339

0.225806451612903 0.8803 0.849 0.735 0.5503 0.4626 0.2

0.258064516129032 0.8135 0.7876 0.687 0.5181 0.4393 0.1963

0.290322580645161 0.7021 0.6802 0.5934 0.4575 0.3989 0.1854

0.32258064516129 0.576 0.5571 0.4877 0.4244 0.3746 0.1842

0.354838709677419 0.5239 0.5086 0.4485 0.3709 0.371 0.1773

0.387096774193548 0.475 0.4598 0.4085 0.3423 0.3126 0.1712

0.419354838709677 0.4512 0.4371 0.3836 0.3106 0.2748 0.1374

0.451612903225806 0.4253 0.4114 0.3603 0.2961 0.2613 0.1334

0.483870967741936 0.4118 0.3995 0.354 0.2833 0.2547 0.1197
148

0.516129032258065 0.3934 0.383 0.3369 0.275 0.2489 0.1189

0.548387096774194 0.3822 0.3699 0.3251 0.2717 0.2397 0.1146

0.580645161290323 0.3412 0.3302 0.2897 0.258 0.2368 0.1135

0.612903225806452 0.3274 0.3156 0.2745 0.2568 0.2337 0.1102

0.645161290322581 0.3223 0.3113 0.2741 0.2327 0.2199 0.1098

0.67741935483871 0.3207 0.3108 0.274 0.2183 0.2075 0.1037

0.709677419354839 0.3167 0.3059 0.2674 0.2181 0.1953 0.09964

0.741935483870968 0.3165 0.3059 0.2663 0.2138 0.1915 0.09628

0.774193548387097 0.3038 0.2939 0.2576 0.2137 0.182 0.08824

0.806451612903226 0.3015 0.2915 0.2568 0.2095 0.1815 0.07849

0.838709677419355 0.3013 0.2901 0.2548 0.2024 0.1797 0.07783

0.870967741935484 0.2976 0.2877 0.2514 0.2006 0.1716 0.07746

0.903225806451613 0.2965 0.2858 0.2491 0.1962 0.1672 0.07563

0.935483870967742 0.294 0.2844 0.247 0.1922 0.1637 0.06915

0.967741935483871 0.2913 0.2818 0.2469 0.1907 0.1614 0.06853

0.1 1.10204 1.07616 0.98453 0.76927 0.64967 0.26094

Average of yearly averages: 0.148518333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATURFGRD

Metfile: w14751.dvf

PRZM scenario: PAturfSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.2912 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.2912 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

stored as PATF19GRD.out

Chemical: DPXE2Y45

PRZM environment: PAturfSTD.txt modified Thuday, 23 February 2006 at 16:55:08

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 15:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 08:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.9077 0.8775 0.7875 0.6933 0.6087 0.2272

1962 0.4104 0.3965 0.3457 0.2731 0.2526 0.2038

1963 0.1591 0.1544 0.1447 0.1444 0.1388 0.1231

1964 0.2163 0.2093 0.1988 0.182 0.175 0.1213

1965 0.1859 0.1799 0.1654 0.1434 0.1349 0.09031
149

1966 1.675 1.615 1.398 1.045 0.8785 0.2988

1967 0.7861 0.7752 0.6902 0.58 0.5302 0.3504

1968 0.9875 0.9503 0.8157 0.6261 0.5405 0.3486

1969 2.564 2.483 2.22 1.671 1.388 0.5766

1970 0.5023 0.5023 0.5022 0.4994 0.4762 0.3248

1971 1.17 1.133 0.9749 0.7988 0.6851 0.2815

1972 4.064 3.933 3.432 2.619 2.196 0.8335

1973 1.135 1.096 0.9547 0.7333 0.626 0.4423

1974 0.5937 0.5805 0.5165 0.4804 0.4289 0.2641

1975 0.6043 0.5839 0.5271 0.428 0.3671 0.2429

1976 0.3859 0.3733 0.3402 0.2712 0.2467 0.18

1977 0.1456 0.1416 0.138 0.1363 0.1336 0.1066

1978 0.5422 0.5236 0.4731 0.3998 0.3439 0.1649

1979 0.2771 0.2685 0.2491 0.2193 0.2173 0.1437

1980 0.2645 0.2561 0.238 0.2236 0.1883 0.1375

1981 0.3059 0.2986 0.2715 0.2344 0.208 0.1566

1982 1.069 1.039 0.9845 0.8234 0.7108 0.2874

1983 0.3862 0.3745 0.3461 0.3152 0.2979 0.161

1984 0.4911 0.4753 0.4456 0.4182 0.376 0.1723

1985 0.2824 0.273 0.2418 0.2166 0.205 0.1474

1986 0.8683 0.8389 0.7316 0.5608 0.4769 0.2441

1987 0.4696 0.453 0.4099 0.335 0.3048 0.2023

1988 0.4079 0.3932 0.3535 0.272 0.2302 0.142

1989 0.6636 0.643 0.5673 0.4995 0.4658 0.2533

1990 0.7076 0.6852 0.6132 0.5206 0.4787 0.2569

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.064 3.933 3.432 2.619 2.196 0.8335

0.0645161290322581 2.564 2.483 2.22 1.671 1.388 0.5766

0.0967741935483871 1.675 1.615 1.398 1.045 0.8785 0.4423

0.129032258064516 1.17 1.133 0.9845 0.8234 0.7108 0.3504

0.161290322580645 1.135 1.096 0.9749 0.7988 0.6851 0.3486

0.193548387096774 1.069 1.039 0.9547 0.7333 0.626 0.3248

0.225806451612903 0.9875 0.9503 0.8157 0.6933 0.6087 0.2988

0.258064516129032 0.9077 0.8775 0.7875 0.6261 0.5405 0.2874

0.290322580645161 0.8683 0.8389 0.7316 0.58 0.5302 0.2815

0.32258064516129 0.7861 0.7752 0.6902 0.5608 0.4787 0.2641

0.354838709677419 0.7076 0.6852 0.6132 0.5206 0.4769 0.2569

0.387096774193548 0.6636 0.643 0.5673 0.4995 0.4762 0.2533

0.419354838709677 0.6043 0.5839 0.5271 0.4994 0.4658 0.2441

0.451612903225806 0.5937 0.5805 0.5165 0.4804 0.4289 0.2429

0.483870967741936 0.5422 0.5236 0.5022 0.428 0.376 0.2272

0.516129032258065 0.5023 0.5023 0.4731 0.4182 0.3671 0.2038

0.548387096774194 0.4911 0.4753 0.4456 0.3998 0.3439 0.2023

0.580645161290323 0.4696 0.453 0.4099 0.335 0.3048 0.18

0.612903225806452 0.4104 0.3965 0.3535 0.3152 0.2979 0.1723

0.645161290322581 0.4079 0.3932 0.3461 0.2731 0.2526 0.1649

0.67741935483871 0.3862 0.3745 0.3457 0.272 0.2467 0.161

0.709677419354839 0.3859 0.3733 0.3402 0.2712 0.2302 0.1566

0.741935483870968 0.3059 0.2986 0.2715 0.2344 0.2173 0.1474

0.774193548387097 0.2824 0.273 0.2491 0.2236 0.208 0.1437

0.806451612903226 0.2771 0.2685 0.2418 0.2193 0.205 0.142

0.838709677419355 0.2645 0.2561 0.238 0.2166 0.1883 0.1375

0.870967741935484 0.2163 0.2093 0.1988 0.182 0.175 0.1231

0.903225806451613 0.1859 0.1799 0.1654 0.1444 0.1388 0.1213

0.935483870967742 0.1591 0.1544 0.1447 0.1434 0.1349 0.1066

0.967741935483871 0.1456 0.1416 0.138 0.1363 0.1336 0.09031

0.1 1.6245 1.5668 1.35665 1.02284 0.86173 0.43311

Average of yearly averages: 0.249507

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATF19GRD

Metfile: w14751.dvf

PRZM scenario: PAturfSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45
150

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.029 kg/ha

Application Efficiency: APPEFF 0.99 fraction

Spray Drift DRFT 0.01 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.029 kg/ha

Interval 2 interval 7 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.029 kg/ha

Interval 3 interval 7 days Set to 0 or delete line for single app.

app. rate 3 apprate 0.029 kg/ha

Interval 4 interval 7 days Set to 0 or delete line for single app.

app. rate 4 apprate 0.029 kg/ha

Interval 5 interval 7 days Set to 0 or delete line for single app.

app. rate 5 apprate 0.029 kg/ha

Interval 6 interval 7 days Set to 0 or delete line for single app.

app. rate 6 apprate 0.029 kg/ha

Interval 7 interval 7 days Set to 0 or delete line for single app.

app. rate 7 apprate 0.029 kg/ha

Interval 8 interval 7 days Set to 0 or delete line for single app.

app. rate 8 apprate 0.029 kg/ha

Interval 9 interval 7 days Set to 0 or delete line for single app.

app. rate 9 apprate 0.029 kg/ha

Interval 10 interval 7 days Set to 0 or delete line for single app.

app. rate 10 apprate 0.029 kg/ha

Interval 11 interval 7 days Set to 0 or delete line for single app.

app. rate 11 apprate 0.029 kg/ha

Interval 12 interval 7 days Set to 0 or delete line for single app.

app. rate 12 apprate 0.029 kg/ha

Interval 13 interval 7 days Set to 0 or delete line for single app.

app. rate 13 apprate 0.029 kg/ha

Interval 14 interval 7 days Set to 0 or delete line for single app.

app. rate 14 apprate 0.029 kg/ha

Interval 15 interval 7 days Set to 0 or delete line for single app.

app. rate 15 apprate 0.029 kg/ha

Interval 16 interval 7 days Set to 0 or delete line for single app.

app. rate 16 apprate 0.029 kg/ha

Interval 17 interval 7 days Set to 0 or delete line for single app.

app. rate 17 apprate 0.029 kg/ha

Interval 18 interval 7 days Set to 0 or delete line for single app.

app. rate 18 apprate 0.029 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)
151

Spray Drift Analysis

CA Cotton

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: CAcotton_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:12

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.03077 0.02947 0.02485 0.02033 0.01786 0.006117

1962 0.05288 0.05088 0.04335 0.03238 0.0296 0.01089

1963 0.7594 0.7297 0.6692 0.5503 0.4679 0.1593

1964 0.02927 0.02884 0.02714 0.02316 0.02044 0.008905

1965 2.52 2.419 2.063 1.557 1.271 0.4181

1966 0.0617 0.06073 0.05681 0.04902 0.04376 0.01838

1967 0.5374 0.5172 0.4471 0.3482 0.2881 0.09584

1968 0.3215 0.3132 0.281 0.2175 0.1936 0.07089

1969 2.083 2.013 1.72 1.258 1.034 0.3473

1970 1.334 1.279 1.134 0.8225 0.6674 0.2238

1971 0.4627 0.4433 0.3744 0.2725 0.22 0.07941

1972 0.0144 0.01425 0.01365 0.01209 0.01076 0.004662

1973 0.3525 0.3412 0.3052 0.2443 0.2008 0.06653

1974 0.231 0.2225 0.1916 0.1761 0.1485 0.051

1975 0.05049 0.0487 0.04219 0.03143 0.02577 0.00962

1976 0.04331 0.04152 0.03511 0.02556 0.02085 0.007328

1977 0.1711 0.1642 0.1459 0.1092 0.09109 0.03048

1978 0.6844 0.6591 0.5767 0.4374 0.3593 0.1183

1979 0.3242 0.3123 0.2938 0.229 0.1887 0.06432

1980 1.291 1.249 1.148 0.9099 0.7604 0.2587

1981 0.1392 0.1345 0.1166 0.0867 0.07431 0.02978

1982 0.3506 0.3415 0.3034 0.224 0.1815 0.06051

1983 0.5535 0.5339 0.4676 0.3561 0.2936 0.09992

1984 0.01308 0.0129 0.01217 0.01053 0.009328 0.003981

1985 0.04681 0.04492 0.03823 0.02738 0.02206 0.007185

1986 0.5331 0.5174 0.4742 0.3512 0.3053 0.1071

1987 0.6987 0.6713 0.6011 0.4498 0.3667 0.1222

1988 0.4243 0.4109 0.3603 0.2823 0.2799 0.1066

1989 1.023 0.986 0.8421 0.739 0.6269 0.2137

1990 0.1842 0.1766 0.1489 0.1062 0.08525 0.03244

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.52 2.419 2.063 1.557 1.271 0.4181

0.0645161290322581 2.083 2.013 1.72 1.258 1.034 0.3473

0.0967741935483871 1.334 1.279 1.148 0.9099 0.7604 0.2587

0.129032258064516 1.291 1.249 1.134 0.8225 0.6674 0.2238

0.161290322580645 1.023 0.986 0.8421 0.739 0.6269 0.2137

0.193548387096774 0.7594 0.7297 0.6692 0.5503 0.4679 0.1593

0.225806451612903 0.6987 0.6713 0.6011 0.4498 0.3667 0.1222

0.258064516129032 0.6844 0.6591 0.5767 0.4374 0.3593 0.1183

0.290322580645161 0.5535 0.5339 0.4742 0.3561 0.3053 0.1071

0.32258064516129 0.5374 0.5174 0.4676 0.3512 0.2936 0.1066

0.354838709677419 0.5331 0.5172 0.4471 0.3482 0.2881 0.09992

0.387096774193548 0.4627 0.4433 0.3744 0.2823 0.2799 0.09584

0.419354838709677 0.4243 0.4109 0.3603 0.2725 0.22 0.07941

0.451612903225806 0.3525 0.3415 0.3052 0.2443 0.2008 0.07089
152

0.483870967741936 0.3506 0.3412 0.3034 0.229 0.1936 0.06653

0.516129032258065 0.3242 0.3132 0.2938 0.224 0.1887 0.06432

0.548387096774194 0.3215 0.3123 0.281 0.2175 0.1815 0.06051

0.580645161290323 0.231 0.2225 0.1916 0.1761 0.1485 0.051

0.612903225806452 0.1842 0.1766 0.1489 0.1092 0.09109 0.03244

0.645161290322581 0.1711 0.1642 0.1459 0.1062 0.08525 0.03048

0.67741935483871 0.1392 0.1345 0.1166 0.0867 0.07431 0.02978

0.709677419354839 0.0617 0.06073 0.05681 0.04902 0.04376 0.01838

0.741935483870968 0.05288 0.05088 0.04335 0.03238 0.0296 0.01089

0.774193548387097 0.05049 0.0487 0.04219 0.03143 0.02577 0.00962

0.806451612903226 0.04681 0.04492 0.03823 0.02738 0.02206 0.008905

0.838709677419355 0.04331 0.04152 0.03511 0.02556 0.02085 0.007328

0.870967741935484 0.03077 0.02947 0.02714 0.02316 0.02044 0.007185

0.903225806451613 0.02927 0.02884 0.02485 0.02033 0.01786 0.006117

0.935483870967742 0.0144 0.01425 0.01365 0.01209 0.01076 0.004662

0.967741935483871 0.01308 0.0129 0.01217 0.01053 0.009328 0.003981

0.1 1.3297 1.276 1.1466 0.90116 0.7511 0.25521

Average of yearly averages: 0.0944429333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile: w93193.dvf

PRZM scenario: CAcotton_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Grape

stored as CAGRAPAIR.out

Chemical: DPXE2Y45

PRZM environment: CAgrapes_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:42:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.002715 0.002605 0.002239 0.001644 0.001336 0.0004327
153

1962 0.3327 0.3222 0.2848 0.2115 0.1725 0.05747

1963 0.1398 0.1349 0.1214 0.09716 0.08596 0.03177

1964 0.00501 0.004853 0.004362 0.003666 0.003737 0.001651

1965 0.2897 0.278 0.2363 0.1744 0.142 0.04659

1966 0.006831 0.006723 0.00629 0.005427 0.004847 0.002003

1967 0.04427 0.0431 0.03759 0.03259 0.0287 0.0102

1968 0.009641 0.009247 0.007863 0.006833 0.005723 0.002183

1969 0.2139 0.2066 0.1763 0.1286 0.1051 0.03537

1970 0.1259 0.122 0.1058 0.07652 0.06207 0.0208

1971 0.00335 0.003232 0.002804 0.002146 0.001831 0.00109

1972 0.0005321 0.0005107 0.0004647 0.000366 0.000315 0.0001357

1973 0.1552 0.1498 0.13 0.09936 0.08214 0.02753

1974 0.008977 0.008677 0.007466 0.005519 0.004497 0.002022

1975 0.0005458 0.0005294 0.0004694 0.0003799 0.0003288 0.0001527

1976 0.1916 0.1844 0.1581 0.1179 0.09714 0.03281

1977 0.01012 0.009757 0.008725 0.006895 0.00578 0.002433

1978 0.2407 0.2363 0.2095 0.1633 0.1367 0.04613

1979 0.02609 0.02519 0.02187 0.01651 0.01365 0.005147

1980 0.3072 0.2962 0.2575 0.1919 0.1575 0.05291

1981 0.03259 0.03144 0.02713 0.01996 0.01629 0.006257

1982 0.04139 0.03998 0.03652 0.02882 0.02356 0.007925

1983 0.1362 0.1314 0.1138 0.09589 0.08126 0.02815

1984 0.005313 0.005149 0.004548 0.003638 0.003348 0.001427

1985 0.003771 0.003631 0.003148 0.002901 0.002544 0.0009049

1986 0.2601 0.2504 0.2164 0.1671 0.1382 0.04605

1987 0.02534 0.02441 0.02111 0.01647 0.0137 0.00518

1988 0.01685 0.01611 0.01344 0.00975 0.008069 0.002752

1989 0.01837 0.01768 0.01515 0.01097 0.009519 0.003356

1990 0.0152 0.01459 0.01242 0.009086 0.007481 0.002566

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.3327 0.3222 0.2848 0.2115 0.1725 0.05747

0.0645161290322581 0.3072 0.2962 0.2575 0.1919 0.1575 0.05291

0.0967741935483871 0.2897 0.278 0.2363 0.1744 0.142 0.04659

0.129032258064516 0.2601 0.2504 0.2164 0.1671 0.1382 0.04613

0.161290322580645 0.2407 0.2363 0.2095 0.1633 0.1367 0.04605

0.193548387096774 0.2139 0.2066 0.1763 0.1286 0.1051 0.03537

0.225806451612903 0.1916 0.1844 0.1581 0.1179 0.09714 0.03281

0.258064516129032 0.1552 0.1498 0.13 0.09936 0.08596 0.03177

0.290322580645161 0.1398 0.1349 0.1214 0.09716 0.08214 0.02815

0.32258064516129 0.1362 0.1314 0.1138 0.09589 0.08126 0.02753

0.354838709677419 0.1259 0.122 0.1058 0.07652 0.06207 0.0208

0.387096774193548 0.04427 0.0431 0.03759 0.03259 0.0287 0.0102

0.419354838709677 0.04139 0.03998 0.03652 0.02882 0.02356 0.007925

0.451612903225806 0.03259 0.03144 0.02713 0.01996 0.01629 0.006257

0.483870967741936 0.02609 0.02519 0.02187 0.01651 0.0137 0.00518

0.516129032258065 0.02534 0.02441 0.02111 0.01647 0.01365 0.005147

0.548387096774194 0.01837 0.01768 0.01515 0.01097 0.009519 0.003356

0.580645161290323 0.01685 0.01611 0.01344 0.00975 0.008069 0.002752

0.612903225806452 0.0152 0.01459 0.01242 0.009086 0.007481 0.002566

0.645161290322581 0.01012 0.009757 0.008725 0.006895 0.00578 0.002433

0.67741935483871 0.009641 0.009247 0.007863 0.006833 0.005723 0.002183

0.709677419354839 0.008977 0.008677 0.007466 0.005519 0.004847 0.002022

0.741935483870968 0.006831 0.006723 0.00629 0.005427 0.004497 0.002003

0.774193548387097 0.005313 0.005149 0.004548 0.003666 0.003737 0.001651

0.806451612903226 0.00501 0.004853 0.004362 0.003638 0.003348 0.001427

0.838709677419355 0.003771 0.003631 0.003148 0.002901 0.002544 0.00109

0.870967741935484 0.00335 0.003232 0.002804 0.002146 0.001831 0.0009049

0.903225806451613 0.002715 0.002605 0.002239 0.001644 0.001336 0.0004327

0.935483870967742 0.0005458 0.0005294 0.0004694 0.0003799 0.0003288 0.0001527

0.967741935483871 0.0005321 0.0005107 0.0004647 0.000366 0.000315 0.0001357

0.1 0.28674 0.27524 0.23431 0.17367 0.14162 0.046544

Average of yearly averages: 0.0161132666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CAGRAPAIR
154

Metfile: w93193.dvf

PRZM scenario: CAgrapes_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Lettuce

stored as CALETAIR.out

Chemical: DPXE2Y45

PRZM environment: CAlettuceSTD.txt modified Tueday, 21 February 2006 at 14:38:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w23273.dvf modified Wedday, 3 July 2002 at 09:04:22

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.963 1.903 1.627 0.996 0.6642 0.1649

1962 1.493 1.448 1.289 1.07 1.021 0.4444

1963 2.218 2.13 1.909 1.591 1.353 0.5199

1964 0.6549 0.6294 0.5477 0.436 0.3647 0.2074

1965 0.6151 0.594 0.5231 0.3946 0.3334 0.1636

1966 1.319 1.267 1.098 0.8 0.5346 0.1461

1967 0.7983 0.7712 0.6723 0.6121 0.5773 0.2749

1968 0.72 0.6919 0.5958 0.4568 0.376 0.1911

1969 3.092 2.979 2.6 1.902 1.569 0.5841

1970 3.879 3.715 3.305 2.392 1.941 0.7143

1971 0.5941 0.5728 0.4914 0.363 0.2993 0.1739

1972 1.508 1.45 1.257 0.9084 0.6749 0.1963

1973 0.9311 0.9053 0.8052 0.709 0.6102 0.3102

1974 3.525 3.409 3.048 2.338 1.929 0.6985

1975 1.234 1.187 1.025 0.7667 0.6358 0.2543

1976 0.7907 0.7666 0.6598 0.5316 0.4704 0.2352

1977 1.225 1.185 1.023 0.7796 0.8003 0.3605

1978 2.605 2.508 2.203 1.665 1.377 0.5237

1979 0.9513 0.915 0.8017 0.6919 0.5941 0.2269

1980 1.33 1.293 1.185 0.9598 0.8019 0.3027

1981 2.95 2.855 2.501 1.922 1.589 0.5807

1982 0.6106 0.5902 0.5217 0.4454 0.3789 0.1514

1983 1.76 1.697 1.497 1.145 0.9536 0.3392

1984 0.5581 0.5378 0.4737 0.355 0.2464 0.08255

1985 0.498 0.4788 0.4334 0.3297 0.2545 0.158

1986 1.697 1.636 1.443 1.144 0.9567 0.3773

1987 2.997 2.892 2.467 1.802 1.479 0.542
155

1988 1.643 1.571 1.311 0.9905 0.8791 0.3476

1989 0.1143 0.1108 0.09777 0.07777 0.06906 0.04142

1990 0.2746 0.2636 0.2269 0.2145 0.1893 0.08629

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 3.879 3.715 3.305 2.392 1.941 0.7143

0.0645161290322581 3.525 3.409 3.048 2.338 1.929 0.6985

0.0967741935483871 3.092 2.979 2.6 1.922 1.589 0.5841

0.129032258064516 2.997 2.892 2.501 1.902 1.569 0.5807

0.161290322580645 2.95 2.855 2.467 1.802 1.479 0.542

0.193548387096774 2.605 2.508 2.203 1.665 1.377 0.5237

0.225806451612903 2.218 2.13 1.909 1.591 1.353 0.5199

0.258064516129032 1.963 1.903 1.627 1.145 1.021 0.4444

0.290322580645161 1.76 1.697 1.497 1.144 0.9567 0.3773

0.32258064516129 1.697 1.636 1.443 1.07 0.9536 0.3605

0.354838709677419 1.643 1.571 1.311 0.996 0.8791 0.3476

0.387096774193548 1.508 1.45 1.289 0.9905 0.8019 0.3392

0.419354838709677 1.493 1.448 1.257 0.9598 0.8003 0.3102

0.451612903225806 1.33 1.293 1.185 0.9084 0.6749 0.3027

0.483870967741936 1.319 1.267 1.098 0.8 0.6642 0.2749

0.516129032258065 1.234 1.187 1.025 0.7796 0.6358 0.2543

0.548387096774194 1.225 1.185 1.023 0.7667 0.6102 0.2352

0.580645161290323 0.9513 0.915 0.8052 0.709 0.5941 0.2269

0.612903225806452 0.9311 0.9053 0.8017 0.6919 0.5773 0.2074

0.645161290322581 0.7983 0.7712 0.6723 0.6121 0.5346 0.1963

0.67741935483871 0.7907 0.7666 0.6598 0.5316 0.4704 0.1911

0.709677419354839 0.72 0.6919 0.5958 0.4568 0.3789 0.1739

0.741935483870968 0.6549 0.6294 0.5477 0.4454 0.376 0.1649

0.774193548387097 0.6151 0.594 0.5231 0.436 0.3647 0.1636

0.806451612903226 0.6106 0.5902 0.5217 0.3946 0.3334 0.158

0.838709677419355 0.5941 0.5728 0.4914 0.363 0.2993 0.1514

0.870967741935484 0.5581 0.5378 0.4737 0.355 0.2545 0.1461

0.903225806451613 0.498 0.4788 0.4334 0.3297 0.2464 0.08629

0.935483870967742 0.2746 0.2636 0.2269 0.2145 0.1893 0.08255

0.967741935483871 0.1143 0.1108 0.09777 0.07777 0.06906 0.04142

0.1 3.0825 2.9703 2.5901 1.92 1.587 0.58376

Average of yearly averages: 0.313312

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CALETAIR

Metfile: w23273.dvf

PRZM scenario: CAlettuceSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 16-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha
156

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

CA Tomato

stored as CATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: CAtomato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:43:54

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w93193.dvf modified Wedday, 3 July 2002 at 09:04:24

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.01475 0.01416 0.01194 0.00895 0.007308 0.002414

1962 0.04922 0.04724 0.03988 0.02825 0.0228 0.007376

1963 0.3763 0.3628 0.3444 0.2863 0.2478 0.08563

1964 0.01615 0.01592 0.01498 0.01278 0.0115 0.00487

1965 1.542 1.48 1.262 0.9489 0.7747 0.2546

1966 0.03755 0.03695 0.03457 0.02983 0.02678 0.01101

1967 0.3427 0.3298 0.2899 0.2549 0.2154 0.07285

1968 0.2595 0.2518 0.225 0.1838 0.1511 0.05134

1969 0.2554 0.2448 0.2068 0.1476 0.1277 0.04641

1970 0.6329 0.6066 0.5336 0.3877 0.3144 0.1034

1971 0.05563 0.05351 0.04591 0.0397 0.03608 0.01479

1972 0.003076 0.002968 0.002657 0.002142 0.001958 0.001082

1973 0.2742 0.2645 0.2271 0.1622 0.1307 0.04215

1974 0.111 0.1081 0.09555 0.06954 0.06026 0.02202

1975 0.03937 0.03795 0.03276 0.02424 0.01974 0.006938

1976 0.003359 0.003232 0.002771 0.002066 0.001722 0.0007385

1977 0.08814 0.08456 0.07754 0.05686 0.04643 0.01523

1978 0.4076 0.3933 0.3655 0.3061 0.2694 0.09309

1979 0.07222 0.06976 0.0606 0.05083 0.04358 0.01689

1980 0.5507 0.5285 0.4487 0.3262 0.2662 0.088

1981 0.2519 0.2425 0.2079 0.1518 0.1232 0.04162

1982 0.4257 0.4152 0.377 0.2938 0.2399 0.0803

1983 0.5044 0.4879 0.4693 0.3912 0.3314 0.1144

1984 0.01597 0.01575 0.01486 0.01286 0.0118 0.005

1985 0.01404 0.01349 0.01167 0.008458 0.006833 0.002305

1986 0.6348 0.6104 0.5246 0.3976 0.3242 0.1051

1987 0.2284 0.2199 0.189 0.1576 0.1312 0.04582

1988 0.03004 0.0291 0.02529 0.01895 0.01551 0.00615

1989 0.4059 0.3907 0.3321 0.2451 0.2141 0.0739

1990 0.01039 0.01003 0.008733 0.007605 0.00687 0.003967

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.542 1.48 1.262 0.9489 0.7747 0.2546

0.0645161290322581 0.6348 0.6104 0.5336 0.3976 0.3314 0.1144

0.0967741935483871 0.6329 0.6066 0.5246 0.3912 0.3242 0.1051

0.129032258064516 0.5507 0.5285 0.4693 0.3877 0.3144 0.1034

0.161290322580645 0.5044 0.4879 0.4487 0.3262 0.2694 0.09309

0.193548387096774 0.4257 0.4152 0.377 0.3061 0.2662 0.088

0.225806451612903 0.4076 0.3933 0.3655 0.2938 0.2478 0.08563

0.258064516129032 0.4059 0.3907 0.3444 0.2863 0.2399 0.0803

0.290322580645161 0.3763 0.3628 0.3321 0.2549 0.2154 0.0739

0.32258064516129 0.3427 0.3298 0.2899 0.2451 0.2141 0.07285

0.354838709677419 0.2742 0.2645 0.2271 0.1838 0.1511 0.05134

0.387096774193548 0.2595 0.2518 0.225 0.1622 0.1312 0.04641

0.419354838709677 0.2554 0.2448 0.2079 0.1576 0.1307 0.04582

0.451612903225806 0.2519 0.2425 0.2068 0.1518 0.1277 0.04215

0.483870967741936 0.2284 0.2199 0.189 0.1476 0.1232 0.04162
157

0.516129032258065 0.111 0.1081 0.09555 0.06954 0.06026 0.02202

0.548387096774194 0.08814 0.08456 0.07754 0.05686 0.04643 0.01689

0.580645161290323 0.07222 0.06976 0.0606 0.05083 0.04358 0.01523

0.612903225806452 0.05563 0.05351 0.04591 0.0397 0.03608 0.01479

0.645161290322581 0.04922 0.04724 0.03988 0.02983 0.02678 0.01101

0.67741935483871 0.03937 0.03795 0.03457 0.02825 0.0228 0.007376

0.709677419354839 0.03755 0.03695 0.03276 0.02424 0.01974 0.006938

0.741935483870968 0.03004 0.0291 0.02529 0.01895 0.01551 0.00615

0.774193548387097 0.01615 0.01592 0.01498 0.01286 0.0118 0.005

0.806451612903226 0.01597 0.01575 0.01486 0.01278 0.0115 0.00487

0.838709677419355 0.01475 0.01416 0.01194 0.00895 0.007308 0.003967

0.870967741935484 0.01404 0.01349 0.01167 0.008458 0.00687 0.002414

0.903225806451613 0.01039 0.01003 0.008733 0.007605 0.006833 0.002305

0.935483870967742 0.003359 0.003232 0.002771 0.002142 0.001958 0.001082

0.967741935483871 0.003076 0.002968 0.002657 0.002066 0.001722 0.0007385

0.1 0.62468 0.59879 0.51907 0.39085 0.32322 0.10493

Average of yearly averages: 0.0473130166666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CATOMAIR

Metfile: w93193.dvf

PRZM scenario: CAtomato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-3 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Cabbage

stored as FLCABAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcabbageSTD.txt modified Thuday, 24 May 2007 at 09:40:46

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12842.dvf modified Wedday, 3 July 2002 at 09:04:28

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.406 1.346 0.794 0.3003 0.2002 0.04937
158

1962 1.103 1.061 0.9077 0.6735 0.5705 0.2149

1963 4.089 3.965 3.353 2.267 1.514 0.4025

1964 1.649 1.604 1.496 1.222 1.049 0.4626

1965 0.8052 0.7746 0.6729 0.5195 0.4609 0.1914

1966 0.5683 0.5482 0.4899 0.396 0.3517 0.1329

1967 0.3716 0.3561 0.3007 0.2029 0.1662 0.07783

1968 1.63 1.562 1.349 1.076 0.8381 0.2815

1969 0.973 0.9404 0.8026 0.5369 0.4565 0.2743

1970 0.6234 0.6122 0.5464 0.4237 0.3588 0.136

1971 0.5694 0.5458 0.4667 0.3378 0.2813 0.168

1972 0.666 0.6424 0.5989 0.5563 0.4038 0.2127

1973 0.9073 0.8654 0.7319 0.6267 0.4291 0.2042

1974 0.8208 0.7894 0.5586 0.3239 0.273 0.1338

1975 1.146 1.095 0.9137 0.6472 0.4685 0.2292

1976 0.3185 0.3085 0.2717 0.2118 0.2065 0.1397

1977 0.4746 0.455 0.4334 0.2619 0.1778 0.1033

1978 1.011 0.9684 0.8195 0.5967 0.4321 0.1785

1979 0.6415 0.62 0.5852 0.4773 0.4112 0.1565

1980 0.6651 0.6391 0.5879 0.3732 0.2526 0.1222

1981 1.269 1.221 0.5794 0.4337 0.3664 0.171

1982 1.14 1.091 0.957 0.7298 0.6195 0.246

1983 0.8137 0.7921 0.6872 0.3459 0.2728 0.1638

1984 0.6459 0.624 0.5445 0.4169 0.3499 0.1241

1985 3.806 3.686 3.099 2.211 1.506 0.4164

1986 1.883 1.815 1.538 1.18 0.8552 0.4738

1987 1.437 1.377 1.199 0.9291 0.6282 0.3171

1988 2.431 2.324 1.962 1.237 0.8325 0.3431

1989 1.158 1.114 0.9571 0.7389 0.6214 0.3438

1990 0.5552 0.5357 0.4647 0.3606 0.3061 0.1114

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.089 3.965 3.353 2.267 1.514 0.4738

0.0645161290322581 3.806 3.686 3.099 2.211 1.506 0.4626

0.0967741935483871 2.431 2.324 1.962 1.237 1.049 0.4164

0.129032258064516 1.883 1.815 1.538 1.222 0.8552 0.4025

0.161290322580645 1.649 1.604 1.496 1.18 0.8381 0.3438

0.193548387096774 1.63 1.562 1.349 1.076 0.8325 0.3431

0.225806451612903 1.437 1.377 1.199 0.9291 0.6282 0.3171

0.258064516129032 1.406 1.346 0.9571 0.7389 0.6214 0.2815

0.290322580645161 1.269 1.221 0.957 0.7298 0.6195 0.2743

0.32258064516129 1.158 1.114 0.9137 0.6735 0.5705 0.246

0.354838709677419 1.146 1.095 0.9077 0.6472 0.4685 0.2292

0.387096774193548 1.14 1.091 0.8195 0.6267 0.4609 0.2149

0.419354838709677 1.103 1.061 0.8026 0.5967 0.4565 0.2127

0.451612903225806 1.011 0.9684 0.794 0.5563 0.4321 0.2042

0.483870967741936 0.973 0.9404 0.7319 0.5369 0.4291 0.1914

0.516129032258065 0.9073 0.8654 0.6872 0.5195 0.4112 0.1785

0.548387096774194 0.8208 0.7921 0.6729 0.4773 0.4038 0.171

0.580645161290323 0.8137 0.7894 0.5989 0.4337 0.3664 0.168

0.612903225806452 0.8052 0.7746 0.5879 0.4237 0.3588 0.1638

0.645161290322581 0.666 0.6424 0.5852 0.4169 0.3517 0.1565

0.67741935483871 0.6651 0.6391 0.5794 0.396 0.3499 0.1397

0.709677419354839 0.6459 0.624 0.5586 0.3732 0.3061 0.136

0.741935483870968 0.6415 0.62 0.5464 0.3606 0.2813 0.1338

0.774193548387097 0.6234 0.6122 0.5445 0.3459 0.273 0.1329

0.806451612903226 0.5694 0.5482 0.4899 0.3378 0.2728 0.1241

0.838709677419355 0.5683 0.5458 0.4667 0.3239 0.2526 0.1222

0.870967741935484 0.5552 0.5357 0.4647 0.3003 0.2065 0.1114

0.903225806451613 0.4746 0.455 0.4334 0.2619 0.2002 0.1033

0.935483870967742 0.3716 0.3561 0.3007 0.2118 0.1778 0.07783

0.967741935483871 0.3185 0.3085 0.2717 0.2029 0.1662 0.04937

0.1 2.3762 2.2731 1.9196 1.2355 1.02962 0.41501

Average of yearly averages: 0.219396666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCABAIR
159

Metfile: w12842.dvf

PRZM scenario: FLcabbageSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Cucumber

stored as FLCUCAIR.out

Chemical: DPXE2Y45

PRZM environment: FLcucumberSTD.txt modified Wedday, 13 June 2007 at 11:19:24

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.517 1.453 1.234 0.8963 0.675 0.1664

1962 0.6598 0.6318 0.5354 0.3936 0.3154 0.1917

1963 1.463 1.301 1.115 0.9652 0.8055 0.3056

1964 2.791 2.679 2.283 2.102 1.495 0.6684

1965 6.679 6.463 5.489 4.004 2.978 1.012

1966 3.438 3.316 2.843 2.089 1.562 0.9159

1967 1.837 1.763 1.494 1.111 0.8135 0.4485

1968 1.451 1.394 1.223 1.023 0.7919 0.3331

1969 3.925 3.813 3.304 2.464 1.861 0.6751

1970 1.222 1.189 1.07 0.8671 0.7522 0.3022

1971 2.708 2.602 2.258 1.677 1.242 0.3716

1972 7.724 7.418 6.317 4.399 2.945 0.9258

1973 2.912 2.823 2.532 2.018 1.723 0.697

1974 1.308 1.254 1.078 0.7599 0.5774 0.3332

1975 0.7003 0.6717 0.5766 0.4722 0.3708 0.221

1976 2.445 2.352 2.015 1.54 1.066 0.3352

1977 1.978 1.923 1.669 1.024 0.6969 0.4209

1978 3.461 3.373 2.96 2.257 1.66 0.6134

1979 1.345 1.304 1.153 0.9004 0.763 0.4168

1980 0.6153 0.6008 0.5137 0.3992 0.3072 0.1843

1981 4.533 4.329 3.604 2.502 1.672 0.4782

1982 5.33 5.151 4.609 3.52 2.413 1.029
160

1983 3.433 3.3 3.093 2.391 1.773 0.8568

1984 4.673 4.487 3.844 2.759 1.911 0.7309

1985 2.124 2.046 1.763 1.329 1.118 0.4426

1986 2.754 2.7 2.473 2.017 1.539 0.6553

1987 5.299 5.107 4.496 3.293 2.208 0.7639

1988 1.896 1.85 1.658 1.314 1.119 0.5586

1989 0.9276 0.8912 0.7557 0.5475 0.4402 0.2263

1990 0.9959 0.9523 0.7972 0.5679 0.4213 0.2368

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 7.724 7.418 6.317 4.399 2.978 1.029

0.0645161290322581 6.679 6.463 5.489 4.004 2.945 1.012

0.0967741935483871 5.33 5.151 4.609 3.52 2.413 0.9258

0.129032258064516 5.299 5.107 4.496 3.293 2.208 0.9159

0.161290322580645 4.673 4.487 3.844 2.759 1.911 0.8568

0.193548387096774 4.533 4.329 3.604 2.502 1.861 0.7639

0.225806451612903 3.925 3.813 3.304 2.464 1.773 0.7309

0.258064516129032 3.461 3.373 3.093 2.391 1.723 0.697

0.290322580645161 3.438 3.316 2.96 2.257 1.672 0.6751

0.32258064516129 3.433 3.3 2.843 2.102 1.66 0.6684

0.354838709677419 2.912 2.823 2.532 2.089 1.562 0.6553

0.387096774193548 2.791 2.7 2.473 2.018 1.539 0.6134

0.419354838709677 2.754 2.679 2.283 2.017 1.495 0.5586

0.451612903225806 2.708 2.602 2.258 1.677 1.242 0.4782

0.483870967741936 2.445 2.352 2.015 1.54 1.119 0.4485

0.516129032258065 2.124 2.046 1.763 1.329 1.118 0.4426

0.548387096774194 1.978 1.923 1.669 1.314 1.066 0.4209

0.580645161290323 1.896 1.85 1.658 1.111 0.8135 0.4168

0.612903225806452 1.837 1.763 1.494 1.024 0.8055 0.3716

0.645161290322581 1.517 1.453 1.234 1.023 0.7919 0.3352

0.67741935483871 1.463 1.394 1.223 0.9652 0.763 0.3332

0.709677419354839 1.451 1.304 1.153 0.9004 0.7522 0.3331

0.741935483870968 1.345 1.301 1.115 0.8963 0.6969 0.3056

0.774193548387097 1.308 1.254 1.078 0.8671 0.675 0.3022

0.806451612903226 1.222 1.189 1.07 0.7599 0.5774 0.2368

0.838709677419355 0.9959 0.9523 0.7972 0.5679 0.4402 0.2263

0.870967741935484 0.9276 0.8912 0.7557 0.5475 0.4213 0.221

0.903225806451613 0.7003 0.6717 0.5766 0.4722 0.3708 0.1917

0.935483870967742 0.6598 0.6318 0.5354 0.3992 0.3154 0.1843

0.967741935483871 0.6153 0.6008 0.5137 0.3936 0.3072 0.1664

0.1 5.3269 5.1466 4.5977 3.4973 2.3925 0.92481

Average of yearly averages: 0.517216666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLCUCAIR

Metfile: w12844.dvf

PRZM scenario: FLcucumberSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0728 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond
161

Application Date Date 16-10 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0728 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0728 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Pepper

stored as FLPEPAIR.out

Chemical: DPXE2Y45

PRZM environment: FLpeppersSTD.txt modified Thuday, 24 May 2007 at 09:44:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.6543 0.6257 0.5531 0.5235 0.4612 0.1251

1962 4.186 4.013 3.525 2.553 2.091 0.5978

1963 2.668 2.6 2.429 1.976 1.655 0.6411

1964 4.561 4.428 4.015 3.17 2.633 0.8667

1965 4.396 4.21 3.653 2.679 2.126 0.764

1966 2.907 2.807 2.71 2.237 1.897 0.7983

1967 3.618 3.489 3.131 2.667 2.232 0.7462

1968 3.329 3.261 2.915 2.196 1.82 0.7151

1969 3.366 3.24 3.05 2.389 1.978 0.7275

1970 3.049 2.923 2.674 2.142 1.763 0.6403

1971 2.097 2.014 1.774 1.485 1.289 0.4942

1972 3.439 3.307 2.829 2.019 1.535 0.5526

1973 2.045 1.966 1.762 1.387 1.146 0.6024

1974 2.358 2.263 1.943 1.496 1.28 0.4585

1975 6.167 5.902 5.181 3.799 3.121 0.9581

1976 5.079 4.87 4.194 3.163 2.636 0.9701

1977 5.67 5.458 4.889 3.996 3.323 1.169

1978 1.534 1.475 1.274 0.9939 0.8523 0.5068

1979 8.24 7.909 6.92 5.088 4.175 1.247

1980 2.127 2.037 1.714 1.387 1.206 0.6656

1981 4.197 4.039 3.452 2.669 2.258 0.7205

1982 2.268 2.177 1.889 1.557 1.321 0.5354

1983 3.901 3.733 3.165 2.31 1.885 0.6264

1984 3.083 2.957 2.57 1.982 1.665 0.6098

1985 4.648 4.448 3.948 2.952 2.403 0.7849

1986 1.436 1.4 1.205 0.8905 0.791 0.4256

1987 3.608 3.457 3.039 2.447 2.044 0.6494

1988 1.98 1.89 1.569 1.271 1.045 0.4415

1989 1.456 1.395 1.251 1.131 0.9533 0.3651

1990 6.753 6.455 5.812 4.277 3.471 1.01

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 8.24 7.909 6.92 5.088 4.175 1.247

0.0645161290322581 6.753 6.455 5.812 4.277 3.471 1.169

0.0967741935483871 6.167 5.902 5.181 3.996 3.323 1.01

0.129032258064516 5.67 5.458 4.889 3.799 3.121 0.9701

0.161290322580645 5.079 4.87 4.194 3.17 2.636 0.9581

0.193548387096774 4.648 4.448 4.015 3.163 2.633 0.8667

0.225806451612903 4.561 4.428 3.948 2.952 2.403 0.7983

0.258064516129032 4.396 4.21 3.653 2.679 2.258 0.7849

0.290322580645161 4.197 4.039 3.525 2.669 2.232 0.764

0.32258064516129 4.186 4.013 3.452 2.667 2.126 0.7462

0.354838709677419 3.901 3.733 3.165 2.553 2.091 0.7275
162

0.387096774193548 3.618 3.489 3.131 2.447 2.044 0.7205

0.419354838709677 3.608 3.457 3.05 2.389 1.978 0.7151

0.451612903225806 3.439 3.307 3.039 2.31 1.897 0.6656

0.483870967741936 3.366 3.261 2.915 2.237 1.885 0.6494

0.516129032258065 3.329 3.24 2.829 2.196 1.82 0.6411

0.548387096774194 3.083 2.957 2.71 2.142 1.763 0.6403

0.580645161290323 3.049 2.923 2.674 2.019 1.665 0.6264

0.612903225806452 2.907 2.807 2.57 1.982 1.655 0.6098

0.645161290322581 2.668 2.6 2.429 1.976 1.535 0.6024

0.67741935483871 2.358 2.263 1.943 1.557 1.321 0.5978

0.709677419354839 2.268 2.177 1.889 1.496 1.289 0.5526

0.741935483870968 2.127 2.037 1.774 1.485 1.28 0.5354

0.774193548387097 2.097 2.014 1.762 1.387 1.206 0.5068

0.806451612903226 2.045 1.966 1.714 1.387 1.146 0.4942

0.838709677419355 1.98 1.89 1.569 1.271 1.045 0.4585

0.870967741935484 1.534 1.475 1.274 1.131 0.9533 0.4415

0.903225806451613 1.456 1.4 1.251 0.9939 0.8523 0.4256

0.935483870967742 1.436 1.395 1.205 0.8905 0.791 0.3651

0.967741935483871 0.6543 0.6257 0.5531 0.5235 0.4612 0.1251

0.1 6.1173 5.8576 5.1518 3.9763 3.3028 1.00601

Average of yearly averages: 0.6805

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLPEPAIR

Metfile: w12844.dvf

PRZM scenario: FLpeppersSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-9 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Interval 2 interval 5 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

FL Tomato

stored as FLTOMAIR.out

Chemical: DPXE2Y45

PRZM environment: FLtomatoSTD.txt modified Tueday, 29 May 2007 at 12:54:10

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30
163

Metfile: w12844.dvf modified Wedday, 3 July 2002 at 09:04:30

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.34 1.284 1.193 0.9286 0.7714 0.2653

1962 1.385 1.328 1.156 0.8875 0.7384 0.2834

1963 0.6418 0.6211 0.5326 0.3918 0.3215 0.1527

1964 1.462 1.402 1.193 0.8842 0.7777 0.3116

1965 0.8418 0.8153 0.6958 0.5021 0.4115 0.1906

1966 4.481 4.305 3.675 2.758 2.264 0.7921

1967 1.568 1.506 1.275 1.108 0.9542 0.3914

1968 0.8068 0.7736 0.6537 0.4916 0.4115 0.1654

1969 1.35 1.301 1.141 0.8942 0.8079 0.3116

1970 2.389 2.298 2.126 1.653 1.362 0.5032

1971 0.8095 0.7798 0.6594 0.5006 0.4116 0.1546

1972 0.6599 0.6332 0.5533 0.4748 0.479 0.2003

1973 0.4381 0.4212 0.3605 0.331 0.3015 0.1318

1974 1.385 1.324 1.105 0.816 0.6802 0.2443

1975 0.3674 0.352 0.3125 0.2367 0.1954 0.07378

1976 2.325 2.235 1.994 1.46 1.198 0.4127

1977 1.554 1.489 1.366 1.095 0.8979 0.307

1978 0.3821 0.3677 0.3155 0.2675 0.2271 0.09268

1979 3.905 3.739 3.156 2.279 1.837 0.6014

1980 1.455 1.396 1.189 0.9139 0.7567 0.2739

1981 1.252 1.199 1.008 0.776 0.637 0.2313

1982 1.673 1.604 1.408 1.168 0.9823 0.3472

1983 1.548 1.487 1.381 1.067 0.8736 0.3052

1984 3.303 3.169 2.688 2.103 1.788 0.625

1985 1.977 1.89 1.583 1.346 1.142 0.4007

1986 1.078 1.034 0.941 0.7408 0.6191 0.2323

1987 1.827 1.754 1.622 1.229 1.003 0.3349

1988 0.6064 0.582 0.522 0.4274 0.383 0.152

1989 0.9712 0.9469 0.8093 0.5689 0.46 0.1786

1990 0.709 0.678 0.5695 0.4212 0.3555 0.1428

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.481 4.305 3.675 2.758 2.264 0.7921

0.0645161290322581 3.905 3.739 3.156 2.279 1.837 0.625

0.0967741935483871 3.303 3.169 2.688 2.103 1.788 0.6014

0.129032258064516 2.389 2.298 2.126 1.653 1.362 0.5032

0.161290322580645 2.325 2.235 1.994 1.46 1.198 0.4127

0.193548387096774 1.977 1.89 1.622 1.346 1.142 0.4007

0.225806451612903 1.827 1.754 1.583 1.229 1.003 0.3914

0.258064516129032 1.673 1.604 1.408 1.168 0.9823 0.3472

0.290322580645161 1.568 1.506 1.381 1.108 0.9542 0.3349

0.32258064516129 1.554 1.489 1.366 1.095 0.8979 0.3116

0.354838709677419 1.548 1.487 1.275 1.067 0.8736 0.3116

0.387096774193548 1.462 1.402 1.193 0.9286 0.8079 0.307

0.419354838709677 1.455 1.396 1.193 0.9139 0.7777 0.3052

0.451612903225806 1.385 1.328 1.189 0.8942 0.7714 0.2834

0.483870967741936 1.385 1.324 1.156 0.8875 0.7567 0.2739

0.516129032258065 1.35 1.301 1.141 0.8842 0.7384 0.2653

0.548387096774194 1.34 1.284 1.105 0.816 0.6802 0.2443

0.580645161290323 1.252 1.199 1.008 0.776 0.637 0.2323

0.612903225806452 1.078 1.034 0.941 0.7408 0.6191 0.2313

0.645161290322581 0.9712 0.9469 0.8093 0.5689 0.479 0.2003

0.67741935483871 0.8418 0.8153 0.6958 0.5021 0.46 0.1906

0.709677419354839 0.8095 0.7798 0.6594 0.5006 0.4116 0.1786

0.741935483870968 0.8068 0.7736 0.6537 0.4916 0.4115 0.1654

0.774193548387097 0.709 0.678 0.5695 0.4748 0.4115 0.1546

0.806451612903226 0.6599 0.6332 0.5533 0.4274 0.383 0.1527

0.838709677419355 0.6418 0.6211 0.5326 0.4212 0.3555 0.152

0.870967741935484 0.6064 0.582 0.522 0.3918 0.3215 0.1428

0.903225806451613 0.4381 0.4212 0.3605 0.331 0.3015 0.1318

0.935483870967742 0.3821 0.3677 0.3155 0.2675 0.2271 0.09268

0.967741935483871 0.3674 0.352 0.3125 0.2367 0.1954 0.07378

0.1 3.2116 3.0819 2.6318 2.058 1.7454 0.59158

Average of yearly averages: 0.293658666666667
164

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: FLTOMAIR

Metfile: w12844.dvf

PRZM scenario: FLtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-2 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

GA Peach

stored as GAPEACHAIR.out

Chemical: DPXE2Y45

PRZM environment: GAPeachesSTD.txt modified Tueday, 29 May 2007 at 12:54:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03813.dvf modified Wedday, 3 July 2002 at 09:04:32

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.02252 0.02161 0.01836 0.01356 0.01132 0.003818

1962 0.5092 0.4873 0.4138 0.3005 0.2447 0.07906

1963 0.2125 0.2037 0.1727 0.1258 0.1028 0.03971

1964 0.8193 0.7847 0.6606 0.4745 0.3892 0.1336

1965 0.03618 0.03553 0.03295 0.02825 0.02553 0.01487

1966 0.2178 0.2098 0.1845 0.1345 0.1095 0.03679

1967 0.1794 0.1726 0.1479 0.1099 0.09099 0.03649

1968 0.6628 0.6356 0.5384 0.3874 0.3162 0.1065

1969 0.03147 0.03108 0.02946 0.02592 0.02331 0.01046

1970 0.002935 0.002823 0.00242 0.001798 0.001506 0.0008568

1971 0.2938 0.2816 0.2376 0.1716 0.1414 0.04743

1972 0.03909 0.03802 0.03282 0.02404 0.01971 0.01021

1973 0.3161 0.3033 0.2578 0.1881 0.1538 0.05052

1974 0.2436 0.2337 0.1981 0.1438 0.1177 0.04251

1975 0.03607 0.03476 0.03 0.02545 0.02218 0.01069

1976 1.602 1.549 1.335 0.977 0.7964 0.2619

1977 0.07823 0.07709 0.0725 0.06214 0.05526 0.02336

1978 0.006156 0.00593 0.005112 0.003905 0.003437 0.001869

1979 0.07724 0.07419 0.06318 0.046 0.03779 0.01261

1980 0.003594 0.003547 0.003353 0.002922 0.002631 0.001275
165

1981 0.42 0.4014 0.3362 0.2388 0.1943 0.06218

1982 0.02312 0.02276 0.02134 0.01849 0.01662 0.008801

1983 0.179 0.1717 0.1462 0.1048 0.08421 0.02701

1984 0.3066 0.2935 0.2446 0.1734 0.141 0.0482

1985 0.01429 0.01406 0.01314 0.01137 0.01021 0.004433

1986 0.0005725 0.0005623 0.0005217 0.0004464 0.000398 0.0001657

1987 0.01027 0.00984 0.008309 0.007461 0.006378 0.002134

1988 0.007133 0.006827 0.005734 0.004126 0.003368 0.001212

1989 0.2571 0.2463 0.2078 0.1506 0.1261 0.04309

1990 0.01163 0.01144 0.01067 0.009172 0.008207 0.004517

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.602 1.549 1.335 0.977 0.7964 0.2619

0.0645161290322581 0.8193 0.7847 0.6606 0.4745 0.3892 0.1336

0.0967741935483871 0.6628 0.6356 0.5384 0.3874 0.3162 0.1065

0.129032258064516 0.5092 0.4873 0.4138 0.3005 0.2447 0.07906

0.161290322580645 0.42 0.4014 0.3362 0.2388 0.1943 0.06218

0.193548387096774 0.3161 0.3033 0.2578 0.1881 0.1538 0.05052

0.225806451612903 0.3066 0.2935 0.2446 0.1734 0.1414 0.0482

0.258064516129032 0.2938 0.2816 0.2376 0.1716 0.141 0.04743

0.290322580645161 0.2571 0.2463 0.2078 0.1506 0.1261 0.04309

0.32258064516129 0.2436 0.2337 0.1981 0.1438 0.1177 0.04251

0.354838709677419 0.2178 0.2098 0.1845 0.1345 0.1095 0.03971

0.387096774193548 0.2125 0.2037 0.1727 0.1258 0.1028 0.03679

0.419354838709677 0.1794 0.1726 0.1479 0.1099 0.09099 0.03649

0.451612903225806 0.179 0.1717 0.1462 0.1048 0.08421 0.02701

0.483870967741936 0.07823 0.07709 0.0725 0.06214 0.05526 0.02336

0.516129032258065 0.07724 0.07419 0.06318 0.046 0.03779 0.01487

0.548387096774194 0.03909 0.03802 0.03295 0.02825 0.02553 0.01261

0.580645161290323 0.03618 0.03553 0.03282 0.02592 0.02331 0.01069

0.612903225806452 0.03607 0.03476 0.03 0.02545 0.02218 0.01046

0.645161290322581 0.03147 0.03108 0.02946 0.02404 0.01971 0.01021

0.67741935483871 0.02312 0.02276 0.02134 0.01849 0.01662 0.008801

0.709677419354839 0.02252 0.02161 0.01836 0.01356 0.01132 0.004517

0.741935483870968 0.01429 0.01406 0.01314 0.01137 0.01021 0.004433

0.774193548387097 0.01163 0.01144 0.01067 0.009172 0.008207 0.003818

0.806451612903226 0.01027 0.00984 0.008309 0.007461 0.006378 0.002134

0.838709677419355 0.007133 0.006827 0.005734 0.004126 0.003437 0.001869

0.870967741935484 0.006156 0.00593 0.005112 0.003905 0.003368 0.001275

0.903225806451613 0.003594 0.003547 0.003353 0.002922 0.002631 0.001212

0.935483870967742 0.002935 0.002823 0.00242 0.001798 0.001506 0.0008568

0.967741935483871 0.0005725 0.0005623 0.0005217 0.0004464 0.000398 0.0001657

0.1 0.64744 0.62077 0.52594 0.37871 0.30905 0.103756

Average of yearly averages: 0.0375423833333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: GAPEACHAIR

Metfile: w03813.dvf

PRZM scenario: GAPeachesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha
166

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

ID Potato

stored as IDPOTAIR.out

Chemical: DPXE2Y45

PRZM environment: IDNpotato_WirrigSTD.txt modified Tueday, 29 May 2007 at 12:55:22

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24156.dvf modified Wedday, 3 July 2002 at 09:04:38

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.2489 0.2399 0.207 0.1597 0.1332 0.047

1962 0.02675 0.02674 0.02669 0.02642 0.02522 0.01483

1963 0.4366 0.4231 0.3942 0.3268 0.2772 0.1054

1964 0.2516 0.2434 0.2134 0.1708 0.1487 0.07011

1965 0.03431 0.03324 0.03059 0.02738 0.02595 0.01762

1966 0.1075 0.1034 0.08842 0.07783 0.07168 0.02899

1967 0.2465 0.2379 0.2066 0.172 0.1502 0.05835

1968 0.1702 0.1643 0.147 0.1269 0.1076 0.04618

1969 0.2758 0.2661 0.2347 0.1879 0.156 0.06241

1970 0.7912 0.7629 0.6633 0.5171 0.4292 0.1577

1971 0.5256 0.5112 0.4522 0.348 0.2919 0.1291

1972 0.3606 0.3516 0.3077 0.2333 0.1986 0.08671

1973 0.131 0.1261 0.1126 0.0876 0.07293 0.03681

1974 0.7437 0.7176 0.6202 0.4636 0.4282 0.1753

1975 0.2482 0.2401 0.2106 0.1632 0.1381 0.07373

1976 0.7897 0.7627 0.6638 0.4944 0.4116 0.1505

1977 0.3285 0.3182 0.283 0.2242 0.1888 0.08505

1978 0.3748 0.362 0.3144 0.2349 0.1934 0.07609

1979 0.04437 0.04437 0.04436 0.04423 0.042 0.02444

1980 0.1061 0.1039 0.0962 0.07757 0.06473 0.02551

1981 0.4213 0.4077 0.3608 0.2708 0.2259 0.08883

1982 0.2168 0.2095 0.1832 0.1477 0.1369 0.0692

1983 0.1678 0.1621 0.1482 0.1277 0.1109 0.05075

1984 0.5217 0.5044 0.4402 0.3401 0.2932 0.1133

1985 0.3955 0.3806 0.3269 0.2506 0.213 0.09303

1986 0.1327 0.1286 0.118 0.1066 0.09446 0.04437

1987 0.1677 0.1617 0.1437 0.1116 0.09382 0.03634

1988 0.0302 0.02956 0.02819 0.02236 0.01864 0.01153

1989 0.03252 0.0318 0.03019 0.0268 0.02316 0.009865

1990 0.1084 0.1042 0.08992 0.07226 0.06059 0.02267

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.7912 0.7629 0.6638 0.5171 0.4292 0.1753

0.0645161290322581 0.7897 0.7627 0.6633 0.4944 0.4282 0.1577

0.0967741935483871 0.7437 0.7176 0.6202 0.4636 0.4116 0.1505

0.129032258064516 0.5256 0.5112 0.4522 0.348 0.2932 0.1291

0.161290322580645 0.5217 0.5044 0.4402 0.3401 0.2919 0.1133

0.193548387096774 0.4366 0.4231 0.3942 0.3268 0.2772 0.1054

0.225806451612903 0.4213 0.4077 0.3608 0.2708 0.2259 0.09303

0.258064516129032 0.3955 0.3806 0.3269 0.2506 0.213 0.08883

0.290322580645161 0.3748 0.362 0.3144 0.2349 0.1986 0.08671

0.32258064516129 0.3606 0.3516 0.3077 0.2333 0.1934 0.08505
167

0.354838709677419 0.3285 0.3182 0.283 0.2242 0.1888 0.07609

0.387096774193548 0.2758 0.2661 0.2347 0.1879 0.156 0.07373

0.419354838709677 0.2516 0.2434 0.2134 0.172 0.1502 0.07011

0.451612903225806 0.2489 0.2401 0.2106 0.1708 0.1487 0.0692

0.483870967741936 0.2482 0.2399 0.207 0.1632 0.1381 0.06241

0.516129032258065 0.2465 0.2379 0.2066 0.1597 0.1369 0.05835

0.548387096774194 0.2168 0.2095 0.1832 0.1477 0.1332 0.05075

0.580645161290323 0.1702 0.1643 0.1482 0.1277 0.1109 0.047

0.612903225806452 0.1678 0.1621 0.147 0.1269 0.1076 0.04618

0.645161290322581 0.1677 0.1617 0.1437 0.1116 0.09446 0.04437

0.67741935483871 0.1327 0.1286 0.118 0.1066 0.09382 0.03681

0.709677419354839 0.131 0.1261 0.1126 0.0876 0.07293 0.03634

0.741935483870968 0.1084 0.1042 0.0962 0.07783 0.07168 0.02899

0.774193548387097 0.1075 0.1039 0.08992 0.07757 0.06473 0.02551

0.806451612903226 0.1061 0.1034 0.08842 0.07226 0.06059 0.02444

0.838709677419355 0.04437 0.04437 0.04436 0.04423 0.042 0.02267

0.870967741935484 0.03431 0.03324 0.03059 0.02738 0.02595 0.01762

0.903225806451613 0.03252 0.0318 0.03019 0.0268 0.02522 0.01483

0.935483870967742 0.0302 0.02956 0.02819 0.02642 0.02316 0.01153

0.967741935483871 0.02675 0.02674 0.02669 0.02236 0.01864 0.009865

0.1 0.72189 0.69696 0.6034 0.45204 0.39976 0.14836

Average of yearly averages: 0.0670571666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: IDPOTAIR

Metfile: w24156.dvf

PRZM scenario: IDNpotato_WirrigSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0739 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 3 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0739 kg/ha

Interval 2 interval 3 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0739 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

ME Potato

stored as MEPOTAIR.out
168

Chemical: DPXE2Y45

PRZM environment: MEpotatoSTD.txt modified Tueday, 29 May 2007 at 12:56:18

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14607.dvf modified Wedday, 3 July 2002 at 09:05:36

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.6326 0.6151 0.553 0.5172 0.4721 0.1818

1962 1.201 1.167 1.089 0.9068 0.8224 0.4979

1963 0.7287 0.7108 0.6893 0.6381 0.6327 0.5198

1964 0.6345 0.6318 0.5914 0.5664 0.5048 0.4077

1965 0.6265 0.624 0.6145 0.5978 0.5886 0.3958

1966 0.6411 0.6253 0.5661 0.517 0.4522 0.2879

1967 0.7453 0.7254 0.6707 0.6251 0.5909 0.4619

1968 0.8265 0.8225 0.8073 0.7425 0.6512 0.5029

1969 0.9986 0.9724 0.8765 0.761 0.7523 0.6326

1970 1.271 1.235 1.108 0.9079 0.8273 0.5586

1971 0.6565 0.656 0.6539 0.6511 0.6498 0.4277

1972 0.9642 0.939 0.8534 0.7571 0.705 0.4899

1973 1.076 1.045 0.94 0.7777 0.6898 0.5376

1974 0.5972 0.5953 0.5878 0.5759 0.5751 0.4146

1975 0.4996 0.4871 0.4413 0.3833 0.3685 0.3001

1976 1.313 1.278 1.15 1.08 1.007 0.5891

1977 1.134 1.105 1.04 0.8991 0.8337 0.6515

1978 0.997 0.9726 0.8928 0.7317 0.6555 0.4883

1979 0.6894 0.6699 0.6259 0.5179 0.471 0.3925

1980 0.5623 0.5481 0.4984 0.4227 0.3939 0.3342

1981 2.152 2.081 1.834 1.462 1.296 0.6495

1982 1.076 1.046 0.9852 0.9057 0.8992 0.7255

1983 1.125 1.095 0.9821 0.9226 0.8439 0.5942

1984 0.9831 0.9605 0.8881 0.8154 0.7351 0.5277

1985 0.4016 0.3904 0.3638 0.3324 0.3275 0.2644

1986 0.774 0.7522 0.6763 0.6074 0.5576 0.3661

1987 0.4946 0.4925 0.4678 0.4322 0.4279 0.3681

1988 0.4614 0.4498 0.424 0.4036 0.4009 0.3261

1989 1.117 1.094 0.97 0.7867 0.6878 0.3926

1990 1.142 1.115 1.038 0.9899 0.9198 0.6626

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 2.152 2.081 1.834 1.462 1.296 0.7255

0.0645161290322581 1.313 1.278 1.15 1.08 1.007 0.6626

0.0967741935483871 1.271 1.235 1.108 0.9899 0.9198 0.6515

0.129032258064516 1.201 1.167 1.089 0.9226 0.8992 0.6495

0.161290322580645 1.142 1.115 1.04 0.9079 0.8439 0.6326

0.193548387096774 1.134 1.105 1.038 0.9068 0.8337 0.5942

0.225806451612903 1.125 1.095 0.9852 0.9057 0.8273 0.5891

0.258064516129032 1.117 1.094 0.9821 0.8991 0.8224 0.5586

0.290322580645161 1.076 1.046 0.97 0.8154 0.7523 0.5376

0.32258064516129 1.076 1.045 0.94 0.7867 0.7351 0.5277

0.354838709677419 0.9986 0.9726 0.8928 0.7777 0.705 0.5198

0.387096774193548 0.997 0.9724 0.8881 0.761 0.6898 0.5029

0.419354838709677 0.9831 0.9605 0.8765 0.7571 0.6878 0.4979

0.451612903225806 0.9642 0.939 0.8534 0.7425 0.6555 0.4899

0.483870967741936 0.8265 0.8225 0.8073 0.7317 0.6512 0.4883

0.516129032258065 0.774 0.7522 0.6893 0.6511 0.6498 0.4619

0.548387096774194 0.7453 0.7254 0.6763 0.6381 0.6327 0.4277

0.580645161290323 0.7287 0.7108 0.6707 0.6251 0.5909 0.4146

0.612903225806452 0.6894 0.6699 0.6539 0.6074 0.5886 0.4077

0.645161290322581 0.6565 0.656 0.6259 0.5978 0.5751 0.3958

0.67741935483871 0.6411 0.6318 0.6145 0.5759 0.5576 0.3926

0.709677419354839 0.6345 0.6253 0.5914 0.5664 0.5048 0.3925

0.741935483870968 0.6326 0.624 0.5878 0.5179 0.4721 0.3681

0.774193548387097 0.6265 0.6151 0.5661 0.5172 0.471 0.3661

0.806451612903226 0.5972 0.5953 0.553 0.517 0.4522 0.3342

0.838709677419355 0.5623 0.5481 0.4984 0.4322 0.4279 0.3261

0.870967741935484 0.4996 0.4925 0.4678 0.4227 0.4009 0.3001

0.903225806451613 0.4946 0.4871 0.4413 0.4036 0.3939 0.2879

0.935483870967742 0.4614 0.4498 0.424 0.3833 0.3685 0.2644

0.967741935483871 0.4016 0.3904 0.3638 0.3324 0.3275 0.1818
169

0.1 1.264 1.2282 1.1061 0.98317 0.91774 0.6513

Average of yearly averages: 0.464973333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MEPOTAIR

Metfile: w14607.dvf

PRZM scenario: MEpotatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.0739 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-6 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.0739 kg/ha

Interval 2 interval 5 days Set to 0 or delete line for single app.

app. rate 2 apprate 0.0739 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

MI Cherry

stored as MICHEAIR.out

Chemical: DPXE2Y45

PRZM environment: MICherriesSTD.txt modified Tueday, 29 May 2007 at 12:56:56

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14850.dvf modified Wedday, 3 July 2002 at 09:05:40

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1207 0.1167 0.1036 0.08319 0.07244 0.02514

1962 0.3802 0.3669 0.3197 0.2475 0.2112 0.09509

1963 0.9877 0.9578 0.8474 0.6579 0.5577 0.2332

1964 0.2901 0.2804 0.2448 0.2085 0.1829 0.1282

1965 0.1284 0.1254 0.1161 0.1047 0.1002 0.07545

1966 0.2056 0.1993 0.1752 0.1529 0.1391 0.0788

1967 0.1744 0.1696 0.1558 0.1452 0.1323 0.09175

1968 0.1238 0.1197 0.1048 0.09173 0.08106 0.04785

1969 0.6966 0.6747 0.6152 0.5291 0.4482 0.1725

1970 0.2086 0.203 0.1817 0.1656 0.148 0.1127

1971 0.125 0.121 0.1069 0.1005 0.1 0.07095

1972 0.2863 0.2768 0.2588 0.2086 0.1817 0.09549

1973 0.1131 0.1096 0.0994 0.08397 0.08023 0.06214

1974 0.3312 0.3213 0.2819 0.2277 0.1966 0.09479
170

1975 0.2823 0.274 0.2515 0.2041 0.1757 0.09614

1976 0.1366 0.1319 0.1149 0.09806 0.0941 0.06592

1977 0.1734 0.1682 0.151 0.1316 0.1183 0.06979

1978 0.5265 0.5088 0.4475 0.3563 0.3067 0.1495

1979 0.2534 0.2464 0.2207 0.1903 0.1828 0.1308

1980 0.19 0.184 0.1622 0.1265 0.109 0.07802

1981 0.4332 0.4187 0.3834 0.3282 0.3205 0.1492

1982 0.7982 0.7748 0.6776 0.5205 0.4449 0.2128

1983 0.3774 0.3675 0.3455 0.3024 0.2983 0.1934

1984 0.1507 0.1464 0.1312 0.122 0.1217 0.09616

1985 0.6627 0.6385 0.5535 0.4775 0.4297 0.1764

1986 1.033 1.01 0.9453 0.7532 0.6448 0.3176

1987 0.751 0.7274 0.6444 0.5313 0.4681 0.2604

1988 0.2425 0.2425 0.2424 0.2421 0.2417 0.1464

1989 0.6121 0.5922 0.5184 0.4183 0.3626 0.1599

1990 0.3184 0.3085 0.2879 0.2304 0.2011 0.1149

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.033 1.01 0.9453 0.7532 0.6448 0.3176

0.0645161290322581 0.9877 0.9578 0.8474 0.6579 0.5577 0.2604

0.0967741935483871 0.7982 0.7748 0.6776 0.5313 0.4681 0.2332

0.129032258064516 0.751 0.7274 0.6444 0.5291 0.4482 0.2128

0.161290322580645 0.6966 0.6747 0.6152 0.5205 0.4449 0.1934

0.193548387096774 0.6627 0.6385 0.5535 0.4775 0.4297 0.1764

0.225806451612903 0.6121 0.5922 0.5184 0.4183 0.3626 0.1725

0.258064516129032 0.5265 0.5088 0.4475 0.3563 0.3205 0.1599

0.290322580645161 0.4332 0.4187 0.3834 0.3282 0.3067 0.1495

0.32258064516129 0.3802 0.3675 0.3455 0.3024 0.2983 0.1492

0.354838709677419 0.3774 0.3669 0.3197 0.2475 0.2417 0.1464

0.387096774193548 0.3312 0.3213 0.2879 0.2421 0.2112 0.1308

0.419354838709677 0.3184 0.3085 0.2819 0.2304 0.2011 0.1282

0.451612903225806 0.2901 0.2804 0.2588 0.2277 0.1966 0.1149

0.483870967741936 0.2863 0.2768 0.2515 0.2086 0.1829 0.1127

0.516129032258065 0.2823 0.274 0.2448 0.2085 0.1828 0.09616

0.548387096774194 0.2534 0.2464 0.2424 0.2041 0.1817 0.09614

0.580645161290323 0.2425 0.2425 0.2207 0.1903 0.1757 0.09549

0.612903225806452 0.2086 0.203 0.1817 0.1656 0.148 0.09509

0.645161290322581 0.2056 0.1993 0.1752 0.1529 0.1391 0.09479

0.67741935483871 0.19 0.184 0.1622 0.1452 0.1323 0.09175

0.709677419354839 0.1744 0.1696 0.1558 0.1316 0.1217 0.0788

0.741935483870968 0.1734 0.1682 0.151 0.1265 0.1183 0.07802

0.774193548387097 0.1507 0.1464 0.1312 0.122 0.109 0.07545

0.806451612903226 0.1366 0.1319 0.1161 0.1047 0.1002 0.07095

0.838709677419355 0.1284 0.1254 0.1149 0.1005 0.1 0.06979

0.870967741935484 0.125 0.121 0.1069 0.09806 0.0941 0.06592

0.903225806451613 0.1238 0.1197 0.1048 0.09173 0.08106 0.06214

0.935483870967742 0.1207 0.1167 0.1036 0.08397 0.08023 0.04785

0.967741935483871 0.1131 0.1096 0.0994 0.08319 0.07244 0.02514

0.1 0.79348 0.77006 0.67428 0.53108 0.46611 0.23116

Average of yearly averages: 0.126712666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MICHEAIR

Metfile: w14850.dvf

PRZM scenario: MICherriesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife
171

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

MS Cotton

stored as MSCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: MScottonSTD.txt modified Tueday, 29 May 2007 at 12:57:52

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w03940.dvf modified Wedday, 3 July 2002 at 09:05:46

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 1.472 1.411 1.192 0.9872 0.8817 0.3144

1962 0.2865 0.2755 0.2575 0.2034 0.1975 0.1118

1963 2.079 1.997 1.702 1.289 1.103 0.4056

1964 0.5399 0.5226 0.4757 0.428 0.3885 0.1824

1965 0.1581 0.1526 0.1332 0.1068 0.1004 0.06473

1966 3.353 3.295 2.935 2.139 1.743 0.5837

1967 2.984 2.866 2.516 2.105 1.813 0.6914

1968 1.76 1.691 1.615 1.249 1.033 0.3916

1969 0.2519 0.2438 0.225 0.2035 0.1929 0.1113

1970 0.5862 0.5704 0.4906 0.421 0.3763 0.1598

1971 2.581 2.475 2.106 1.559 1.281 0.4411

1972 1.541 1.489 1.337 1.07 0.9112 0.3444

1973 1.572 1.508 1.348 1.091 0.9081 0.3334

1974 1.135 1.088 0.9187 0.6644 0.556 0.2289

1975 2.407 2.319 2.17 1.718 1.44 0.5158

1976 3.641 3.503 3.229 2.595 2.196 0.778

1977 0.9365 0.9051 0.8052 0.6773 0.6399 0.295

1978 3.048 2.935 2.751 2.127 1.748 0.6135

1979 2.647 2.541 2.162 1.964 1.825 0.7129

1980 2.135 2.061 1.887 1.394 1.143 0.4411

1981 1.869 1.795 1.669 1.297 1.074 0.3788

1982 2.794 2.677 2.294 1.796 1.484 0.5082

1983 5.026 4.862 4.199 3.213 2.649 0.9204

1984 1.131 1.086 0.9877 0.9084 0.8064 0.3501

1985 0.4351 0.4186 0.3818 0.3327 0.3077 0.1346

1986 2.195 2.11 1.858 1.396 1.159 0.3982

1987 1.174 1.13 1.002 0.8294 0.7743 0.3145

1988 0.6382 0.6131 0.5313 0.4528 0.4187 0.1846

1989 3.347 3.227 2.822 2.327 2.042 0.7556

1990 2.531 2.436 2.173 1.704 1.407 0.5146

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 5.026 4.862 4.199 3.213 2.649 0.9204

0.0645161290322581 3.641 3.503 3.229 2.595 2.196 0.778

0.0967741935483871 3.353 3.295 2.935 2.327 2.042 0.7556

0.129032258064516 3.347 3.227 2.822 2.139 1.825 0.7129

0.161290322580645 3.048 2.935 2.751 2.127 1.813 0.6914

0.193548387096774 2.984 2.866 2.516 2.105 1.748 0.6135

0.225806451612903 2.794 2.677 2.294 1.964 1.743 0.5837

0.258064516129032 2.647 2.541 2.173 1.796 1.484 0.5158
172

0.290322580645161 2.581 2.475 2.17 1.718 1.44 0.5146

0.32258064516129 2.531 2.436 2.162 1.704 1.407 0.5082

0.354838709677419 2.407 2.319 2.106 1.559 1.281 0.4411

0.387096774193548 2.195 2.11 1.887 1.396 1.159 0.4411

0.419354838709677 2.135 2.061 1.858 1.394 1.143 0.4056

0.451612903225806 2.079 1.997 1.702 1.297 1.103 0.3982

0.483870967741936 1.869 1.795 1.669 1.289 1.074 0.3916

0.516129032258065 1.76 1.691 1.615 1.249 1.033 0.3788

0.548387096774194 1.572 1.508 1.348 1.091 0.9112 0.3501

0.580645161290323 1.541 1.489 1.337 1.07 0.9081 0.3444

0.612903225806452 1.472 1.411 1.192 0.9872 0.8817 0.3334

0.645161290322581 1.174 1.13 1.002 0.9084 0.8064 0.3145

0.67741935483871 1.135 1.088 0.9877 0.8294 0.7743 0.3144

0.709677419354839 1.131 1.086 0.9187 0.6773 0.6399 0.295

0.741935483870968 0.9365 0.9051 0.8052 0.6644 0.556 0.2289

0.774193548387097 0.6382 0.6131 0.5313 0.4528 0.4187 0.1846

0.806451612903226 0.5862 0.5704 0.4906 0.428 0.3885 0.1824

0.838709677419355 0.5399 0.5226 0.4757 0.421 0.3763 0.1598

0.870967741935484 0.4351 0.4186 0.3818 0.3327 0.3077 0.1346

0.903225806451613 0.2865 0.2755 0.2575 0.2035 0.1975 0.1118

0.935483870967742 0.2519 0.2438 0.225 0.2034 0.1929 0.1113

0.967741935483871 0.1581 0.1526 0.1332 0.1068 0.1004 0.06473

0.1 3.3524 3.2882 2.9237 2.3082 2.0203 0.75133

Average of yearly averages: 0.406014333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: MSCOTAIR

Metfile: w03940.dvf

PRZM scenario: MScottonSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-5 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

NC Apple

stored as NCAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: NCappleSTD.txt modified Tueday, 29 May 2007 at 12:58:16

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30
173

Metfile: w03812.dvf modified Wedday, 3 July 2002 at 09:05:50

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1965 0.2081 0.2004 0.174 0.1488 0.1318 0.04861

1966 0.3098 0.2987 0.2602 0.201 0.1674 0.06324

1967 0.2056 0.1983 0.1796 0.1541 0.1317 0.05144

1968 0.0924 0.08905 0.08136 0.06371 0.05563 0.02621

1969 0.5727 0.5508 0.471 0.3602 0.2998 0.1064

1970 0.2395 0.2339 0.2022 0.1508 0.1264 0.05254

1971 0.184 0.1772 0.1567 0.1243 0.1052 0.04228

1972 0.6106 0.5885 0.5275 0.3974 0.3287 0.1177

1973 1.439 1.387 1.223 0.9348 0.7808 0.2906

1974 0.7027 0.6758 0.6273 0.57 0.5009 0.2033

1975 0.6573 0.6381 0.5715 0.4371 0.3647 0.1372

1976 0.4772 0.4618 0.4051 0.3355 0.2833 0.1075

1977 0.6581 0.6333 0.5435 0.4317 0.3636 0.1375

1978 0.2884 0.2774 0.2614 0.2035 0.1689 0.06728

1979 0.7969 0.7666 0.6924 0.5499 0.4719 0.1767

1980 1.019 0.9871 0.8442 0.6712 0.5661 0.2064

1981 0.08236 0.07965 0.07188 0.06298 0.05382 0.02985

1982 0.2079 0.2 0.1747 0.1362 0.1145 0.04261

1983 0.6179 0.5959 0.5324 0.4714 0.406 0.1472

1984 0.3829 0.3691 0.3248 0.2608 0.2322 0.09522

1985 0.1878 0.1804 0.1537 0.1156 0.09904 0.04376

1986 0.1736 0.1672 0.1459 0.1075 0.08837 0.0326

1987 0.4314 0.4149 0.3552 0.3048 0.2886 0.1121

1988 0.4593 0.4415 0.3774 0.2769 0.2269 0.09005

1989 0.2706 0.2604 0.2253 0.1715 0.145 0.05667

1990 0.3391 0.3267 0.289 0.2256 0.1876 0.07031

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.037037037037037 1.439 1.387 1.223 0.9348 0.7808 0.2906

0.0740740740740741 1.019 0.9871 0.8442 0.6712 0.5661 0.2064

0.111111111111111 0.7969 0.7666 0.6924 0.57 0.5009 0.2033

0.148148148148148 0.7027 0.6758 0.6273 0.5499 0.4719 0.1767

0.185185185185185 0.6581 0.6381 0.5715 0.4714 0.406 0.1472

0.222222222222222 0.6573 0.6333 0.5435 0.4371 0.3647 0.1375

0.259259259259259 0.6179 0.5959 0.5324 0.4317 0.3636 0.1372

0.296296296296296 0.6106 0.5885 0.5275 0.3974 0.3287 0.1177

0.333333333333333 0.5727 0.5508 0.471 0.3602 0.2998 0.1121

0.37037037037037 0.4772 0.4618 0.4051 0.3355 0.2886 0.1075

0.407407407407407 0.4593 0.4415 0.3774 0.3048 0.2833 0.1064

0.444444444444444 0.4314 0.4149 0.3552 0.2769 0.2322 0.09522

0.481481481481481 0.3829 0.3691 0.3248 0.2608 0.2269 0.09005

0.518518518518518 0.3391 0.3267 0.289 0.2256 0.1876 0.07031

0.555555555555556 0.3098 0.2987 0.2614 0.2035 0.1689 0.06728

0.592592592592593 0.2884 0.2774 0.2602 0.201 0.1674 0.06324

0.62962962962963 0.2706 0.2604 0.2253 0.1715 0.145 0.05667

0.666666666666667 0.2395 0.2339 0.2022 0.1541 0.1318 0.05254

0.703703703703704 0.2081 0.2004 0.1796 0.1508 0.1317 0.05144

0.740740740740741 0.2079 0.2 0.1747 0.1488 0.1264 0.04861

0.777777777777778 0.2056 0.1983 0.174 0.1362 0.1145 0.04376

0.814814814814815 0.1878 0.1804 0.1567 0.1243 0.1052 0.04261

0.851851851851852 0.184 0.1772 0.1537 0.1156 0.09904 0.04228

0.888888888888889 0.1736 0.1672 0.1459 0.1075 0.08837 0.0326

0.925925925925926 0.0924 0.08905 0.08136 0.06371 0.05563 0.02985

0.962962962962963 0.08236 0.07965 0.07188 0.06298 0.05382 0.02621

0.1 0.86353 0.83275 0.73794 0.60036 0.52046 0.20423

Average of yearly averages: 0.0982796153846154

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: NCAPPAIR

Metfile: w03812.dvf

PRZM scenario: NCappleSTD.txt

EXAMS environment file: pond298.exv
174

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

NC Cotton

stored as NCCOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NCcottonSTD.txt modified Tueday, 29 May 2007 at 12:58:38

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w13722.dvf modified Wedday, 3 July 2002 at 09:05:50

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.7135 0.6934 0.6327 0.5246 0.4925 0.2002

1962 2.02 1.95 1.84 1.539 1.378 0.5803

1963 1.164 1.121 0.9622 0.7417 0.5719 0.2872

1964 1.261 1.216 1.085 1.04 0.9243 0.5209

1965 4.19 4.045 3.588 3.094 2.668 1.033

1966 1.68 1.624 1.446 1.229 1.189 0.6223

1967 2.975 2.879 2.678 2.29 2.088 0.8591

1968 1.249 1.219 1.065 0.8683 0.7832 0.4749

1969 1.466 1.417 1.311 1.091 1.026 0.5336

1970 1.339 1.292 1.2 1.145 1.021 0.4578

1971 1.083 1.051 0.922 0.8903 0.8568 0.448

1972 2.036 1.992 1.8 1.765 1.629 0.6948

1973 3.854 3.714 3.215 2.608 2.228 0.8639

1974 1.045 1.011 0.8885 0.7825 0.6863 0.3935

1975 2.132 2.055 1.785 1.338 1.187 0.5172

1976 1.481 1.425 1.224 1.065 0.9436 0.4082

1977 1.576 1.517 1.333 1.122 1.035 0.5277

1978 1.494 1.441 1.25 1.068 0.9838 0.5358

1979 1.406 1.364 1.237 1.105 1.103 0.5712

1980 2.184 2.098 1.795 1.338 1.178 0.5477

1981 1.76 1.696 1.474 1.35 1.265 0.5703

1982 3.269 3.169 2.808 2.274 1.96 0.8478

1983 0.6457 0.6255 0.5717 0.5346 0.4732 0.3403

1984 1.894 1.826 1.684 1.311 1.104 0.5025

1985 1.222 1.193 1.046 0.9194 0.8519 0.4324

1986 2.009 1.939 1.749 1.363 1.175 0.5107

1987 1.593 1.535 1.382 1.122 0.9431 0.4507

1988 1.03 0.994 0.9227 0.7782 0.7012 0.3615
175

1989 1.081 1.045 0.9813 0.9215 0.8873 0.4376

1990 0.8048 0.7737 0.6763 0.5171 0.4287 0.2047

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 4.19 4.045 3.588 3.094 2.668 1.033

0.0645161290322581 3.854 3.714 3.215 2.608 2.228 0.8639

0.0967741935483871 3.269 3.169 2.808 2.29 2.088 0.8591

0.129032258064516 2.975 2.879 2.678 2.274 1.96 0.8478

0.161290322580645 2.184 2.098 1.84 1.765 1.629 0.6948

0.193548387096774 2.132 2.055 1.8 1.539 1.378 0.6223

0.225806451612903 2.036 1.992 1.795 1.363 1.265 0.5803

0.258064516129032 2.02 1.95 1.785 1.35 1.189 0.5712

0.290322580645161 2.009 1.939 1.749 1.338 1.187 0.5703

0.32258064516129 1.894 1.826 1.684 1.338 1.178 0.5477

0.354838709677419 1.76 1.696 1.474 1.311 1.175 0.5358

0.387096774193548 1.68 1.624 1.446 1.229 1.104 0.5336

0.419354838709677 1.593 1.535 1.382 1.145 1.103 0.5277

0.451612903225806 1.576 1.517 1.333 1.122 1.035 0.5209

0.483870967741936 1.494 1.441 1.311 1.122 1.026 0.5172

0.516129032258065 1.481 1.425 1.25 1.105 1.021 0.5107

0.548387096774194 1.466 1.417 1.237 1.091 0.9838 0.5025

0.580645161290323 1.406 1.364 1.224 1.068 0.9436 0.4749

0.612903225806452 1.339 1.292 1.2 1.065 0.9431 0.4578

0.645161290322581 1.261 1.219 1.085 1.04 0.9243 0.4507

0.67741935483871 1.249 1.216 1.065 0.9215 0.8873 0.448

0.709677419354839 1.222 1.193 1.046 0.9194 0.8568 0.4376

0.741935483870968 1.164 1.121 0.9813 0.8903 0.8519 0.4324

0.774193548387097 1.083 1.051 0.9622 0.8683 0.7832 0.4082

0.806451612903226 1.081 1.045 0.9227 0.7825 0.7012 0.3935

0.838709677419355 1.045 1.011 0.922 0.7782 0.6863 0.3615

0.870967741935484 1.03 0.994 0.8885 0.7417 0.5719 0.3403

0.903225806451613 0.8048 0.7737 0.6763 0.5346 0.4925 0.2872

0.935483870967742 0.7135 0.6934 0.6327 0.5246 0.4732 0.2047

0.967741935483871 0.6457 0.6255 0.5717 0.5171 0.4287 0.2002

0.1 3.2396 3.14 2.795 2.2884 2.0752 0.85797

Average of yearly averages: 0.524526666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: NCCOTAIR

Metfile: w13722.dvf

PRZM scenario: NCcottonSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-6 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF
176

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

NY Grape

stored as CACOTAIR.out

Chemical: DPXE2Y45

PRZM environment: NYGrapesSTD.txt modified Tueday, 29 May 2007 at 12:59:44

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14860.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1127 0.1099 0.0995 0.08593 0.08161 0.04125

1962 1.107 1.075 0.9791 0.8028 0.7724 0.3429

1963 0.3513 0.3513 0.3512 0.3496 0.3343 0.202

1964 0.7512 0.7257 0.6324 0.4844 0.4113 0.2081

1965 0.4647 0.4487 0.3903 0.3102 0.2742 0.1818

1966 0.4894 0.4748 0.4212 0.3531 0.3448 0.1923

1967 1.09 1.055 0.9393 0.7441 0.644 0.2896

1968 0.2481 0.248 0.2472 0.2433 0.2338 0.1319

1969 0.147 0.1432 0.1289 0.1061 0.09827 0.07231

1970 0.7079 0.6842 0.6383 0.5018 0.4529 0.1922

1971 0.4809 0.4658 0.4095 0.3341 0.2994 0.2029

1972 0.8107 0.7877 0.7301 0.611 0.5291 0.2556

1973 0.8589 0.8368 0.7537 0.6201 0.5574 0.2885

1974 0.7993 0.7786 0.6817 0.5402 0.4839 0.2714

1975 0.6302 0.6115 0.5633 0.4563 0.415 0.2765

1976 0.4286 0.4202 0.3749 0.3211 0.2831 0.1855

1977 0.5302 0.5227 0.491 0.4267 0.397 0.2001

1978 0.4496 0.4349 0.4033 0.366 0.3424 0.2013

1979 0.7436 0.7196 0.6346 0.5594 0.5463 0.3021

1980 1.038 1.01 0.9045 0.8181 0.7545 0.4415

1981 0.3785 0.3785 0.3784 0.3765 0.3595 0.2498

1982 0.7478 0.7297 0.66 0.5534 0.4973 0.2519

1983 0.8111 0.7855 0.7384 0.6374 0.5913 0.2979

1984 0.7624 0.7417 0.6735 0.5429 0.4918 0.299

1985 0.6575 0.6397 0.5904 0.539 0.4901 0.2772

1986 1.313 1.278 1.153 0.9386 0.8146 0.4498

1987 0.4808 0.4666 0.4163 0.3771 0.354 0.2751

1988 0.2952 0.2852 0.2571 0.2329 0.2229 0.1451

1989 0.5858 0.5744 0.5132 0.4043 0.3677 0.2033

1990 0.5559 0.5397 0.509 0.4268 0.3682 0.1747

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.313 1.278 1.153 0.9386 0.8146 0.4498

0.0645161290322581 1.107 1.075 0.9791 0.8181 0.7724 0.4415

0.0967741935483871 1.09 1.055 0.9393 0.8028 0.7545 0.3429

0.129032258064516 1.038 1.01 0.9045 0.7441 0.644 0.3021

0.161290322580645 0.8589 0.8368 0.7537 0.6374 0.5913 0.299

0.193548387096774 0.8111 0.7877 0.7384 0.6201 0.5574 0.2979

0.225806451612903 0.8107 0.7855 0.7301 0.611 0.5463 0.2896

0.258064516129032 0.7993 0.7786 0.6817 0.5594 0.5291 0.2885

0.290322580645161 0.7624 0.7417 0.6735 0.5534 0.4973 0.2772

0.32258064516129 0.7512 0.7297 0.66 0.5429 0.4918 0.2765

0.354838709677419 0.7478 0.7257 0.6383 0.5402 0.4901 0.2751

0.387096774193548 0.7436 0.7196 0.6346 0.539 0.4839 0.2714

0.419354838709677 0.7079 0.6842 0.6324 0.5018 0.4529 0.2556

0.451612903225806 0.6575 0.6397 0.5904 0.4844 0.415 0.2519

0.483870967741936 0.6302 0.6115 0.5633 0.4563 0.4113 0.2498

0.516129032258065 0.5858 0.5744 0.5132 0.4268 0.397 0.2081

0.548387096774194 0.5559 0.5397 0.509 0.4267 0.3682 0.2033

0.580645161290323 0.5302 0.5227 0.491 0.4043 0.3677 0.2029
177

0.612903225806452 0.4894 0.4748 0.4212 0.3771 0.3595 0.202

0.645161290322581 0.4809 0.4666 0.4163 0.3765 0.354 0.2013

0.67741935483871 0.4808 0.4658 0.4095 0.366 0.3448 0.2001

0.709677419354839 0.4647 0.4487 0.4033 0.3531 0.3424 0.1923

0.741935483870968 0.4496 0.4349 0.3903 0.3496 0.3343 0.1922

0.774193548387097 0.4286 0.4202 0.3784 0.3341 0.2994 0.1855

0.806451612903226 0.3785 0.3785 0.3749 0.3211 0.2831 0.1818

0.838709677419355 0.3513 0.3513 0.3512 0.3102 0.2742 0.1747

0.870967741935484 0.2952 0.2852 0.2571 0.2433 0.2338 0.1451

0.903225806451613 0.2481 0.248 0.2472 0.2329 0.2229 0.1319

0.935483870967742 0.147 0.1432 0.1289 0.1061 0.09827 0.07231

0.967741935483871 0.1127 0.1099 0.0995 0.08593 0.08161 0.04125

0.1 1.0848 1.0505 0.93582 0.79693 0.74345 0.33882

Average of yearly averages: 0.236785333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: CACOTAIR

Metfile: w14860.dvf

PRZM scenario: NYGrapesSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-6 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 7 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

OR Apple

stored as ORAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: ORappleSTD.txt modified Tueday, 29 May 2007 at 13:00:08

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w24232.dvf modified Wedday, 3 July 2002 at 09:06:10

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.1129 0.1093 0.09623 0.07413 0.0618 0.02641

1962 0.2064 0.2 0.1803 0.1428 0.1203 0.06342

1963 0.6386 0.6169 0.5388 0.4182 0.3558 0.1587

1964 0.1877 0.1837 0.1727 0.1422 0.09891 0.05555

1965 0.1922 0.1887 0.1699 0.1382 0.09932 0.0742
178

1966 0.2665 0.261 0.241 0.1874 0.1289 0.06426

1967 0.1752 0.1716 0.1579 0.1326 0.1176 0.06874

1968 0.1393 0.1365 0.1205 0.1069 0.0988 0.06174

1969 0.1716 0.1663 0.1497 0.1341 0.1239 0.06761

1970 0.08218 0.08094 0.07607 0.06588 0.05905 0.03831

1971 0.4962 0.484 0.4288 0.3336 0.2889 0.1473

1972 0.1925 0.1881 0.1659 0.1294 0.116 0.07748

1973 0.09086 0.08898 0.08191 0.06903 0.0615 0.03898

1974 0.3876 0.3791 0.3457 0.2856 0.1926 0.06125

1975 0.239 0.2341 0.2155 0.1824 0.1622 0.09506

1976 0.0578 0.05677 0.0528 0.04525 0.04059 0.01932

1977 0.05346 0.05185 0.0466 0.04221 0.0355 0.02082

1978 0.2865 0.2771 0.2424 0.1865 0.1564 0.06864

1979 0.1225 0.1192 0.1113 0.09337 0.08866 0.05732

1980 0.2015 0.1954 0.1859 0.156 0.146 0.08357

1981 0.2638 0.2565 0.2326 0.1862 0.1943 0.1217

1982 0.2185 0.2118 0.1884 0.1475 0.1258 0.07054

1983 0.06966 0.06762 0.06007 0.04864 0.04533 0.03658

1984 0.2788 0.2703 0.2389 0.2074 0.1939 0.09042

1985 0.2519 0.2427 0.2117 0.157 0.1297 0.07448

1986 0.09607 0.09452 0.08818 0.07632 0.06865 0.04415

1987 0.2519 0.2479 0.2324 0.1461 0.1141 0.07518

1988 0.1892 0.1851 0.1696 0.1412 0.1242 0.07808

1989 0.2766 0.2691 0.2415 0.1908 0.1395 0.04855

1990 0.1942 0.19 0.181 0.1527 0.1349 0.08173

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 0.6386 0.6169 0.5388 0.4182 0.3558 0.1587

0.0645161290322581 0.4962 0.484 0.4288 0.3336 0.2889 0.1473

0.0967741935483871 0.3876 0.3791 0.3457 0.2856 0.1943 0.1217

0.129032258064516 0.2865 0.2771 0.2424 0.2074 0.1939 0.09506

0.161290322580645 0.2788 0.2703 0.2415 0.1908 0.1926 0.09042

0.193548387096774 0.2766 0.2691 0.241 0.1874 0.1622 0.08357

0.225806451612903 0.2665 0.261 0.2389 0.1865 0.1564 0.08173

0.258064516129032 0.2638 0.2565 0.2326 0.1862 0.146 0.07808

0.290322580645161 0.2519 0.2479 0.2324 0.1824 0.1395 0.07748

0.32258064516129 0.2519 0.2427 0.2155 0.157 0.1349 0.07518

0.354838709677419 0.239 0.2341 0.2117 0.156 0.1297 0.07448

0.387096774193548 0.2185 0.2118 0.1884 0.1527 0.1289 0.0742

0.419354838709677 0.2064 0.2 0.1859 0.1475 0.1258 0.07054

0.451612903225806 0.2015 0.1954 0.181 0.1461 0.1242 0.06874

0.483870967741936 0.1942 0.19 0.1803 0.1428 0.1239 0.06864

0.516129032258065 0.1925 0.1887 0.1727 0.1422 0.1203 0.06761

0.548387096774194 0.1922 0.1881 0.1699 0.1412 0.1176 0.06426

0.580645161290323 0.1892 0.1851 0.1696 0.1382 0.116 0.06342

0.612903225806452 0.1877 0.1837 0.1659 0.1341 0.1141 0.06174

0.645161290322581 0.1752 0.1716 0.1579 0.1326 0.09932 0.06125

0.67741935483871 0.1716 0.1663 0.1497 0.1294 0.09891 0.05732

0.709677419354839 0.1393 0.1365 0.1205 0.1069 0.0988 0.05555

0.741935483870968 0.1225 0.1192 0.1113 0.09337 0.08866 0.04855

0.774193548387097 0.1129 0.1093 0.09623 0.07632 0.06865 0.04415

0.806451612903226 0.09607 0.09452 0.08818 0.07413 0.0618 0.03898

0.838709677419355 0.09086 0.08898 0.08191 0.06903 0.0615 0.03831

0.870967741935484 0.08218 0.08094 0.07607 0.06588 0.05905 0.03658

0.903225806451613 0.06966 0.06762 0.06007 0.04864 0.04533 0.02641

0.935483870967742 0.0578 0.05677 0.0528 0.04525 0.04059 0.02082

0.967741935483871 0.05346 0.05185 0.0466 0.04221 0.0355 0.01932

0.1 0.37749 0.3689 0.33537 0.27778 0.19426 0.119036

Average of yearly averages: 0.069003

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: ORAPPAIR

Metfile: w24232.dvf

PRZM scenario: ORappleSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45
179

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 1-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

PA Apple

stored as PAPPAIR.out

Chemical: DPXE2Y45

PRZM environment: PAappleSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3221 0.3099 0.2757 0.2129 0.1775 0.05886

1962 0.1307 0.1261 0.1095 0.08491 0.07772 0.0502

1963 0.04857 0.04698 0.04114 0.03639 0.03556 0.02413

1964 0.2324 0.224 0.1939 0.1595 0.1537 0.06824

1965 0.07541 0.07271 0.06291 0.05594 0.05353 0.03254

1966 0.6936 0.6687 0.5808 0.439 0.3695 0.1234

1967 0.2708 0.2627 0.2329 0.186 0.1749 0.1204

1968 0.9133 0.8929 0.779 0.5845 0.4844 0.1943

1969 0.5522 0.5332 0.4771 0.3574 0.2967 0.1303

1970 0.1558 0.1508 0.1445 0.1236 0.107 0.07525

1971 0.2402 0.2321 0.2022 0.156 0.1336 0.05939

1972 0.5067 0.4905 0.4302 0.3304 0.2815 0.1277

1973 0.4286 0.4154 0.3631 0.2803 0.2444 0.112

1974 0.5059 0.488 0.4283 0.3447 0.3032 0.1265

1975 0.5669 0.5478 0.4973 0.416 0.3659 0.1528

1976 0.3311 0.3196 0.2832 0.2431 0.2095 0.09189

1977 0.1225 0.1186 0.1037 0.08133 0.08112 0.05039

1978 0.4506 0.4351 0.3899 0.307 0.2642 0.1033

1979 0.2977 0.2877 0.2561 0.218 0.1937 0.08521

1980 0.5649 0.545 0.4735 0.3827 0.3245 0.1292

1981 0.105 0.1014 0.09138 0.08226 0.07255 0.04548

1982 0.9582 0.9281 0.8308 0.6536 0.5447 0.1952

1983 0.6342 0.6134 0.5354 0.4441 0.3952 0.1662

1984 0.6129 0.5926 0.5215 0.4217 0.3564 0.148

1985 0.9379 0.9058 0.8043 0.6917 0.5958 0.2389

1986 0.6098 0.5899 0.522 0.4441 0.386 0.2027

1987 0.2976 0.2872 0.2486 0.1968 0.1804 0.09592

1988 0.2202 0.2129 0.1892 0.1514 0.132 0.06161
180

1989 1.212 1.172 1.119 0.8809 0.7435 0.2755

1990 0.774 0.7493 0.652 0.5099 0.4545 0.2

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.212 1.172 1.119 0.8809 0.7435 0.2755

0.0645161290322581 0.9582 0.9281 0.8308 0.6917 0.5958 0.2389

0.0967741935483871 0.9379 0.9058 0.8043 0.6536 0.5447 0.2027

0.129032258064516 0.9133 0.8929 0.779 0.5845 0.4844 0.2

0.161290322580645 0.774 0.7493 0.652 0.5099 0.4545 0.1952

0.193548387096774 0.6936 0.6687 0.5808 0.4441 0.3952 0.1943

0.225806451612903 0.6342 0.6134 0.5354 0.4441 0.386 0.1662

0.258064516129032 0.6129 0.5926 0.522 0.439 0.3695 0.1528

0.290322580645161 0.6098 0.5899 0.5215 0.4217 0.3659 0.148

0.32258064516129 0.5669 0.5478 0.4973 0.416 0.3564 0.1303

0.354838709677419 0.5649 0.545 0.4771 0.3827 0.3245 0.1292

0.387096774193548 0.5522 0.5332 0.4735 0.3574 0.3032 0.1277

0.419354838709677 0.5067 0.4905 0.4302 0.3447 0.2967 0.1265

0.451612903225806 0.5059 0.488 0.4283 0.3304 0.2815 0.1234

0.483870967741936 0.4506 0.4351 0.3899 0.307 0.2642 0.1204

0.516129032258065 0.4286 0.4154 0.3631 0.2803 0.2444 0.112

0.548387096774194 0.3311 0.3196 0.2832 0.2431 0.2095 0.1033

0.580645161290323 0.3221 0.3099 0.2757 0.218 0.1937 0.09592

0.612903225806452 0.2977 0.2877 0.2561 0.2129 0.1804 0.09189

0.645161290322581 0.2976 0.2872 0.2486 0.1968 0.1775 0.08521

0.67741935483871 0.2708 0.2627 0.2329 0.186 0.1749 0.07525

0.709677419354839 0.2402 0.2321 0.2022 0.1595 0.1537 0.06824

0.741935483870968 0.2324 0.224 0.1939 0.156 0.1336 0.06161

0.774193548387097 0.2202 0.2129 0.1892 0.1514 0.132 0.05939

0.806451612903226 0.1558 0.1508 0.1445 0.1236 0.107 0.05886

0.838709677419355 0.1307 0.1261 0.1095 0.08491 0.08112 0.05039

0.870967741935484 0.1225 0.1186 0.1037 0.08226 0.07772 0.0502

0.903225806451613 0.105 0.1014 0.09138 0.08133 0.07255 0.04548

0.935483870967742 0.07541 0.07271 0.06291 0.05594 0.05353 0.03254

0.967741935483871 0.04857 0.04698 0.04114 0.03639 0.03556 0.02413

0.1 0.93544 0.90451 0.80177 0.64669 0.53867 0.20243

Average of yearly averages: 0.118183666666667

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PAPPAIR

Metfile: w14751.dvf

PRZM scenario: PAappleSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1109 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 10 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1109 kg/ha

Record 17:FILTRA

IPSCND

UPTKF
181

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)

PA Tomato

stored as PATOMAIR.out

Chemical: DPXE2Y45

PRZM environment: PAtomatoSTD.txt modified Tueday, 29 May 2007 at 13:01:58

EXAMS environment: pond298.exv modified Thuday, 29 August 2002 at 16:33:30

Metfile: w14751.dvf modified Wedday, 3 July 2002 at 09:06:14

Water segment concentrations (ppb)

Year Peak 96 hr 21 Day 60 Day 90 Day Yearly

1961 0.3387 0.3262 0.2903 0.2246 0.1879 0.07126

1962 0.2203 0.2127 0.1849 0.1441 0.131 0.07737

1963 0.06939 0.06701 0.0583 0.05445 0.0539 0.03698

1964 0.3337 0.3217 0.2782 0.2242 0.215 0.09527

1965 0.1537 0.1481 0.1291 0.1129 0.1046 0.05836

1966 0.6018 0.5806 0.5061 0.3848 0.3257 0.1342

1967 0.347 0.3361 0.2982 0.2342 0.213 0.1302

1968 1.063 1.043 0.9163 0.7009 0.6416 0.2617

1969 0.6447 0.6228 0.557 0.419 0.3485 0.1634

1970 0.1928 0.1873 0.1771 0.1524 0.138 0.09624

1971 0.2926 0.2838 0.2495 0.1978 0.1699 0.07712

1972 0.4915 0.4763 0.42 0.3252 0.3081 0.1408

1973 0.505 0.4899 0.4298 0.3604 0.3279 0.1415

1974 0.6952 0.6707 0.6022 0.4879 0.4282 0.1764

1975 0.8918 0.8621 0.7739 0.6464 0.5634 0.2257

1976 0.4947 0.4777 0.4325 0.3698 0.3172 0.1371

1977 0.3373 0.3254 0.2817 0.213 0.1916 0.09462

1978 0.6168 0.5958 0.5306 0.4217 0.3658 0.1473

1979 0.4338 0.4204 0.3792 0.3231 0.2871 0.1254

1980 0.6847 0.6609 0.589 0.4707 0.4068 0.1635

1981 0.1132 0.1095 0.09931 0.09108 0.08059 0.05421

1982 1.189 1.155 1.051 0.8292 0.693 0.252

1983 1.064 1.03 0.9014 0.8148 0.7008 0.2779

1984 0.5632 0.5449 0.4848 0.4007 0.3404 0.157

1985 1.169 1.13 1.003 0.8602 0.7437 0.2956

1986 0.8014 0.7757 0.6867 0.5895 0.5143 0.2689

1987 0.4373 0.4223 0.3661 0.2957 0.2703 0.1431

1988 0.3254 0.3145 0.2807 0.2262 0.1973 0.09186

1989 1.66 1.606 1.546 1.232 1.043 0.3895

1990 0.9391 0.9095 0.7926 0.6298 0.5652 0.2563

Sorted results

Prob. Peak 96 hr 21 Day 60 Day 90 Day Yearly

0.032258064516129 1.66 1.606 1.546 1.232 1.043 0.3895

0.0645161290322581 1.189 1.155 1.051 0.8602 0.7437 0.2956

0.0967741935483871 1.169 1.13 1.003 0.8292 0.7008 0.2779

0.129032258064516 1.064 1.043 0.9163 0.8148 0.693 0.2689

0.161290322580645 1.063 1.03 0.9014 0.7009 0.6416 0.2617

0.193548387096774 0.9391 0.9095 0.7926 0.6464 0.5652 0.2563

0.225806451612903 0.8918 0.8621 0.7739 0.6298 0.5634 0.252

0.258064516129032 0.8014 0.7757 0.6867 0.5895 0.5143 0.2257

0.290322580645161 0.6952 0.6707 0.6022 0.4879 0.4282 0.1764

0.32258064516129 0.6847 0.6609 0.589 0.4707 0.4068 0.1635

0.354838709677419 0.6447 0.6228 0.557 0.4217 0.3658 0.1634

0.387096774193548 0.6168 0.5958 0.5306 0.419 0.3485 0.157

0.419354838709677 0.6018 0.5806 0.5061 0.4007 0.3404 0.1473

0.451612903225806 0.5632 0.5449 0.4848 0.3848 0.3279 0.1431

0.483870967741936 0.505 0.4899 0.4325 0.3698 0.3257 0.1415

0.516129032258065 0.4947 0.4777 0.4298 0.3604 0.3172 0.1408

0.548387096774194 0.4915 0.4763 0.42 0.3252 0.3081 0.1371

0.580645161290323 0.4373 0.4223 0.3792 0.3231 0.2871 0.1342
182

0.612903225806452 0.4338 0.4204 0.3661 0.2957 0.2703 0.1302

0.645161290322581 0.347 0.3361 0.2982 0.2342 0.215 0.1254

0.67741935483871 0.3387 0.3262 0.2903 0.2262 0.213 0.09624

0.709677419354839 0.3373 0.3254 0.2817 0.2246 0.1973 0.09527

0.741935483870968 0.3337 0.3217 0.2807 0.2242 0.1916 0.09462

0.774193548387097 0.3254 0.3145 0.2782 0.213 0.1879 0.09186

0.806451612903226 0.2926 0.2838 0.2495 0.1978 0.1699 0.07737

0.838709677419355 0.2203 0.2127 0.1849 0.1524 0.138 0.07712

0.870967741935484 0.1928 0.1873 0.1771 0.1441 0.131 0.07126

0.903225806451613 0.1537 0.1481 0.1291 0.1129 0.1046 0.05836

0.935483870967742 0.1132 0.1095 0.09931 0.09108 0.08059 0.05421

0.967741935483871 0.06939 0.06701 0.0583 0.05445 0.0539 0.03698

0.1 1.1585 1.1213 0.99433 0.82776 0.70002 0.277

Average of yearly averages: 0.158026333333333

Inputs generated by pe5.pl - Novemeber 2006

Data used for this run:

Output File: PATOMAIR

Metfile: w14751.dvf

PRZM scenario: PAtomatoSTD.txt

EXAMS environment file: pond298.exv

Chemical Name: DPXE2Y45

Description Variable Name Value Units Comments

Molecular weight mwt 483.15 g/mol

Henry's Law Const. henry 3.1E-15 atm-m^3/mol

Vapor Pressure vapr 1.57E-13 torr

Solubility sol 1.023 mg/L

Kd Kd mg/L

Koc Koc 328 mg/L

Photolysis half-life kdp 0.31 days Half-life

Aerobic Aquatic Metabolism kbacw 341.1355 days Halfife

Anaerobic Aquatic Metabolism kbacs 208 days Halfife

Aerobic Soil Metabolism asm 631.76 days Halfife

Hydrolysis: pH 7 days Half-life

Method: CAM 2 integer See PRZM manual

Incorporation Depth: DEPI cm

Application Rate: TAPP 0.1098 kg/ha

Application Efficiency: APPEFF 0.95 fraction

Spray Drift DRFT 0.00 fraction of application rate applied to pond

Application Date Date 16-4 dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1 interval 5 days Set to 0 or delete line for single app.

app. rate 1 apprate 0.1098 kg/ha

Record 17:FILTRA

IPSCND

UPTKF

Record 18:PLVKRT

PLDKRT 0.019804

FEXTRC 0.5

Flag for Index Res. Run IR EPA Pond

Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run)
183

APPENDIX C

Initial Federally Listed Species
184

Species Counts by State for Indicated Crops

No species were excluded.

Minimum of 1 Acre.

All Medium Types Reported

broccoli, brussels sprouts, cabbage - head, cauliflower, celery, chinese 

cabbage, collards, escarole and endive, kale, lettuce, all, lettuce, head, 

lettuce, leaf, lettuce, romaine, mustard cabbage (bok choy), mustard greens 

(mizuna), parsley, rhubarb, spinach, turnip greens, watercress, cantaloups, 

cucumbers and pickles, honeydew melons, pumpkins, squash, watermelons, 

eggplant, okra, peppers, bell, peppers, chile (all peppers - excluding bell), 

pimientos, tomatoes, cotton, all, apples, pears, all, pears, bartlett (AZ, CA, 

ID, OR, & WA only), pears, other (AZ, CA, ID, OR, & WA only), potatoes, 

almonds, apricots, cherries, sweet, cherries, tart, nectarines, peaches, all, 

peaches, clingstone (AZ & CA only), peaches, freestone (AZ & CA only), 

plums (AZ & CA only), plums and prunes, prunes (AZ & CA only), grapes

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

Alabama

The taxa Amphibian has 2 species co-occurring with indicated crops.

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Bivalve has 30 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 10 species co-occurring with indicated crops.

The taxa Ferns has 3 species co-occurring with indicated crops.

The taxa Fish has 15 species co-occurring with indicated crops.

The taxa Gastropod has 10 species co-occurring with indicated crops.

The taxa Mammal has 4 species co-occurring with indicated crops.

The taxa Monocot has 3 species co-occurring with indicated crops.

The taxa Reptile has 8 species co-occurring with indicated crops.

Alaska

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

Arizona

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185

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Amphibian has 2 species co-occurring with indicated crops.

The taxa Bird has 7 species co-occurring with indicated crops.

The taxa Dicot has 16 species co-occurring with indicated crops.

The taxa Fish has 18 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Mammal has 9 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 2 species co-occurring with indicated crops.

Arkansas

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 6 species co-occurring with indicated crops.

The taxa Crustacean has 2 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Fish has 3 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

California

The taxa Amphibian has 6 species co-occurring with indicated crops.

The taxa Bird has 15 species co-occurring with indicated crops.

The taxa Conf/cycds has 2 species co-occurring with indicated crops.

The taxa Crustacean has 9 species co-occurring with indicated crops.

The taxa Dicot has 159 species co-occurring with indicated crops.

The taxa Fish has 31 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 22 species co-occurring with indicated crops.

The taxa Mammal has 20 species co-occurring with indicated crops.

The taxa Monocot has 17 species co-occurring with indicated crops.

The taxa Reptile has 11 species co-occurring with indicated crops.

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186

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

Colorado

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Dicot has 10 species co-occurring with indicated crops.

The taxa Fish has 6 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Connecticut

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

Delaware

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

Florida

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 8 species co-occurring with indicated crops.

The taxa Bivalve has 7 species co-occurring with indicated crops.

The taxa Conf/cycds has 1 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 46 species co-occurring with indicated crops.

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187

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Fish has 4 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 8 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 10 species co-occurring with indicated crops.

Georgia

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 4 species co-occurring with indicated crops.

The taxa Bivalve has 16 species co-occurring with indicated crops.

The taxa Conf/cycds has 1 species co-occurring with indicated crops.

The taxa Dicot has 10 species co-occurring with indicated crops.

The taxa Ferns has 2 species co-occurring with indicated crops.

The taxa Fish has 11 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

The taxa Monocot has 6 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

Hawaii

The taxa Arachnid has 1 species co-occurring with indicated crops.

The taxa Bird has 32 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 233 species co-occurring with indicated crops.

The taxa Ferns has 12 species co-occurring with indicated crops.

The taxa Gastropod has 39 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 22 species co-occurring with indicated crops.

The taxa Reptile has 4 species co-occurring with indicated crops.

Idaho

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188

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Dicot has 3 species co-occurring with indicated crops.

The taxa Fish has 8 species co-occurring with indicated crops.

The taxa Gastropod has 6 species co-occurring with indicated crops.

The taxa Mammal has 4 species co-occurring with indicated crops.

Illinois

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 7 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 7 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Indiana

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 11 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

Iowa

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Dicot has 3 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 2 species co-occurring with indicated crops.

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189

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Kansas

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Fish has 4 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Kentucky

The taxa Bird has 6 species co-occurring with indicated crops.

The taxa Bivalve has 22 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 10 species co-occurring with indicated crops.

The taxa Fish has 4 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

Louisiana

The taxa Bird has 5 species co-occurring with indicated crops.

The taxa Bivalve has 3 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 2 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Reptile has 7 species co-occurring with indicated crops.

Maine

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

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190

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Fish has 2 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

Maryland

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Fish has 2 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 5 species co-occurring with indicated crops.

Massachusetts

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Insect has 3 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

Michigan

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Insect has 4 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

The taxa Monocot has 3 species co-occurring with indicated crops.

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191

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Reptile has 1 species co-occurring with indicated crops.

Minnesota

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Mississippi

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 5 species co-occurring with indicated crops.

The taxa Bivalve has 9 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 3 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

The taxa Reptile has 9 species co-occurring with indicated crops.

Missouri

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 6 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 7 species co-occurring with indicated crops.

The taxa Fish has 7 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Montana

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192

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Fish has 5 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

Nebraska

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Fish has 2 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Nevada

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Dicot has 8 species co-occurring with indicated crops.

The taxa Fish has 23 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

New Hampshire

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

New Jersey

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

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193

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 3 species co-occurring with indicated crops.

The taxa Reptile has 5 species co-occurring with indicated crops.

New Mexico

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 6 species co-occurring with indicated crops.

The taxa Crustacean has 2 species co-occurring with indicated crops.

The taxa Dicot has 13 species co-occurring with indicated crops.

The taxa Fish has 13 species co-occurring with indicated crops.

The taxa Gastropod has 5 species co-occurring with indicated crops.

The taxa Mammal has 5 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

New York

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

North Carolina

The taxa Arachnid has 1 species co-occurring with indicated crops.

The taxa Bird has 4 species co-occurring with indicated crops.

The taxa Bivalve has 8 species co-occurring with indicated crops.

The taxa Dicot has 21 species co-occurring with indicated crops.

The taxa Fish has 4 species co-occurring with indicated crops.

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194

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 4 species co-occurring with indicated crops.

The taxa Monocot has 5 species co-occurring with indicated crops.

The taxa Reptile has 5 species co-occurring with indicated crops.

North Dakota

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Ohio

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Bivalve has 6 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Insect has 4 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 2 species co-occurring with indicated crops.

Oklahoma

The taxa Bird has 6 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Fish has 4 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Oregon

The taxa Bird has 4 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 11 species co-occurring with indicated crops.

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195

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Fish has 22 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 3 species co-occurring with indicated crops.

Pennsylvania

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

Rhode Island

The taxa Bird has 1 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

The taxa Reptile has 4 species co-occurring with indicated crops.

South Carolina

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 4 species co-occurring with indicated crops.

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 12 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 6 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

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196

AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

South Dakota

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Fish has 2 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Tennessee

The taxa Arachnid has 1 species co-occurring with indicated crops.

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Bivalve has 38 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 17 species co-occurring with indicated crops.

The taxa Ferns has 1 species co-occurring with indicated crops.

The taxa Fish has 16 species co-occurring with indicated crops.

The taxa Gastropod has 3 species co-occurring with indicated crops.

The taxa Mammal has 3 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Texas

The taxa Amphibian has 4 species co-occurring with indicated crops.

The taxa Arachnid has 10 species co-occurring with indicated crops.

The taxa Bird has 12 species co-occurring with indicated crops.

The taxa Crustacean has 1 species co-occurring with indicated crops.

The taxa Dicot has 27 species co-occurring with indicated crops.

The taxa Fish has 9 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 9 species co-occurring with indicated crops.

The taxa Mammal has 5 species co-occurring with indicated crops.

The taxa Monocot has 3 species co-occurring with indicated crops.

The taxa Reptile has 6 species co-occurring with indicated crops.

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AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

Utah

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Dicot has 22 species co-occurring with indicated crops.

The taxa Fish has 8 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

The taxa Reptile has 1 species co-occurring with indicated crops.

Vermont

The taxa Bivalve has 1 species co-occurring with indicated crops.

The taxa Dicot has 1 species co-occurring with indicated crops.

The taxa Mammal has 1 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Virginia

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bird has 2 species co-occurring with indicated crops.

The taxa Bivalve has 21 species co-occurring with indicated crops.

The taxa Crustacean has 2 species co-occurring with indicated crops.

The taxa Dicot has 13 species co-occurring with indicated crops.

The taxa Fish has 7 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Insect has 3 species co-occurring with indicated crops.

The taxa Mammal has 5 species co-occurring with indicated crops.

The taxa Monocot has 4 species co-occurring with indicated crops.

The taxa Reptile has 5 species co-occurring with indicated crops.

Washington

The taxa Bird has 4 species co-occurring with indicated crops.

The taxa Dicot has 7 species co-occurring with indicated crops.

The taxa Fish has 19 species co-occurring with indicated crops.

The taxa Insect has 1 species co-occurring with indicated crops.

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AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, ME, MD, MA, MI, 

MN, MS, MO, MT, NE, NV, NH, NJ, NM, NY, NC, ND, OH, OK, OR, PA, PR, RI, SC, SD, TN, 

TX, UT, VT, VA, WA, WV, WI, WY

The taxa Mammal has 5 species co-occurring with indicated crops.

The taxa Reptile has 2 species co-occurring with indicated crops.

West Virginia

The taxa Amphibian has 1 species co-occurring with indicated crops.

The taxa Bivalve has 5 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Gastropod has 1 species co-occurring with indicated crops.

The taxa Mammal has 5 species co-occurring with indicated crops.

The taxa Monocot has 1 species co-occurring with indicated crops.

Wisconsin

The taxa Bird has 3 species co-occurring with indicated crops.

The taxa Bivalve has 2 species co-occurring with indicated crops.

The taxa Dicot has 4 species co-occurring with indicated crops.

The taxa Insect has 2 species co-occurring with indicated crops.

The taxa Mammal has 2 species co-occurring with indicated crops.

The taxa Monocot has 2 species co-occurring with indicated crops.

Wyoming

The taxa Dicot has 2 species co-occurring with indicated crops.

The taxa Fish has 1 species co-occurring with indicated crops.

The taxa Mammal has 4 species co-occurring with indicated crops.

No species were excluded.

Dispersed species included in report.

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