# 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)

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## PREPARED 

## BY 

## : Edward Odenkirchen, Ph. D

. James Hetrick, Ph.D

. Environmental Risk Branch 1 Environmental Fate and Effects Division Office of Pesticide Programs

APPROVED 

## B Y 

## : 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 Hy

pothesis

................................ ................................ ................................ 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 leaf y vegetables (celery, lettuce, spinach, Arugula, Cardoon, Amaranth leafy), cotton, grape, pome fruit (apple, crabapple, loquat, may haw, 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 f ormulations 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 temperature 1 

## ) 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: I N

-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 9 0% 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 I N

-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 I

nvertebrates 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. Itappears 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/surf actants 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). Inall 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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### 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 0.352 6 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 fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 0.6 700 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 LOC s 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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 0.13 36 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 0.0 378 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 wit

h chronic LOC of 1



### .

## 10

Tier II RQs for Estuarine/Marine Invertebrates fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 0.3 390 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 semi

aquatic plants

- monocots Yes4 

### Yes 1 

### all

Terrestrial and semi

aquatic plants

- dicots Yes4 

### Yes 1 

### all Terrestrial invertebrates Yes all No Birds No Yes 1,2,3 ,5 

### All Terrestrial phase
am phibians No Yes 1,2 ,5 

### All Reptiles No Yes 1,2,3 ,5 

### All Mammals No Yes 1,2,3 ,5 

### All Aquatic vascular plants No No Freshwater fish No Yes2 ,5 

### All Aquatic phase
am phibians 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 Yes 3 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 inver tebrates 2 direct effects on aquatic invertebrates 3 direct effects on estuarine/marine invertebrates 4 insufficient data to preclude risk 5direct 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

-py ridinyl)

- 1 H

-py razole

- 5

-carboxamide Empirical Formula: C 18

## H 14

## N5 

## O2

## BrCl2 

## Molecular Weight: 483.15 g/mole

CAS No.: 500008

-45

-7 (chlorantraniliprole)

Common Name: chlorantraniliprole Pesticide Ty

pe: Insecticide

Chemical Family: Anthranilic diamide Physical State: Fine Crystalline Powder

Odor: No odor
pH: 5.77 ± 0.087 at 20 o

## C
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

-210 o

## C Relative Density: 1.5070 at 20 o

## C

## 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 20 o

## C: 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 at20 o

## C (2.1 x 10 - 11 

## Pa at 25 o

## C)
Henry ’s Law Constant : 3.1 x 10 - 15 

## atm

-m3

## /mol (20 o

## C) (3.1 x 10 - 10 

## Pa

-m3

## /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, cro ss - 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 leaf roller, peach twig borer, and southern army worm. Inaddition 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 Coragen TM 

## SC

Use Site Application Method Target Pest Application rate (lb a.i./acre) Number of

Applications/ Interval Brassica and leafy vegetables drip chemigation b eet 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

f oliar (air or ground spray) diamondback moth 0.02 6

-0.045 4 to 7 for maximum crop application of 0.2 lb a.i./acre

5 day interval b eet 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 b eet 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 Coragen TM 

## 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 f oliar (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 b eet 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 b eet 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 f oliar (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 b eet 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 b eet 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 lb s 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 qua ntitatively

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:

Chloran traniliprole, 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 T

esting 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 dy namics. 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 wildlif e 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 la beled 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 ty pically 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 grou p, 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, EC 5/NOAEC Aquatic Plants all aquatic plants most sensitive species tested (algae/vascular) of algae and vascular EC50/EC25, EC 5/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

-py ridinyl)

- 1H

py razol

- 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 (t 1/2 

## = 228 to 924 days) in aerobic soils incubated at 25 0

## C (MRID 46889015, 46889014, 46889124). It degrades faster at higher soil temperatures of 34

- 35 0

## C and 49 0

## C (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 (t 1 /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, IN

F9N04, 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

## =15 3 , 1/n=1. 0028) in a loamy s and 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 s and 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 C hlorantraniliprole 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
m3

### /mol 3.1E

- 15 Estimated
Hydrolysis @ pH 7 Days Stable MRID 46889017 Photodegradation in Water Days 0.31 MRID 46889018

Aerobic Soil Metabolism Days 577.6 1 

### 537.3 374 .6 410.1 246.6 228.0 8 88.6 924.1 396.0 MRID 46889124

MRID 46889015 MRID 46889124 (Total Soil Extractable Residue @ 25 oC) 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 st udy. 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

-py

razol

- 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

-py

razol

- 5

-yl]

-6

- chloro

-3,8 dimethyl

-4(3 H)

- 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 @ 25 0

### C incubation 5.2 @ 35 0

### C incubation 4.2 @ 49 0

### C incubation N

-Methyl

- [3

-bromo - 1H

pyrazol

- 5

-yl]carboxylic acid

IN

-EVK64 ND @ 25 0

### C incubation

1.7 @ 35 0

### C incubation 5.3 @ 49 0

### C incubation IN

-EQW78 9.5 @ 25 0

### C incubation

33.3 @ 35 0

### C incubation 71.6 @ 49 0

### C incubation (2

- [3

-Bromo - 1

-(3

-chloro

-2

- pyridinyl)

- 1H

-py

razol

- 5

-yl]

-6

- chloro

-3,8 dimethyl

-4(3H)

- quinazolinone IN

-ECD73 4.9 @ 25 0

### C incubation

8.2 @ 35 0

### C incubation 9.1 @ 49 0

### C incubation 2

- [3

-bromo - 1

-(3

-chloro

-2

- pyridinyl)

- 1H

-py

razole

- 5

-yl]

- 6

- chloro

-3,8

-dimethyl

-4(3H)

- quinazolinone INGAZ70 4.3 @ 25 0

### C incubation

7.4 @ 35 0

### C incubation 1.0 @ 49 0

### C incubation 2

- [3

-bromo - 1

-(3

-chloro

-2

- pyridinyl)

- 1H

-py

razol

- 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

-py

razol

- 5

-yl]

-6

- chloro

-3,8 dimethyl

-4(3H)

- quinazolinone IN

-F6L99 4.2 @ no photodegradation

ND @ photodegradation 5

-bromo -N

-methyl

- 1H

pyrazole

-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

-py

razole

- 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

-py razol

- 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

-py

razole

- 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), IN

GAZ70 (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), IN

F6L99 (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 half

lives 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). Inthe Prince Edward study, IN

-EQW78 (5.3% of applied @ Day 0), IN

-ECD73 (1.3%@ Day 0) and I N

-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 resid ues 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

54 1 ). 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

-py ridinyl)

- [H

-py

razole

- 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 C hlorantraniliprole 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 46 889017 Photodegradation in Water days 0.31 MRID 46889018

Aerobic Soil Metabolism Days 631.76 2,3 

### MRID 46889124 MRID 46889015 MRID 46889124 Calculated 90th 

### percentile of mean 1 

### 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 mean 1 

### 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 25 0C. 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 90 th 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 half

lives. 

## 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 (MaximumApplication 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 DuPontTME 2

### Y45 

### 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 Chlo rantraniliprole for Various Crop Types (Maximum Aerial Application Rate)

Scenario Application

Rate (lbs ai/A) #

App s 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 0.0 99 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) #

App s 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 DuPont

14380 Anas

platyrhynchos (Mallard) Subacute

dietary LC50

NOAEC >5620

5620 mg/kg diet

Chlorantraniliprole Technical Technical DuPont

14384 Anas

platyrhynchos (Mallard) Reproduction LOAEC (viable embryo reduction) NOAEC 250

500 mg/kg diet

Chlorantraniliprole Technical Technical DuPont

14378 Colinus

virginianus (Northern bobwhite) Acute oral

dose LD 50

NOAEL >2250

2250 mg/kg bw

Chlorantraniliprole Technical Technical DuPont

14379 Colinus

virginianus (Northern bobwhite) Subacute

dietary LC50

NOAEC) >5620

5620 mg/kg diet

Chlorantraniliprole Technical Technical DuPont

14383 Colinus

virginianus (Northern bobwhite) Reproduction LOAEC (egsheell thinning) NOAEC 250

120 mg/kg

-diet

IN

-EQW78 Technical

metabolite DuPont

18859 Colinus

virginianus (Northern bobwhite) Acute oral

dose LD 50

NOAEL >2250

2250 mg I

N

EQW78/kg bw

Chlorantraniliprole 20SC Formulated

Product DuPont

18945 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 DuPont

18946 Colinus

virginianus (Northern bobwhite) Acute oral

dose LD 50

NOAEL(transient clinical signs, no mortality) >2250

486 mg a.i./kg

bw

Chlorantraniliprole 2 0SC Formulated

Product DuPont

19420 Colinus

virginianus (Northern bobwhite) Subacute

dietary LC50

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 T

oxicity 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 LD5 0. 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 C hlorantraniliprole, 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 DuPont

18423 Aphidius

rhopalosiphi Mortality

and reproduction LR

50 and ER 50 >750 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

12405 Aphidius

rhopalosiphi Mortality

and reproduction LR

50 and ER 50 >750 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

12753 Apis mellifera

(Honeybee) Semi

-field NOEC 156.16 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

14387 Apis 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 DuPont

14388 Apis mellifera

(Honeybee) semi

-field NOAEC 52.5 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

14706 Apis mellifera

(Honeybee) semi

-field NOAEC 52.5 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

16269 Apis mellifera

(Honeybee) Acute Mortality <4% 112.5 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

16271 Apis mellifera

(Honeybee) semi

-field NOAEC >60 g chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

16272 Apis mellifera

(Honeybee) semi

-field NOAEC >60 g chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

17208 Apis mellifera

(Honeybee) semi

-field NOAEC 60 g. chlorantraniliprole/ha

Chlorantraniliprole 20SC Formulated Product DuPont

17247 Apis mellifera

(Honeybee) semi

-field LOAEC (mortality and decreased flight intensity) >60 g. chlorantraniliprole/ha

Chlorantraniliprole 20SC Formulated Product DuPont

17248 Apis mellifera

(Honeybee) semi

-field LOAEC (mortality and decreased flight intensity) 60 g. chlorantraniliprole/ha Chlorantraniliprole Technical Technical DuPont

17582 Apis mellifera

(Honeybee) Acute oral LD 50 >0.0274 >104.1 μg/bee in water

μg/bee in acetone chlorantraniliprole/bee Chlorantraniliprole 20SC Formulated Product DuPont

180 85 Apis 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 180 86 (Honeybee) (mortality and decreased flight intensity) Chlorantraniliprole 20SC Formulated Product DuPont

18087 Apis mellifera

(Honeybee) semi

-field NOAEC 60 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

18426 Apis mellifera

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

Chlorantraniliprole 20SC Formulated Product DuPont

17301 Chrysoperla

carnea (Green lacewing) larvae Mortality

Reproduction EC50

LOEC 120

120 g chlorantraniliprole/ha

Chlorantraniliprole 20SC Formulated Product DuPont

19746 Coccinella

septempunctata (Lady bird beetle) Mortality

Reproduction LOAEC

LOAEC 60

60 g. chlorantraniliprole/ha

Chlorantraniliprole 20SC Formulated Product DuPont

17300 Coccinella

septempunctata (Lady bird beetle) larvae Mortality

Reproduction EC50

LOEC <120

120 g. chlorantraniliprole/ha Chlorantraniliprole Technical DuPont

14398 Eisenia fetida

(Earthworm) Acute LC50 >1000 mg chlorantraniliprole /kg soil dry weight.

IN

-EQW78 Technical metabolite DuPont

15389 Eisenia fetida

(Earthworm) Acute LC50 >1000 mg I N

-EQW78/kg soil dry weight. Chlorantraniliprole 35WG Formulated Product DuPont

16694 Eisenia fetida

(Earthworm Reproduction

Growth NOAEC 350 mg chlorantraniliprole /kg soil dry weight.

IN

-EQW78 Technical metabolite DuPont

17093 Eisenia fetida

(Earthworm Reproduction

Growth NOAEC 1000 mg IN

-EQW78/kg soil dry weight.

IN

-F6 L9 9 Technical metabolite DuPont

17631 Eisenia fetida

(Earthworm) Acute LC50 632.5 mg I N

-F6 L9 9/kg soil dry weight.

IN

-ECD73 Technical metabolite DuPont

17632 Eisenia fetida

(Earthworm) Reproduction

Growth NOAEC 1000 mg I N

-ECD73/kg artificial soil dry weight

IN

- GAZ70 Technical metabolite DuPont

17633 Eisenia fetida

(Earthworm) Reproduction

Growth NOAEC 1000 mg I N

- GAZ70/kg soil dry weight Chlorantraniliprole 35WG Formulated Product DuPont

18817 Eisenia fetida

(Earthworm) Acute LC50 >350 mg chlorantraniliprole/kg drysoil Chlorantraniliprole 20SC Formulated Product DuPont

18818 Eisenia fetida

(Earthworm) Acute LC50 >20 0 mg chlorantraniliprole/kg drysoil Chlorantraniliprole 20SC Formulated Product DuPont

16532 Episyrphus

balteatus (Hoverfly) Mortality LR 100 120 g chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

18082 Episyrphus

balteatus (Hoverfly) Mortality

Reproduction LR

50 ER 50 12.6

13.3 g chlorantraniliprole/ha

Chlorantraniliprole 20SC Formulated Product DuPont

19747 Episyrphus

balteatus (Hoverfly) Mortality 1 st

treatment Mortality 2nd treatment Reproduction <control

>control

NOAEL 60

60

60 G chlorantraniliprole/ha twice with 7

-day interval Chlorantraniliprole 35WG Formulated Product DuPont

18084 Episyrphus

balteatus (Hoverfly) Mortality

Reproduction LR50

ER 50 4.64

>4.4 g. chlorantraniliprole/ha

Chlorantraniliprole 35WG Formulated Product DuPont

20303 Episyrphus

balteatus (Hoverfly) Mortality 1 st

treatment Mortality 2nd treatment Reproduction <control

<control

NOAEL 60

60

60 g. chlorantraniliprole/ha twice with 7

-day interval

IN

-EQW78 Technical metabolite DuPont

16531 Folsomia

candida (Springtail) Reproduction EC 50 NOEC >100

100 mg IN

-EQW78/kg dry soil

IN

-ECD73 Technical metabolite DuPont

17083 Folsomia

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 DuPont

1 8730 Folsomia

candida (Springtail) Reproduction EC 50 NOEC 0.48

0.39 mg chlorantraniliprole /kg dry soil Chlorantraniliprole Technical DuPont

19748 Hypoaspis

aculeifer (mite) Reproduction NOAEC 100 mg chlorantraniliprole /kg dry soil Chlorantraniliprole 20SC Formulated Product DuPont

18081 RV1 Orius

laevigatus Mortality

and reproduction LR

50 & ER 50 >120 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

1 2406 Typhlodromus

pyri Mortality

and reproduction LR

50 and ER 50 >750 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

14704 Typhlodromus

pyri Mortality

and reproduction LR

50 ER 50 >750 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

17312 Typhlodromus

pyri Population

study NOAEC 750 g. chlorantraniliprole/ha Chlorantraniliprole 35WG Formulated Product DuPont

14705 Typhlodromus

pyri Population

reduction (transient) LOAEC 52.5 g. chlorantraniliprole/ha Chlorantraniliprole 20SC Formulated Product DuPont

18424 Typhlodromus

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 DuPont

19074 Zea 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 DuPont

19075 Zea 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 sp ecies 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 DuPont

18428 Brachionus

calyciflorus Acute EC 50 >1.00 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

15109 Centroptilum

triangulifer (Mayfly) Acute LC50 0.0116 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

17585 Chimarra

atterima (Caddisfly) Acute LC50 0.0117 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

15112 Chironomus

riparius (Midge) Acute LC50 0.0859 mg chlorantraniliprole/L

Chlorantraniliprole Technical Technical DuPont

14396 Chironomus

riparius (Midge) Chronic NOAEC (pore water from 28

-d sediment study 0.005 mg chlorantraniliprole/kg spiked sediment dry weight Chlorantraniliprole Technical Technical DuPont

18090 Copepods (of

the suborder Cyclopo ida) Acute LC50 >1.00 mg chlorantraniliprole technical/L Chlorantraniliprole Technical Technical DuPont

15868 28

-day old

Daphnia magna (Water flea) Acute EC 50 0.0166 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

12411* Daphnia magna

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

12754 RV1 Daphnia magna

(Water flea) Chronic NOAEC 0.00447 mg chlorantraniliprole/L

LB A24

-002 Technical

metabolite DuPont

14889 RV1 Daphnia mag na (Water flea) Acute EC 50 NOAEC >10

10 mg LBA24

-002/L

LB A22

-002 Technical

metabolite DuPont

14890 RV1 Daphnia magna

(Water flea) Acute EC 50 NOAEC >0.24

0.24 mg LBA22

-002/L Chlorantraniliprole 35WG Formulated

Product DuPont

15113 Daphnia magna

(Water f lea) Acute EC 50 0.011 mg chlorantraniliprole/L

IN

-EQW78 Technical

metabolite DuPont

15388 Daphnia magna

(Water flea) Acute EC 50 NOAEC >0.138

0.138 mg I

N

-EQW78/L Chlorantraniliprole Technical Technical DuPont

15874 Daphnia magna

(Water flea) Chronic NOAEC 0.00447 mg chlorantraniliprole/L

LB A23

-000 DuPont

16754 RV1 Daphnia magna

(Water flea) Acute EC 50 NOAEC >0.0 1 mg LBA23

-000/L Chlorantraniliprole Technical Technical DuPont

17653 Daphnia magna

(Water flea) Acute EC 50 0.0 098 mg chlorantraniliprole/L

IN

- GAZ70 Technical

metabolite DuPont

18387 Daphnia magna

(Water flea) Acute EC 50 NOAEC >0.00987

0.00987 mg I

N

- 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 DuPont

18427 RV1 Daphnia magna

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

IN

-ECD73 Technical

metabolite DuPont

18472 Daphnia magna

(Water flea) Acute EC 50 NOAEC >0.013

0.0138 mg I

N

-ECD73/L

IN

-F6 L9 9 Technical

metabolite DuPont

18473 Daphnia magna

(Water flea) Acute EC 50 46.8 mg I N

-F6 L9 9/L

IN

-F9N04 Technical

metabolite DuPont

18474 Daphnia magna

(Water flea) Acute EC 50 0.03 mg I N

-F9N04/L Chlorantraniliprole Technical Technical DuPont

15877 Gammarus

pseudolimnaeus Acute LC50 0.0351 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

15114 Hyalella azteca Acute LC50 >0.389 mg chlorantraniliprole/L

Chlorantraniliprole Technical Technical DuPont

15873 Lumbriculus

variegatus (California blackworm) Acute LC50 >1.49 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

15872 Oronectes virilis

(Crayfish) Acute LC50 >1.42 mg chlorantraniliprole/L

Chlorantraniliprole Technical Technical DuPont

18804 Soyedina

carolinensis (Carolina Forestfly) Acute LC50 >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 DuPont

14278 Ictalurus

punctatus (Channel catfish) Acute LC50 >13.4 mg chlorantraniliprole/L

Chlorantraniliprole Technical Technical DuPont

12333 Lepomis

macrochirus (Bluegill sunfish) Acute LC50 >15.1 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

12332 Oncorhynchus

mykiss (Rainbow trout) Acute LC50 >13.8 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

14279 Oncorhynchus

mykiss (Rainbow trout) Chronic NOAEC 0.11 mg chlorantraniliprole/L

Chlorantraniliprole 35WG Formulated

Product DuPont

15396 Lepomis

macrochirus (Bluegill sunfish) Acute LC50 >1. 19 mg chlorantraniliprole/L

Chlorantraniliprole 20SC Formulated

Product DuPont

18602 Lepomis

macrochirus (Bluegill sunfish) Acute LC50 >1.84 mg chlorantraniliprole/L Chlorantraniliprole 35WG Formulated

Product DuPont

15386 Oncorhynchus

mykiss (Rainbow trout) Acute LC50 >1.09 mg chlorantraniliprole/L Chlorantraniliprole 20SC Formulated

Product DuPont

18601 Oncorhynchus

mykiss (Rainbow trout) Acute LC50 >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 DuPont

12335 Americamysis

bahia (Mysid shrimp) Acute LC50 1.15 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

14397 Americamysis

bahia (Mysid shrimp) Chronic NOAEC 0.695 mg chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

12412 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 DuPont

12334 Cyprinodon

variegatus (Sheepshead minnow) Acute LC50 >12.0 mg/L

Chlorantraniliprole Technical Technical DuPont

14394 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 DuPont

1 4390 Anabaena flos

aquae (Blue

-green algae) Growth /

Reproduction EC50

NOAEC >2

2 mg. chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

12409 RV1 Lemna gibba

(Duckweed) Growth /

Reproduction EC50

NOAEC >2

2 mg. chlorantraniliprole/L

Chlorantraniliprole Technical Technical DuPont

14392 RV1 Navicula

pelliculosa Growth /

Reproduction EC50

NOEC > 15.1

15.1 mg. chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

12408 RV1 Selenastrum

capricornutum (Green algae) Growth /

Reproduction EC50

NOEC >2

2 mg. chlorantraniliprole/L Chlorantraniliprole Technical Technical DuPont

14391 Skeletonema

costatum Growth /

Reproduction EC50

NOEC > 14.6

14.6 mg. chlorantraniliprole/L Chlorantraniliprole 20SC Formulated

Product DuPont

18088 Pseudokirchneriella

subcapitata (Green algae) Growth /

Reproduction EC50

NOEC >4

4 mg. chlorantraniliprole/L Chlorantraniliprole 35WG Formulated

Product DuPont

18089 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 LC 50>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 Grow th/reproduction

– Unicellular NOEC 1.78 mg/L Grow th

– Vascular NOEC 2 mg/L Most sensitive tested Most sensitive tested

## 48

V. RISK CHARACTERIZATION

A. Risk E

stimation

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 >5 620 500 <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 runof f 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 Semi

aquatic Areas g ai/ha Plant

Type Non

Listed Effects Endpoint (g/ha) Listed

Effects Endpoint (g/ha) Non

Listed RQ Listed

RQ

Ground Unincorp./100.8 g/ha 2.0160 11.0880 Monocot Dicot <300

>300 <300

<300 >0.0067

<0.0067 >0.03 7

>0.03 7

Ground Incorp/100.8 g/ha 2.0160 11.0880 Monocot Dicot <300

>300 <300

<300 >0.0067

<0.0067 >0.03 7

>0.03 7

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 Non

Listed Effects Endpoint (g/ha) Listed

Effects Endpoint (g/ha) Non

Listed RQ Listed

RQ

Ground Unincorp./100.8 g/ha 1.0080 Monocot Dicot >300

>300 <300

<300 <0.003 4

<0.003 4 >0.003 4

>0.003 4

Ground Incorp/100.8 g/ha 1.0080 Monocot Dicot >300

>300 <300

<300 <0.003 4

<0.003 4 >0.003 4

>0.003 4 Aerial /100.8 g/ha 5.0400 Monocot Dicot >300

>300 <300

<300 <0.01 7

<0.01 7 >0.01 7

>0.01 7



## 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 Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 f or Various Crop Types

Scenario Application Peak 60

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Ave Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 1 9 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 1 9 7 1.625 1.3 57 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 1 9 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=1 1.6 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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 60

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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=1 2,000 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 fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 60

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 1 9 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 1 9 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 1 9 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=1 2,000 μg/L 2

-Chronic Toxicity Endpoint= 1,280 μg/L * RQ = EEC/toxicity endpoint ** Acute RQs compared with acu te 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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 fromGround Spray Application of DPX

E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### RQ Chronic2



### RQ Identified

Concerns Rate (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 0.8 13 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 1 9 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 1 9 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 1 9 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 fromAerial Spray Application of DPX

E2Y45 for Various Crop Types

Scenario Application Peak Non

Listed RQ Listed

RQ Identified

Concerns Rate (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

-Li sted Toxicity Endpoint=> 2,000 μg/L 2

-Li sted Toxicity Endpoint= 2,000 μg/L * RQ = EEC/toxicity endpoint
** RQs compared with LOCs for non listed and listed species ( 1.0)

## 59

PRZM/EXAMS RQs for Vascular Plants fromGround Spray Application of DPX

E2Y45 for Various Crop Types

Scenario Application Peak Non

Listed RQ Listed

RQ Identified

Concerns Rate (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 0.09 8 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 1 9 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 1 9 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 1 9 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

-Li sted Toxicity Endpoint=> 2,000 μg/L 2

-Li sted 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 fromAerial Spray Application of DPX

E2Y45 for Various Crop Types

Scenario Application Peak Non

Listed RQ Listed

RQ Identified

Concerns Rate (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 0.0 038 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 0.0 009 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

-Li sted Toxicity Endpoint=> 1,780 μg/L 2

-Li sted Toxicity Endpoint= 1780 μg/L * RQ = EEC/toxicity endpoint
** RQs compared with LOCs for non listed a nd listed species ( 1.0)

## 61

PRZM/EXAMS RQs for Unicellular Plants from Ground Spray Application of DPX

E2Y45 for Various Crop Types

Scenario Application Peak Non

Listed RQ Listed

RQ Identified

Concerns Rate (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

-Li sted Toxicity Endpoint=> 1,780 μg/L 2

-Li sted 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. Quan tif

ied 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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### 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 0.0 99 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 fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### 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 0.03 15 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 RQ s 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 nurs ery (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 fromAerial Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### 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 3.00 1 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 3.2 71 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 0.6 74 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 fromGround Spray Application of DPX

-E2Y45 for Various Crop Types

Scenario Application Peak 21

-day Average Acute 1



### 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 non

target 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 ef fects on non

-target insects cannot be precluded.

## 68

V I

. 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 semi

aquatic plants

- monocots Yes4 

### Yes 1 

### all

Terrestrial and semi

aquatic plants

- dicots Yes4 

### Yes 1 

### all Terrestrial invertebrates Yes all No Birds No Yes 1,2,3 ,5 

### All Terrestrial phase
am phibians No Yes 1,2 ,5 

### All Reptiles No Yes 1,2,3 ,5 

### All Mammals No Yes 1,2,3 ,5 

### All Aquatic vascular plants No No Freshwater fish No Yes2 ,5 

### All Aquatic phase
am phibians 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 Yes 3 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 5direct 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 ty

pical 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

Assu med 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 7 8 % 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 estua rine/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. Analy tically, 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 1.82 1 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 0.451 612903225806 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 0.8 482 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 I ndex 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 0.09 67741935483871 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 1.2 88 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 0.677419354 83871 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 0.4 638 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 Metf ile: 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 I ndex 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 0.5 682 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 0.45 21 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 0.12903 2258064516 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 0.368 3 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 0.9677419354838 71 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 tor r 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 I ndex 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 0.1 171 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 1 968 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 0.1 429 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 0.09 529 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 0.145 6 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 0.9354838 70967742 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

- Novemeb er 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 I ndex 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 0.513 3 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 0.115 3 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 0.3548387 09677419 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: 0.134394333 333333 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 3 41.1355 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 I ndex 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 0.743 9 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 0.3 059 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 198 1 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 0.6 671 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 0.5 031 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 0.108 6 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 I ndex 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, 2 1 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 0.4 08 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 1.1 51 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

-lif e 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 I ndex 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 0.791 5 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 0.18 37 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 2 1 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 1.4 34 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 I ndex 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 1 968 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 0.321 6 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 0.25 8064516129032 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 0.71 24 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 0.3 975 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 0.80645161290322 6 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: Out put 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 I ndex 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 0.0698 7 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 19 83 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 0.0645161 290322581 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 0.1 087 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 0.61 924 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 I ndex 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 1 964 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 0.323 4 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 0.0 78 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 0.41935483 8709677 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 0.0820 3 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 I ndex 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 0.1 785 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 0.1 336 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 0.48 75 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 0.2580 64516129032 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 I ndex 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 3.1 67 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 2.6 68 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 I ndex 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 1.1 9 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 0.25 31 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 I ndex 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 0.1935483 87096774 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 0.483870967741 936 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 0.90322580645161 3 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: 0.2460803333 33333 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 I ndex 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 0.0645161290322 581 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 0.96774193548387 1 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 Hydrolysi s: 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 I ndex 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 0.2 64
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 0.5 997 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 0.7419354838709 68 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 I ndex 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 0.3 87096774193548 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 0.8387096774193 55 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 0.228 9

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: FLp eppersSTD.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 32 8 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: PLVK

RT PLDKRT 0.019804 FEXTRC 0.5 Flag for I ndex 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 1 974 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 2.2 5 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: FLp eppersSTD.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 63 1.76 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 I ndex 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 0.6 584 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 0.258064516 129032 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 0.27 35 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 EXAM S 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 I ndex 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 1.1 66 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 0.48387096774 1936 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 0.774193 548387097 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 I ndex 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 0.1 456 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 0.64 8 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 0.1 704 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

-lif e 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 I ndex 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 08:04:2 8 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 0.1 152 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 0.11 16 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 9 0 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 0.5 80645161290323 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 0.10 8 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 1 8 apprate 0.029 kg/ha Record 17: FILTRA

## 119 IPSCND UPTKF Record 18: PLVKRT

PLDKRT 0.019804 FEXTRC 0.5 Flag for I ndex 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 2.0 6 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 0.87096774193 5484 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 0.885 54 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 I ndex 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 0.2580645161290 32 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 0.0909 1 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 0.01 961 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 4 83.15 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 I ndex 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 19 66 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 0.66 16 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 0.4 356 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 0.06451612903 22581 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 0.90322580645 1613 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 I ndex Res. Run IR EPA Pond Flag for runof

f 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 1 974 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 0.15 33 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 0.1 216 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 0.3870967741935 48 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 0.0515 6 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 0.9354 83870967742 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

- Novemeb er 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 I ndex Res. Run IR EPA Pond Flag for runoff calc. RUNOFF none none, monthly or total(average of entire run) 

## MI Nursery

stored as MI

nursey.out Chemical: DPXE2Y45 PRZM environment: MI

nurserySTD.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 3.1 11 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 1.8 71 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 2.13 5 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 0.387096774193 548 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: MI

nursey Metfile: w14840.dvf PRZM scenario: MI nurserySTD.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

-lif e 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 I ndex 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 1 980 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 0.88 67 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 0.23 2 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 0.8387096774193 55 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 0.437 1 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 I ndex 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 0.0 7815 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 0.1 656 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 0.5483870967 74194 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 0.967741 935483871 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: w 14850.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

- 1 3 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 A pplication 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 I ndex 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 1.3 76 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 0.03225 8064516129 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 2.4 94 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 0.48387096774193 6 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 0.831 4 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 I ndex 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 1 967 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 0.377 3 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 0.65 75 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 I ndex 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 09:06:1 4 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 0.33 34 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 0.315 3 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 0.90322580645161 3 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 I ndex 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 0.2 893 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 0.7741935483 87097 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 A naerobic 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 I ndex 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 0.62 87 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 0.1935483870 96774 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 0.61290322 5806452 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 0.5 456 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 I ndex 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 0.2 186 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 0.0322 58064516129 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 0.20 81 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 0.5806451612 90323 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 0.1 887 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 32 8 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 I ndex 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

## 1 41 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 0.70967741 9354839 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 I ndex 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 Metf ile: 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

S orted 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 0.493 3 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 0.9677419 35483871 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 I ndex 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 0.531 4 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 196 8 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 0.21 32 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 0.83870967741935 5 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 I ndex Res. Run IR EPA Pond Flag f or 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 a t 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 0.771 6 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 0.9 544 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 0.29032258 0645161 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 0.7096774 19354839 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 I ndex 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 0.2 576 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 0.813 5 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 0.5 48387096774194 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 0.3 207 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 0.25 68 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 I ndex 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 0.5 8 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 0.7 076 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 0.8 785 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 0.367 1 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 0.677419354 83871 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 I ndex 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 0.7 594 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 0.2 81 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 0.3 242 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 0.3870967 74193548 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 I ndex 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 0.32258064516 129 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: 0.0161132 666666667 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 I ndex 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 0.5 773 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 0.8 017 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 0.0 8629

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 0.2903225 80645161 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

-lif e 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 I ndex 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 12:4 3:54 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 0.0089 5 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 1 972 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 0.001 722 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 0.0127 8 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 0.0032 32 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 I ndex 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: FLcabbageS TD.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 0.09 67741935483871 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 0.351 7 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 0.806451612903 226 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 I ndex 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 1 971 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 1 977 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

## 160 198 3 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 0.09 67741935483871 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 0.5483870967 74194 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 0.9 959 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: FLcucumb erSTD.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 I ndex 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 0.798 3 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 9 6 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 0.61290322580645 2 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 0.993 9 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: FLp eppersSTD.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 I ndex 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 1.1 93 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 0.0 7378 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 0.75 67 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 0.971 2 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 0.9354 83870967742 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 200 6
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 20 8 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 I ndex 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 modif ied 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 0.217 8 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 0.293 8 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 0.1290322 58064516 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 S et 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 I ndex 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 0.4 636 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 0.0930 3 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 0.387096774193 548 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 0.025 22 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 Ef

ficiency: 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 I ndex 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 Metf ile: 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 0.6 381 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 0.57 51 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 0.4 51612903225806 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: pond29 8.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 man ual 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 0.0198 04 FEXTRC 0.5 Flag for I ndex 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 19 67 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 0.11 09 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 I ndex 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 4.8 62 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 0.0967 741935483871 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 0.83 8709677419355 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 0.15 81 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 I ndex 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 0.43 17 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 0.288 6 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 0.555 555555555556 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 0.153 7 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 I ndex 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 0.8 478 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 0.70 12 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 2.6 08 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 0.393 5 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 I ndex 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 0.5 574 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 0.63 46 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 0.6774193548387 1 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 ra te 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 I ndex 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 0.17 16 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 0.1 294 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 0.03 55 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 0.06451 61290322581 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 0.21 55 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 0.0 6874 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 0.61290322 5806452 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 0.1 225 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 0.3 689 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 I ndex 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 0.3 695 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 0.4193548 38709677 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 0.3 196 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 0.18 6 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 I ndex 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 0.336 1 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 0.3 87096774193548 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 0.091 86 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 kbac s 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 I ndex 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 Typ es Reported 

# broccoli, brussels sprouts, cabbage

- head, cauliflower, celery, chinese cabbage, collards, escarole and endive, kale, lettuce, all, lettuce, head, lettuce, lea

f, 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, &W A 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, W I, 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

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 1 of 15

## 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, W I, 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 cro ps. 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 c rops. 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 2 of 15

## 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, W I, 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 I nsect 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 indicate d 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 in dicated 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 sp ecies 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 3 of 15

## 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, W I, WY The taxa Fish has 4 species co

-occurring with ind icated 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

-occurri ng 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 I nsect 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, W I, WY The taxa Bird has 1 species co

-occurring with indicated crops. The taxa D icot 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. 

## Il linois 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 Rept ile 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 5 of 15

## 189 AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, IL, IN, IA, KS, KY, LA, M E, 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, W I, WY The taxa Gastropod has 1 species co

-occurring with indicated crops. The taxa Mammal has 1 species co

-occurring with indi cated 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

-occurri ng 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 s pecies 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 6 of 15

## 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, W I, 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 Fis h 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 indi cated 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 speci es 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 7 of 15

## 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, W I, 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 spe cies 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, W I, WY The taxa Bird has 3 species co

-occurring with indicated crops. The taxa Dicot has 2 species co

-occurrin g 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 i ndicated 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

-occurrin g 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 spe cies co

-occurring with indicated crops.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 9 of 15

## 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, W I, 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 in dicated 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 10 of 15

## 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, W I, 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 M onocot 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

-occurri ng 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 spe cies 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 11 of 15

## 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, W I, 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

-occurrin g 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 s pecies 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 Repti le 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 12 of 15

## 196 AL, AK, AZ, AR, CA, CO, CT, DE, DC, FL, GA, HI, ID, I L, 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, W I, 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 T he 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 Fi sh 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.
Th e taxa Monocot has 3 species co

-occurring with indicated crops. The taxa Reptile has 6 species co

-occurring with indicated crops.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 13 of 15

## 197 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, W I, 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 14 of 15

## 198 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, N D, OH, OK, OR, PA, PR, RI, SC, SD, TN, TX, UT, VT, VA, WA , WV, W I, 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.
Th e 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.

12/4/2007 10:34:09 AM Ver. 2.10.3 Page 15 of 15

## 199