Document ID: EPA-HQ-OPP-2007-0327-0003
Agency: epa
Document Type: Supporting & Related Material
Title: 
Posted Date: 2007-08-29T04:00Z

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY

WASHINGTON D.C., 20460

OFFICE  OF 

PREVENTION, PESTICIDES AND 

TOXIC SUBSTANCES

DP Barcode:	319075

PC Code:	128940

December 29, 2005

MEMORANDUM

SUBJECT: 	Section 18 Ecological Risk and Drinking Water Exposure
Assessment for the Control of Soybean Rust Using Flutriafol (Impact ( ,
125SC)

FROM:	Thuy Nguyen, Senior Scientist, ERB III

Environmental Fate and Effects Division (7507C)	

THROUGH:    	Daniel Rieder, Branch Chief, ERB III

Environmental Fate and Effects Division (7507C)	

TO:	Daniel Rosenblatt, Risk Manager

Carmen Rodia, Risk Manager Reviewer 

MUIERB

Registration Division (7505C)

The EFED has reviewed the emergency exemption request from the Minnesota
and South Dakota Departments of Agriculture to use Flutriafol for the
control of Australasian soybean rust.  This is the first section 18
request for this use.  Flutriafol (Impact (, 125SC), a product of
Cheminova Inc, could be applied via ground or aerial spray at a rate of
0.91 oz a.i./A (0.0569 lb a.i./A) per application.  A maximum of 2
applications is allowed per year with an assumed 7-day interval between
application.

Please note that no Subdivision E, J and/or N Guideline studies were
submitted with this request.  Risk assessed and presented in this
document was solely based on the non guideline studies submitted by the
Registrant, Cheminova Inc.  According to the fate and ecological effects
data extracted from these non guidelines studies, EFED concludes that
the proposed use of this fungicide to control soybean rust  presents
potential risks to non target birds and mammals, specifically
Federally-listed endangered and threatened species.  This assessment
includes the following:

-  summary of potential risks associated with the use of flutriafol
(Section I); and  

-  water assessment for the use of flutriafol on soybean (Section II).

Although this risk assessment addresses the specific requests from
Minnesota and South Dakota, the analysis of exposure and potential risks
in this report was approached from the perspective of a “national”
new use assessment, except for estuarine/marine invertebrates.  The
assessment of potential ecological risks for flutriafol is based on the
use rate, the numbers of application, and the interval between
applications outlined in the Minnesota and South Dakota Section 18
request.  Higher rates, more frequent applications, or different
intervals for Section 18 requests to control soybean rust from other
states, especially those associated with estuarine or marine habitant,
are likely to change the conclusions concerning potential risks to
terrestrial and aquatic non-target organisms that are outlined below. 

I.   SUMMARY OF RISKS 

A summary of potential risks associated with flutriafol use to control
soybean rust is provided below and in Table I-1.  Note that no
Subdivision E, J, and/or N Guideline studies were submitted for review
in conjunction with this section 18 request, and risk presumed in this
assessment was solely based on the non guideline studies submitted by
the Registrant, Cheminova Inc. 

The estimation of the Estimated Environmental Concentration (EEC) values
for aquatic exposure are described in section II.  Note that although
this is a request for a Section 18 in Minnesota and South Dakota, the
analysis of exposure was approached from the perspective of a
“national” new use assessment, and the aquatic EECs were calculated
using modeling scenarios simulated in areas with the highest soybean
acreage and the highest level of runoff vulnerability: Georgia,
Michigan, and Mississippi.  The EEC values for terrestrial exposure were
derived from the upper bound Kenaga exposure values of the Kenaga
nomograph, which is based on a large set of actual field residue data
and modified by Fletcher et al. (1994).  These values represent how much
pesticide residue might be expected on various types of plants and
insects that may serve as food items for birds and mammals foraging in
and about the vicinity of the treated areas . All EECs were calculated
at the highest application rate of 0.0569 lbs ai/A, 2 applications, and
a 7-day reapplication interval.

Table I-1 -  Summary of risks for the use of Flutriafol to control rust
on soybeans

	

Acute Risk	

Chronic Risk

Birds	

RQ = 0.07 (1000g, short grass)*	

No data.  Cannot be assessed

Terrestrial Mammals	

RQ = 0.06 (15g, short grass)*

RQ = 0.05 (35g, short grass)*	

No data.  Cannot be assessed

Terrestrial Plants	

No data.  Cannot be assessed	

No data.  Cannot be assessed

Freshwater Organisms	

No LOC exceedance	

No LOC exceedance

Freshwater Plants - Vascular	

No data.  Cannot be assessed	

No data.  Cannot be assessed

Aquatic Plants - Vascular	

No LOC exceedance	

No data.  Cannot be assessed

* Exceed Acute Endangered Species LOC of 0.05.



Note that no toxicity data were available from the Registrant’s
submission to assess risks to estuarine/marine invertebrates.  Since
this request is for Minnesota and South Dakota, the use of flutriafol on
soybean may not enter the estuarine/marine environment and cause
potential risk to the associated aquatic organism, and therefore the
estuarine/marine tests could be waived for this request.  However, these
tests may be required if future Section 18s for flutriafol use on
soybean are requested for states/use sites associated with estuarine or
marine habitant.

Potential Risks from Flutriafol Exposure

Birds, Acute Exposure - Based on the upper bound exposure at an
application rate of 0.0569 lbs a.i./Acre (2 applications, 7-day
reapplication interval), the RQ was 0.07 (large birds, short grass food
item), which exceeds the acute endangered species LOC of 0.05.  EECs
based on other food items or bird size classes did not result in LOC
exceedances.  A reduction in the maximum application rate from 0.0569
lbs a.i./Acre to 0.0375 lbs a.i./Acre would result in no acute avian LOC
exceedance.  Application rates of 0.04 lbs a.i./Acre and 0.0425 lbs
a.i./Acre would not result in LOC exceedance if the re-application
interval was 14 or 21 days, respectively.  A single application at the
maximum application rate of 0.0569 lb ai/A does not result in acute
avian LOC exceedance. 

EFED used the default foliar dissipation half-life of 35 days to
estimate residue levels remaining from the first application at the time
of the second application because no appropriate foliar dissipation
half-life data were available for use in deriving EECs. 

Note that there is no LOC exceedance when the EECs were calculated based
on the mean Kenaga values.

	

Birds, Chronic Exposures - No chronic avian data were available for use
in RQ calculations.  Therefore chronic risks to bird cannot be assessed.

Terrestrial Mammals, Acute Exposures.  Based on the highest proposed
application rate for soybeans of 0.0569 lbs a.i./Acre (2 applications,
7-day reapplication interval), acute RQs are 0.06 and 0.05 for 15g and
35g herbivores, respectively , feeding on short grass. These RQs exceeds
the acute endangered species LOC of 0.05.  The RQs based on other food
items, large herbivores, all insectivores, and all granivores were below
the LOC.  A reduction in the maximum application rate from 0.0569 lbs
a.i./Acre to 0.0413 lbs a.i./Acre would result in no acute mammals LOC
exceedances.  Application rates of 0.0438 lbs a.i./Acre and 0.0465 lbs
a.i./Acre would not result in LOC exceedances if the re-application
interval was 14 or 21 days, respectively.  Also, a single application at
the maximum application rate of 0.0569 lb ai/Acre will reduce all RQs
below the acute LOC.

Note that there is no LOC exceedance when the EECs were calculated
based on the mean Kenaga values.

Terrestrial Mammals, Chronic Exposures.  No chronic mammal data were
available for use in RQ calculations.  Therefore chronic risks to
terrestrial mammals cannot be assessed.

Terrestrial Plants.  No toxicity data were available for use in RQ
calculations for terrestrial plants.  Therefore risks to terrestrial
plants cannot be assessed.

Aquatic Organisms, Acute Exposure.  No acute LOCs were exceeded for
freshwater organisms.  Using the most sensitive toxicity endpoint among
all freshwater organisms (LC50 of 890 ppb from freshwater invertebrates)
and the highest peak aquatic exposure (EEC of 25 ppb from the GA Soybean
scenario), no RQ exceeds the LOC.  Therefore, it is expected that
flutriafol at application rate proposed for this Emergency Exemption Use
request does not pose acute risk to freshwater fish or invertebrates at
the Agency’s concern levels.

Aquatic Organisms, Chronic Exposure.   No chronic LOCs were exceeded for
freshwater organisms.  The lowest reported NOAEC in these aquatic
organisms was 310 ppb (daphnia).  This value is approximately 10-fold 
higher than the highest peak aquatic EEC of 25 ppb (GA scenario). 
Therefore, it is expected that flutriafol at application rate proposed
for this Emergency Exemption Use request does not pose chronic risk to
fish or invertebrates at the Agency’s concern levels.

Aquatic Plants.  The lowest algal EC50 was 1900 ppb.  This value is
substantially higher than the highest peak aquatic EEC of 25 ppb (GA
scenario), which indicates no acute risks to non vascular plants. 
Chronic toxicity data for non vascular plants and toxicity data for
other aquatic plant species are not available in the sources used for
this assessment, therefore associated risks could not be evaluated.

Co-Location of Endangered Species

A summary of the number of endangered species located (county level)
where soybeans are produced is presented below.  Individual endangered
or threatened bird and mammal species located in counties that produce
soybeans are identified in Appendix C.  Only avian endangered species
LOCs were exceeded; however, potential indirect effects on species that
depend on birds for survival or reproduction cannot be ruled out at this
time. 

II.  WATER ASSESSMENT FOR THE USE OF FLUTRIAFOL ON SOYBEAN

Surface Water Modeling

A Tier II water assessment was conducted for the proposed use of
flutriafol on soybeans using the proposed maximum application rate for
soybean;  0.0569 lbs ai/acre with 2 applications at 7 days interval
(assumed because not specified).   

Modeling of the Estimated Drinking Water Concentrations (EDWC) and
Estimated Environmental Concentrations (EEC) were generated using PRZM3
(Vers. 3.12 beta compiled(05/24/01, Carsel, 1997) and EXAMS (Vers.
2.98.04 compiled 07/18/04, Burns, 2002).  PRZM simulates pesticide fate
and transport as a result of leaching, direct spray drift, runoff and
erosion from an agricultural field and EXAMS estimates environmental
fate and transport of pesticides in a surface water body for a 30-year
period (1961 to 1990).  Standard soybean cropping scenarios for three
states with the highest soybean acreage and highest runoff vulnerability
were simulated to represent the national use of flutriafol on this crop:
Georgia, Michigan, and Mississippi. 

The EECs for surface water uses a single site or multiple sites, which
typically represents a high-end exposure scenario from pesticide use on
a particular crop or noncrop use site.  PRZM and EXAMS were linked by
the program (PE4-PL, ver. 01).   Detailed description, documentation,
and direct links for running these models can be found in:
http://www.epa.gov/oppefed1/models/water/index.htm.  The standard
scenario for ecological exposure simulates the fate of a pesticide
transported as a result of runoff and erosion, and or spray drift from
an 10-ha agricultural field directly into a surface water body (PRZM).
The small field is assumed to be 100% cropped. The surface water body in
which the EECs are simulated (EXAMS) is the standard pond (10,000-m2
pond, 2-m deep).  

The Index Reservoir (IR) is intended as a drop-in replacement for the
standard pond for use in drinking water exposure assessment.  It is used
in a manner similar to the standard pond, except that flow rates have
been modified to reflect local weather conditions.  Guidance for using
the IR is located at: http://www.epa.gov/pesticides/trac/science/.  The
index reservoir (IR)  is approximately 82 m wide and 640 m long, with an
area of 5.3 ha. (USEPA, 2000).  The area of the entire watershed is
172.8 ha.  Weather and agricultural practices are simulated for 30 years
so that the 10-year exceedance probability at the site can be estimated.
The simulation was generated using 30 years of meteorological data,
encompassing the years from 1961 to 1990.

The Percent Crop Area (PCA) is a generic watershed-based adjustment
factor that will be applied to pesticide concentrations estimated for
the surface water component of the drinking water exposure assessment
using PRZM/EXAMS with the index reservoir (IR) only.  No adjustment was
made for the standard pond runs.  The output generated by the linked
PRZM/EXAMS models is multiplied by the maximum percent of crop area
(PCA) in any watershed (expressed as a decimal) generated for the crop
or crops of interest.  Currently, OPP will apply PCA adjustments for
four major crops, one of which is soybeans. The default PCA factor for
soybeans is 0.41.  Guidance for using PCAs and a thorough discussion of
this method and comparisons of monitoring and modeling results for
selected pesticide/crop/site combinations is located at:
http://www.epa.gov/pesticides/trac/science/. 

Table II-1 presents the input parameters used in the PRZM/EXAMS
modeling. The estimated concentrations of flutriafol in surface drinking
water (EDWCs) are presented in Table II-2 and for aquatic exposure
(EECs) in Table II-3.  Print outs of the surface water modeling runs are
listed in Appendix A.

Ground Water Modeling

The SCI-GROW model version 2.3 was used to estimate the concentration of
flutriafol in ground water.  SCI-GROW estimated the concentration of
flutriafol in shallow ground water sources to be less than 1 μg/L. 
Input parameters for SCI-GROW are also presented in Table II-1. Note
that no PCA adjustment is required for SCI-GROW.  Print outs of the
surface water modeling runs are listed in Appendix B.

Environmental Fate

Flutriafol is a systemic fungicide with eradicating action.  Similar to
all triazoles, flutriafol acts as a steroid demethylation inhibitor,
causing fungal cell wall to collapse and inhibiting hyphal growth. 

The vapor pressure of flutriafol indicates that volatility is not a
major route of degradation for this chemical in the environment. 
Hydrolysis and aqueous photolysis are also very slow.  In soil,
flutriafol is quite persistent, with a half life value of more than one
year. No significant degradation products were identified in either
water or soil studies.  As indicated by the adsorption/desorption
coefficients, flutriafol is moderately mobile in the laboratory tested
soils.  Field studies show that there is minimal potential for
flutriafol to significantly leach to ground water under practical use
conditions.   

Key chemical-physical and environmental fate properties of flutriafol
used in the surface and ground water modeling are summarized in Table
II-1.  The environmental fate data and physical and chemical properties
(Table II-1) were selected from the available non guideline study
reports in accordance with Guidance for Selecting Input Parameters in
Modeling the Environmental Fate and Transport of Pesticides, Version II,
February 28, 2002. Detailed description, documentation, and direct links
for running these models can be found in:

http://www.epa.gov/oppefed1/models/water/index.htm

Table II-1.  PRZM/EXAMS and SCI-GROW Input Parameters for Flutriafol use
on Soybean.

Parameter	

Value and Unit	

Source

Max. application rate	

2 applications @ 0.0569 lb ai/acre	

Section 18 request

Maximum # of applications	

2	

Section 18 request

Reapplication Interval	

7 and 14 days	

not provided so assumed

Application Efficiency (APPEFF)	

0.95 - aerial spray	

EFED Guidance

Spray Drift (DRFT) 	

0.05 eco-aerial spray (as)

0.16 drinking water as	

EFED Guidance

Chemical Application Method (CAM)	

2 (foliar application)	

Proposed use

Molecular Formula

Mole Wt. g/mol	

C16H13F2N3O

301.3	

1

Henry’s Law Constant (20(C)

Vapor Pressure (calculated)	

1.3 x 10-11 atm x m3 x mol-1

4 x 10-7 Pa at 20(C	

1

Solubility in water	

95 mg/L (20(C in water)	

1

Partition Coefficients [sorption-desorption]  Freundlich Kf mL/g	

1.3 - 9.8 ( n=5)

	

1

Partition Coefficients

Koc mL/g	

123, 157, 295, 304, 395 (mean=255; n=5) 1/n=0.94-0.97

PRZM/EXAMS = 255 (mean)

SCI-GROW input = 295 (median)	

1

Hydrolysis	

stable in buffered solutions at pH 4, 7, and 9 at 25 C within 30 days
incubation in dark	

1

Aqueous photolysis	

stable in aqueous buffer solution (pH 7) at 25 C for periods up to the
equivalent of 66 days FL summer sunlight	

1

Aerobic soil metabolism 

[half-life] days	

1747 (mean first order; 672-3492 days, n=10)

PRZM/EXAMS, SCI-GROW = 1747

 (mean, no raw data (only range) were available to calculate 90th
percentile of mean)	

1

Anaerobic aquatic  metabolism

[half-life] days	

no data; compound stable to hydrolysis

PRZM/EXAMS =3500 ( 2 x aerobic soil metabolism)	

1

Soil photolysis	

stable to sunlight of soil surfaces	

1

Aerobic aquatic metabolism	

no data	

1

1- Cheminova A/S- Document N (Tier 3), July 2004

The Tier II assessment for flutriafol concentrations in Table II-2 are
the 1-in-10-year annual exceedance probability for peak (acute), annual
daily average (chronic), and overall daily average (cancer)
concentrations in the Index Reservoir for 2 aerial applications applied
at the maximum proposed rate of 0.0569 lb a.i./Acre each, at 7-day
interval between application, for 30 years. 



Table II-2.  Tier II PRZM/EXAMS Flutriafol Estimated Drinking Water
Concentrations  (EDWCs) in Index Reservoir corrected for percent crop
area (PCA = 0.41 for soybeans), based on 2 aerial applications of 0.0569
lb a.i./Acre each, and 7-day interval between application

	

1-in-10 year EDWC (ug/L)

Scenario	

Acute	

Chronic	

Cancer

MI Bean	

4	

2	

1

GA Soybean	

3	

1	

<1

MS Soybean	

2	

1	

<1

Tier II assessment flutriafol concentrations in Table II-3 represent the
1-in-10-year annual exceedance probability for peak, 96-hr, 21-day,
60-day, and  90-day in the standard farm pond for ground and aerial
applications applied at the maximum proposed rate for 30 years.

Table II-3. Tier II PRZM/EXAMS Flutriafol Estimated Environmental
Concentrations (EECs) in Standard Farm Pond, based on 2 aerial
applications of 0.0569 lb a.i./Acre each, and 7-day interval between
application

	

1-in-10 year EEC (ug/L)

Scenario	

Peak	

96-hr	

21-day	

60-day	

90-day

GA Soybean	

25	

25	

25	

24	

24

MI Bean	

17	

17	

17	

17	

17

MS Soybean	

11	

11	

11	

11	

11



Additional Citations

EPA. 1999.  Jones, R.D., J. Breithaupt, J. Carleton, L. Libelo, J. Lin,
R. Matzner, and R. Parker. Guidance for Use of the Index Reservoir in
Drinking Water Exposure Assessments. Environmental Fate and Effects
Division, Office of Pesticide Programs, U.S. Environmental Protection
Agency, Washington. D.C. 

USDA. 2005. A Coordinated Framework for Soybean Rust Surveillance,
Reporting, Prediction, Management and Outreach. page 24, 
http://www.aphis.usda.gov/ppq/ep/soybean_rust/coordfram041405.pdf

Appendix A.  PRZM/EXAMS printouts

PRZM environment: GAsoybeanC.txt	modified Friday, 14 October 2005 at
15:22:04

EXAMS environment: ir298.exv	modified Thuday, 29 August 2002 at 15:34:12

Metfile: w93805.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	1.539	1.487	1.304	0.8502	0.7725	0.2525

1962	3.733	3.6	3.215	2.472	2.137	0.8471

1963	5.343	5.161	4.472	3.323	2.831	0.9915

1964	6.327	6.168	5.358	4.368	3.885	1.444

1965	4.469	4.316	4.072	3.501	3.086	1.314

1966	7.962	7.676	6.975	5.37	4.444	1.465

1967	2.98	2.879	2.5	2.076	1.905	0.896

1968	5.382	5.199	4.863	4.125	3.661	1.35

1969	15.85	15.31	13.22	9.803	8.075	2.477

1970	3.073	2.988	2.666	2.109	1.802	1.078

1971	2.304	2.226	1.939	1.516	1.379	0.5352

1972	3.998	3.86	3.391	2.798	2.049	0.7695

1973	2.332	2.257	1.979	1.56	1.451	0.8974

1974	4.364	4.233	3.899	3.088	2.574	0.9386

1975	2.801	2.702	2.497	2.247	1.946	0.7621

1976	6.763	6.524	5.72	4.386	3.63	1.177

1977	1.82	1.768	1.568	1.229	1.043	0.6177

1978	1.18	1.141	0.852	0.7453	0.6717	0.3034

1979	4.071	3.926	3.431	2.63	2.285	0.8537

1980	2.015	1.945	1.737	1.582	1.423	0.644

1981	2.016	1.956	1.834	1.463	1.35	0.553

1982	2.682	2.588	2.241	1.806	1.566	0.6014

1983	2.721	2.628	2.459	1.732	1.474	0.6236

1984	1.782	1.725	1.512	1.159	0.9702	0.618

1985	4.985	4.84	4.197	3.439	2.514	0.8286

1986	2.295	2.214	2.046	1.653	1.578	0.9453

1987	2.573	2.484	2.153	1.493	1.235	0.6351

1988	2.565	2.476	2.146	1.72	1.625	0.7578

1989	4.306	4.154	3.626	2.899	2.462	0.9144

1990	1.979	1.911	1.704	1.461	1.259	0.6107

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	15.85	15.31	13.22	9.803	8.075	2.477

0.0645161290322581	7.962	7.676	6.975	5.37	4.444	1.465

0.0967741935483871	6.763	6.524	5.72	4.386	3.885	1.444

0.129032258064516	6.327	6.168	5.358	4.368	3.661	1.35

0.161290322580645	5.382	5.199	4.863	4.125	3.63	1.314

0.193548387096774	5.343	5.161	4.472	3.501	3.086	1.177

0.225806451612903	4.985	4.84	4.197	3.439	2.831	1.078

0.258064516129032	4.469	4.316	4.072	3.323	2.574	0.9915

0.290322580645161	4.364	4.233	3.899	3.088	2.514	0.9453

0.32258064516129	4.306	4.154	3.626	2.899	2.462	0.9386

0.354838709677419	4.071	3.926	3.431	2.798	2.285	0.9144

0.387096774193548	3.998	3.86	3.391	2.63	2.137	0.8974

0.419354838709677	3.733	3.6	3.215	2.472	2.049	0.896

0.451612903225806	3.073	2.988	2.666	2.247	1.946	0.8537

0.483870967741936	2.98	2.879	2.5	2.109	1.905	0.8471

0.516129032258065	2.801	2.702	2.497	2.076	1.802	0.8286

0.548387096774194	2.721	2.628	2.459	1.806	1.625	0.7695

0.580645161290323	2.682	2.588	2.241	1.732	1.578	0.7621

0.612903225806452	2.573	2.484	2.153	1.72	1.566	0.7578

0.645161290322581	2.565	2.476	2.146	1.653	1.474	0.644

0.67741935483871	2.332	2.257	2.046	1.582	1.451	0.6351

0.709677419354839	2.304	2.226	1.979	1.56	1.423	0.6236

0.741935483870968	2.295	2.214	1.939	1.516	1.379	0.618

0.774193548387097	2.016	1.956	1.834	1.493	1.35	0.6177

0.806451612903226	2.015	1.945	1.737	1.463	1.259	0.6107

0.838709677419355	1.979	1.911	1.704	1.461	1.235	0.6014

0.870967741935484	1.82	1.768	1.568	1.229	1.043	0.553

0.903225806451613	1.782	1.725	1.512	1.159	0.9702	0.5352

0.935483870967742	1.539	1.487	1.304	0.8502	0.7725	0.3034

0.967741935483871	1.18	1.141	0.852	0.7453	0.6717	0.2525

0.1	6.7194	6.4884	5.6838	4.3842	3.8626	1.4346

Average of yearly averages:	0.890053333333334

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flusbi

Metfile:	w93805.dvf

PRZM scenario:	GAsoybeanC.txt

EXAMS environment file:	ir298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3600	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.0637	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.16	fraction of application rate applied to pond

Application Date	Date	01-09	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	IR

Flag for runoff calc.	RUNOFF	total	none, monthly or total(average of
entire run)

----------------

PRZM environment: MIbeansC.txt	modified Monday, 10 May 2004 at 07:24:24

EXAMS environment: ir298.exv	modified Thuday, 29 August 2002 at 15:34:12

Metfile: w14826.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	5.639	5.565	5.318	4.933	4.654	1.646

1962	3.187	3.16	3.049	2.826	2.676	2.142

1963	2.42	2.394	2.328	2.285	2.191	1.565

1964	2.495	2.467	2.356	2.141	2.072	1.487

1965	5.198	5.133	4.882	4.666	4.393	2.318

1966	3.098	3.073	2.968	2.753	2.609	2.161

1967	2.8	2.768	2.643	2.523	2.54	1.736

1968	9.874	9.763	9.299	8.375	7.798	3.644

1969	5.268	5.225	5.053	4.702	4.456	3.236

1970	4.187	4.143	3.995	3.914	3.766	2.395

1971	2.964	2.939	2.839	2.635	2.498	2.043

1972	3.424	3.389	3.311	3.185	3.096	1.986

1973	3.548	3.507	3.389	3.269	3.283	2.138

1974	3.011	2.983	2.873	2.658	2.51	2.062

1975	11.89	11.78	11.48	10.56	9.851	4.105

1976	6.486	6.431	6.209	5.752	5.442	4.164

1977	3.444	3.417	3.304	3.077	2.938	2.538

1978	3.491	3.466	3.343	3.064	2.877	1.986

1979	2.257	2.238	2.161	2.002	1.901	1.581

1980	3.427	3.388	3.241	2.972	2.797	1.674

1981	4.722	4.669	4.475	4.235	4.057	2.34

1982	3.273	3.238	3.192	3.062	3.032	2.367

1983	3.71	3.667	3.519	3.364	3.196	2.18

1984	2.794	2.764	2.652	2.529	2.461	1.944

1985	9.035	8.925	8.509	7.739	7.224	3.259

1986	9.777	9.676	9.429	8.8	8.316	4.942

1987	6.892	6.815	6.587	6.029	5.727	4.571

1988	4.695	4.646	4.472	4.176	4.117	3.3

1989	5.335	5.274	5.051	4.598	4.38	2.976

1990	3.756	3.717	3.571	3.452	3.408	2.602

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	11.89	11.78	11.48	10.56	9.851	4.942

0.0645161290322581	9.874	9.763	9.429	8.8	8.316	4.571

0.0967741935483871	9.777	9.676	9.299	8.375	7.798	4.164

0.129032258064516	9.035	8.925	8.509	7.739	7.224	4.105

0.161290322580645	6.892	6.815	6.587	6.029	5.727	3.644

0.193548387096774	6.486	6.431	6.209	5.752	5.442	3.3

0.225806451612903	5.639	5.565	5.318	4.933	4.654	3.259

0.258064516129032	5.335	5.274	5.053	4.702	4.456	3.236

0.290322580645161	5.268	5.225	5.051	4.666	4.393	2.976

0.32258064516129	5.198	5.133	4.882	4.598	4.38	2.602

0.354838709677419	4.722	4.669	4.475	4.235	4.117	2.538

0.387096774193548	4.695	4.646	4.472	4.176	4.057	2.395

0.419354838709677	4.187	4.143	3.995	3.914	3.766	2.367

0.451612903225806	3.756	3.717	3.571	3.452	3.408	2.34

0.483870967741936	3.71	3.667	3.519	3.364	3.283	2.318

0.516129032258065	3.548	3.507	3.389	3.269	3.196	2.18

0.548387096774194	3.491	3.466	3.343	3.185	3.096	2.161

0.580645161290323	3.444	3.417	3.311	3.077	3.032	2.142

0.612903225806452	3.427	3.389	3.304	3.064	2.938	2.138

0.645161290322581	3.424	3.388	3.241	3.062	2.877	2.062

0.67741935483871	3.273	3.238	3.192	2.972	2.797	2.043

0.709677419354839	3.187	3.16	3.049	2.826	2.676	1.986

0.741935483870968	3.098	3.073	2.968	2.753	2.609	1.986

0.774193548387097	3.011	2.983	2.873	2.658	2.54	1.944

0.806451612903226	2.964	2.939	2.839	2.635	2.51	1.736

0.838709677419355	2.8	2.768	2.652	2.529	2.498	1.674

0.870967741935484	2.794	2.764	2.643	2.523	2.461	1.646

0.903225806451613	2.495	2.467	2.356	2.285	2.191	1.581

0.935483870967742	2.42	2.394	2.328	2.141	2.072	1.565

0.967741935483871	2.257	2.238	2.161	2.002	1.901	1.487

0.1	9.7028	9.6009	9.22	8.3114	7.7406	4.1581

Average of yearly averages:	2.5696

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flubmi

Metfile:	w14826.dvf

PRZM scenario:	MIbeansC.txt

EXAMS environment file:	ir298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3500	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.0637	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.16	fraction of application rate applied to pond

Application Date	Date	27-07	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	IR

Flag for runoff calc.	RUNOFF	total	none, monthly or total(average of
entire run)

-------------------------

PRZM environment: MSsoybeanC.txt	modified Satday, 12 October 2002 at
17:07:44

EXAMS environment: ir298.exv	modified Thuday, 29 August 2002 at 15:34:12

Metfile: w13893.dvf	modified Wedday, 3 July 2002 at 09:06:20

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	3.177	3.101	2.853	2.505	1.856	0.5011

1962	2.383	2.325	2.113	1.843	1.672	1.086

1963	1.567	1.529	1.383	1.205	1.08	0.6425

1964	2.107	2.059	1.972	1.709	1.61	0.8389

1965	3.327	3.263	3.118	2.631	2.296	1.103

1966	2.448	2.388	2.168	1.789	1.629	0.9192

1967	2.488	2.43	2.265	1.69	1.527	0.7947

1968	5.557	5.417	4.952	4.326	3.882	1.586

1969	3.375	3.294	3.018	2.254	1.735	1.143

1970	2.798	2.736	2.498	2.081	1.87	1.28

1971	1.784	1.743	1.608	0.9949	0.9401	0.652

1972	4.497	4.383	3.959	3.758	3.446	1.3

1973	2.691	2.626	2.448	2.131	1.962	1.218

1974	1.418	1.386	1.351	1.209	1.076	0.6875

1975	2.606	2.553	2.347	2.088	1.891	0.8271

1976	4.181	4.083	3.753	3.294	3.28	1.417

1977	4.241	4.149	3.863	3.241	2.935	1.41

1978	3.744	3.661	3.448	2.545	2.076	1.091

1979	2.86	2.798	2.556	2.117	2.047	1.368

1980	3.255	3.173	2.88	2.713	2.568	1.187

1981	6.088	5.936	5.639	4.677	3.794	1.484

1982	3.453	3.39	3.139	2.704	2.51	1.54

1983	3.006	2.936	2.765	2.258	1.924	1.068

1984	2.207	2.154	2.002	1.768	1.583	0.9988

1985	1.735	1.693	1.581	1.461	1.395	0.7179

1986	6.986	6.869	6.289	5.184	4.018	1.342

1987	5.003	4.884	4.541	3.722	2.9	1.821

1988	3.251	3.182	2.914	2.426	2.137	1.459

1989	3.993	3.898	3.582	3.445	3.225	1.394

1990	3.706	3.624	3.315	2.973	2.727	1.363

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	6.986	6.869	6.289	5.184	4.018	1.821

0.0645161290322581	6.088	5.936	5.639	4.677	3.882	1.586

0.0967741935483871	5.557	5.417	4.952	4.326	3.794	1.54

0.129032258064516	5.003	4.884	4.541	3.758	3.446	1.484

0.161290322580645	4.497	4.383	3.959	3.722	3.28	1.459

0.193548387096774	4.241	4.149	3.863	3.445	3.225	1.417

0.225806451612903	4.181	4.083	3.753	3.294	2.935	1.41

0.258064516129032	3.993	3.898	3.582	3.241	2.9	1.394

0.290322580645161	3.744	3.661	3.448	2.973	2.727	1.368

0.32258064516129	3.706	3.624	3.315	2.713	2.568	1.363

0.354838709677419	3.453	3.39	3.139	2.704	2.51	1.342

0.387096774193548	3.375	3.294	3.118	2.631	2.296	1.3

0.419354838709677	3.327	3.263	3.018	2.545	2.137	1.28

0.451612903225806	3.255	3.182	2.914	2.505	2.076	1.218

0.483870967741936	3.251	3.173	2.88	2.426	2.047	1.187

0.516129032258065	3.177	3.101	2.853	2.258	1.962	1.143

0.548387096774194	3.006	2.936	2.765	2.254	1.924	1.103

0.580645161290323	2.86	2.798	2.556	2.131	1.891	1.091

0.612903225806452	2.798	2.736	2.498	2.117	1.87	1.086

0.645161290322581	2.691	2.626	2.448	2.088	1.856	1.068

0.67741935483871	2.606	2.553	2.347	2.081	1.735	0.9988

0.709677419354839	2.488	2.43	2.265	1.843	1.672	0.9192

0.741935483870968	2.448	2.388	2.168	1.789	1.629	0.8389

0.774193548387097	2.383	2.325	2.113	1.768	1.61	0.8271

0.806451612903226	2.207	2.154	2.002	1.709	1.583	0.7947

0.838709677419355	2.107	2.059	1.972	1.69	1.527	0.7179

0.870967741935484	1.784	1.743	1.608	1.461	1.395	0.6875

0.903225806451613	1.735	1.693	1.581	1.209	1.08	0.652

0.935483870967742	1.567	1.529	1.383	1.205	1.076	0.6425

0.967741935483871	1.418	1.386	1.351	0.9949	0.9401	0.5011

0.1	5.5016	5.3637	4.9109	4.2692	3.7592	1.5344

Average of yearly averages:	1.14132333333333

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flusbi

Metfile:	w13893.dvf

PRZM scenario:	MSsoybeanC.txt

EXAMS environment file:	ir298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3500	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.0637	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.16	fraction of application rate applied to pond

Application Date	Date	01-09	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	IR

Flag for runoff calc.	RUNOFF	total	none, monthly or total(average of
entire run)

-------------------

PRZM environment: GAsoybeanC.txt	modified Friday, 14 October 2005 at
15:22:04

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w93805.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	1.988	1.976	1.848	1.306	1.154	0.3452

1962	4.844	4.809	4.679	4.534	4.527	2.515

1963	8.296	8.251	8.08	7.77	7.705	5.08

1964	12.83	12.78	12.57	12.3	12.09	8.488

1965	14.91	14.86	14.68	14.45	14.3	12.14

1966	19	18.92	18.73	18.38	18.13	14.57

1967	18.03	18	17.91	17.78	17.41	16.6

1968	20.61	20.57	20.39	20.29	20.19	17.88

1969	30.59	30.45	29.87	28.86	28.36	21.53

1970	26.96	26.93	26.83	26.63	26.49	25.33

1971	24.68	24.66	24.61	24.5	24.41	23.54

1972	24.29	24.25	24.12	23.54	23.16	22.36

1973	23.86	23.83	23.73	23.55	23.4	22.48

1974	23.71	23.67	23.46	23.18	23	21.81

1975	22.58	22.54	22.42	22.29	22.18	21.57

1976	25.06	24.99	24.77	24.43	24.11	21.62

1977	23.73	23.71	23.64	23.5	23.38	22.19

1978	21.3	21.3	21.26	21.19	21.12	20.15

1979	21.21	21.15	20.97	20.72	20.64	19.49

1980	20.36	20.35	20.29	20.17	20.08	19.36

1981	19.28	19.27	19.23	19.14	19.06	18.48

1982	18.71	18.67	18.52	18.38	18.3	17.79

1983	18.65	18.63	18.55	17.93	17.72	17.25

1984	18.48	18.46	18.38	18.24	18.14	17.35

1985	19.23	19.18	19.04	18.97	17.92	16.67

1986	18.82	18.8	18.74	18.47	18.36	17.86

1987	18.63	18.59	18.49	18.37	18.28	17.62

1988	18.46	18.44	18.37	18.16	18.18	17.55

1989	19.77	19.72	19.55	19.33	19.21	17.81

1990	18.87	18.85	18.79	18.65	18.54	17.84

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	30.59	30.45	29.87	28.86	28.36	25.33

0.0645161290322581	26.96	26.93	26.83	26.63	26.49	23.54

0.0967741935483871	25.06	24.99	24.77	24.5	24.41	22.48

0.129032258064516	24.68	24.66	24.61	24.43	24.11	22.36

0.161290322580645	24.29	24.25	24.12	23.55	23.4	22.19

0.193548387096774	23.86	23.83	23.73	23.54	23.38	21.81

0.225806451612903	23.73	23.71	23.64	23.5	23.16	21.62

0.258064516129032	23.71	23.67	23.46	23.18	23	21.57

0.290322580645161	22.58	22.54	22.42	22.29	22.18	21.53

0.32258064516129	21.3	21.3	21.26	21.19	21.12	20.15

0.354838709677419	21.21	21.15	20.97	20.72	20.64	19.49

0.387096774193548	20.61	20.57	20.39	20.29	20.19	19.36

0.419354838709677	20.36	20.35	20.29	20.17	20.08	18.48

0.451612903225806	19.77	19.72	19.55	19.33	19.21	17.88

0.483870967741936	19.28	19.27	19.23	19.14	19.06	17.86

0.516129032258065	19.23	19.18	19.04	18.97	18.54	17.84

0.548387096774194	19	18.92	18.79	18.65	18.36	17.81

0.580645161290323	18.87	18.85	18.74	18.47	18.3	17.79

0.612903225806452	18.82	18.8	18.73	18.38	18.28	17.62

0.645161290322581	18.71	18.67	18.55	18.38	18.18	17.55

0.67741935483871	18.65	18.63	18.52	18.37	18.14	17.35

0.709677419354839	18.63	18.59	18.49	18.24	18.13	17.25

0.741935483870968	18.48	18.46	18.38	18.16	17.92	16.67

0.774193548387097	18.46	18.44	18.37	17.93	17.72	16.6

0.806451612903226	18.03	18	17.91	17.78	17.41	14.57

0.838709677419355	14.91	14.86	14.68	14.45	14.3	12.14

0.870967741935484	12.83	12.78	12.57	12.3	12.09	8.488

0.903225806451613	8.296	8.251	8.08	7.77	7.705	5.08

0.935483870967742	4.844	4.809	4.679	4.534	4.527	2.515

0.967741935483871	1.988	1.976	1.848	1.306	1.154	0.3452

0.1	25.022	24.957	24.754	24.493	24.38	22.468

Average of yearly averages:	17.1756066666667

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flusbp

Metfile:	w93805.dvf

PRZM scenario:	GAsoybeanC.txt

EXAMS environment file:	pond298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3600	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.125	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	01-09	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

-------------------

PRZM environment: MIbeansC.txt	modified Monday, 10 May 2004 at 07:24:24

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w14826.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	2.433	2.413	2.345	2.293	2.26	0.8431

1962	2.56	2.555	2.543	2.521	2.508	2.203

1963	3.12	3.114	3.092	3.059	3.054	2.679

1964	3.671	3.664	3.637	3.594	3.586	3.201

1965	5.299	5.284	5.229	5.191	5.15	4.146

1966	5.322	5.315	5.3	5.281	5.262	5.05

1967	5.934	5.929	5.912	5.889	5.86	5.415

1968	9.309	9.279	9.155	8.937	8.825	6.898

1969	8.521	8.516	8.501	8.475	8.455	8.33

1970	9.345	9.334	9.298	9.247	9.231	8.572

1971	9.141	9.138	9.125	9.099	9.082	8.973

1972	9.711	9.703	9.679	9.641	9.63	9.169

1973	10.17	10.16	10.13	10.08	10.03	9.551

1974	10.1	10.09	10.07	10.04	10.02	9.888

1975	14.07	14.04	13.93	13.72	13.57	11.07

1976	13.13	13.12	13.07	13.01	12.98	12.75

1977	12.92	12.91	12.89	12.86	12.84	12.68

1978	12.95	12.94	12.89	12.8	12.76	12.52

1979	12.64	12.64	12.62	12.59	12.57	12.31

1980	12.63	12.61	12.57	12.49	12.45	12.1

1981	13.26	13.25	13.2	13.11	13.06	12.42

1982	12.99	12.98	12.96	12.92	12.92	12.73

1983	13.13	13.11	13.05	13.03	13	12.71

1984	12.87	12.86	12.85	12.82	12.79	12.64

1985	15.32	15.29	15.16	14.96	14.85	13.18

1986	16.95	16.92	16.84	16.67	16.58	14.94

1987	16.99	16.97	16.89	16.75	16.68	16.12

1988	16.61	16.59	16.54	16.48	16.46	16.22

1989	17.09	17.06	16.99	16.85	16.78	16.3

1990	16.58	16.57	16.54	16.51	16.48	16.31

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	17.09	17.06	16.99	16.85	16.78	16.31

0.0645161290322581	16.99	16.97	16.89	16.75	16.68	16.3

0.0967741935483871	16.95	16.92	16.84	16.67	16.58	16.22

0.129032258064516	16.61	16.59	16.54	16.51	16.48	16.12

0.161290322580645	16.58	16.57	16.54	16.48	16.46	14.94

0.193548387096774	15.32	15.29	15.16	14.96	14.85	13.18

0.225806451612903	14.07	14.04	13.93	13.72	13.57	12.75

0.258064516129032	13.26	13.25	13.2	13.11	13.06	12.73

0.290322580645161	13.13	13.12	13.07	13.03	13	12.71

0.32258064516129	13.13	13.11	13.05	13.01	12.98	12.68

0.354838709677419	12.99	12.98	12.96	12.92	12.92	12.64

0.387096774193548	12.95	12.94	12.89	12.86	12.84	12.52

0.419354838709677	12.92	12.91	12.89	12.82	12.79	12.42

0.451612903225806	12.87	12.86	12.85	12.8	12.76	12.31

0.483870967741936	12.64	12.64	12.62	12.59	12.57	12.1

0.516129032258065	12.63	12.61	12.57	12.49	12.45	11.07

0.548387096774194	10.17	10.16	10.13	10.08	10.03	9.888

0.580645161290323	10.1	10.09	10.07	10.04	10.02	9.551

0.612903225806452	9.711	9.703	9.679	9.641	9.63	9.169

0.645161290322581	9.345	9.334	9.298	9.247	9.231	8.973

0.67741935483871	9.309	9.279	9.155	9.099	9.082	8.572

0.709677419354839	9.141	9.138	9.125	8.937	8.825	8.33

0.741935483870968	8.521	8.516	8.501	8.475	8.455	6.898

0.774193548387097	5.934	5.929	5.912	5.889	5.86	5.415

0.806451612903226	5.322	5.315	5.3	5.281	5.262	5.05

0.838709677419355	5.299	5.284	5.229	5.191	5.15	4.146

0.870967741935484	3.671	3.664	3.637	3.594	3.586	3.201

0.903225806451613	3.12	3.114	3.092	3.059	3.054	2.679

0.935483870967742	2.56	2.555	2.543	2.521	2.508	2.203

0.967741935483871	2.433	2.413	2.345	2.293	2.26	0.8431

0.1	16.916	16.887	16.81	16.654	16.57	16.21

Average of yearly averages:	10.0639366666667

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flubmp

Metfile:	w14826.dvf

PRZM scenario:	MIbeansC.txt

EXAMS environment file:	pond298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3500	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.0637	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	27-07	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

---------------------------------

PRZM environment: MSsoybeanC.txt	modified Satday, 12 October 2002 at
17:07:44

EXAMS environment: pond298.exv	modified Thuday, 29 August 2002 at
16:33:30

Metfile: w13893.dvf	modified Wedday, 3 July 2002 at 09:06:20

Water segment concentrations (ppb)

Year	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

1961	1.613	1.604	1.58	1.384	1.029	0.2744

1962	2.16	2.15	2.123	2.107	2.102	1.586

1963	2.618	2.614	2.599	2.438	2.414	2.109

1964	3.516	3.511	3.485	3.318	3.212	2.72

1965	4.432	4.416	4.366	4.285	4.233	3.547

1966	4.754	4.742	4.702	4.64	4.633	4.2

1967	5.344	5.334	5.322	5.038	4.915	4.568

1968	6.962	6.94	6.855	6.771	6.742	5.498

1969	7.331	7.308	7.169	6.868	6.598	6.376

1970	7.484	7.471	7.449	7.384	7.31	7.004

1971	7.248	7.244	7.23	7.198	7.174	6.921

1972	8.42	8.404	8.363	8.282	8.202	7.169

1973	8.255	8.236	8.201	8.155	8.145	7.87

1974	8.071	8.066	8.048	8.01	7.978	7.694

1975	8.104	8.095	8.062	8.013	7.879	7.53

1976	9.156	9.137	9.092	8.996	8.858	7.986

1977	9.46	9.434	9.366	9.263	9.241	8.624

1978	9.761	9.746	9.694	9.24	9.038	8.771

1979	9.616	9.607	9.572	9.506	9.458	9.2

1980	9.729	9.718	9.685	9.64	9.596	9.187

1981	10.94	10.91	10.85	10.72	10.36	9.391

1982	10.6	10.58	10.55	10.47	10.45	10.11

1983	10.54	10.53	10.51	10.38	10.35	10.01

1984	10.42	10.42	10.39	10.33	10.29	9.907

1985	9.84	9.837	9.824	9.794	9.762	9.409

1986	11.3	11.29	11.2	10.96	10.29	9.268

1987	11.48	11.46	11.42	11.15	10.7	10.31

1988	11.26	11.25	11.21	11.14	11.09	10.68

1989	11.49	11.47	11.41	11.37	11.33	10.64

1990	11.51	11.49	11.42	11.32	11.28	10.88

Sorted results

Prob.	Peak	96 hr	21 Day	60 Day	90 Day	Yearly

0.032258064516129	11.51	11.49	11.42	11.37	11.33	10.88

0.0645161290322581	11.49	11.47	11.42	11.32	11.28	10.68

0.0967741935483871	11.48	11.46	11.41	11.15	11.09	10.64

0.129032258064516	11.3	11.29	11.21	11.14	10.7	10.31

0.161290322580645	11.26	11.25	11.2	10.96	10.45	10.11

0.193548387096774	10.94	10.91	10.85	10.72	10.36	10.01

0.225806451612903	10.6	10.58	10.55	10.47	10.35	9.907

0.258064516129032	10.54	10.53	10.51	10.38	10.29	9.409

0.290322580645161	10.42	10.42	10.39	10.33	10.29	9.391

0.32258064516129	9.84	9.837	9.824	9.794	9.762	9.268

0.354838709677419	9.761	9.746	9.694	9.64	9.596	9.2

0.387096774193548	9.729	9.718	9.685	9.506	9.458	9.187

0.419354838709677	9.616	9.607	9.572	9.263	9.241	8.771

0.451612903225806	9.46	9.434	9.366	9.24	9.038	8.624

0.483870967741936	9.156	9.137	9.092	8.996	8.858	7.986

0.516129032258065	8.42	8.404	8.363	8.282	8.202	7.87

0.548387096774194	8.255	8.236	8.201	8.155	8.145	7.694

0.580645161290323	8.104	8.095	8.062	8.013	7.978	7.53

0.612903225806452	8.071	8.066	8.048	8.01	7.879	7.169

0.645161290322581	7.484	7.471	7.449	7.384	7.31	7.004

0.67741935483871	7.331	7.308	7.23	7.198	7.174	6.921

0.709677419354839	7.248	7.244	7.169	6.868	6.742	6.376

0.741935483870968	6.962	6.94	6.855	6.771	6.598	5.498

0.774193548387097	5.344	5.334	5.322	5.038	4.915	4.568

0.806451612903226	4.754	4.742	4.702	4.64	4.633	4.2

0.838709677419355	4.432	4.416	4.366	4.285	4.233	3.547

0.870967741935484	3.516	3.511	3.485	3.318	3.212	2.72

0.903225806451613	2.618	2.614	2.599	2.438	2.414	2.109

0.935483870967742	2.16	2.15	2.123	2.107	2.102	1.586

0.967741935483871	1.613	1.604	1.58	1.384	1.029	0.2744

0.1	11.462	11.443	11.39	11.149	11.051	10.607

Average of yearly averages:	7.31464666666667

Inputs generated by pe4.pl - 8-August-2003

Data used for this run:

Output File: flusbr

Metfile:	w13893.dvf

PRZM scenario:	MSsoybeanC.txt

EXAMS environment file:	pond298.exv

Chemical Name:	flutriafol

Description	Variable Name	Value	Units	Comments

Molecular weight	mwt	301	g/mol

Henry's Law Const.	henry	1.3E-11	atm-m^3/mol

Vapor Pressure	vapr	3E-09	torr

Solubility	sol	95	mg/L

Kd	Kd		mg/L

Koc	Koc	255	mg/L

Photolysis half-life	kdp	0	days	Half-life

Aerobic Aquatic Metabolism	kbacw	1000	days	Halfife

Anaerobic Aquatic Metabolism	kbacs	3500	days	Halfife

Aerobic Soil Metabolism	asm	1747	days	Halfife

Hydrolysis:	pH 7	0	days	Half-life

Method:	CAM	2	integer	See PRZM manual

Incorporation Depth:	DEPI	0	cm

Application Rate:	TAPP	0.0637	kg/ha

Application Efficiency:	APPEFF	0.95	fraction

Spray Drift	DRFT	0.05	fraction of application rate applied to pond

Application Date	Date	01-09	dd/mm or dd/mmm or dd-mm or dd-mmm

Interval 1	interval	14	days	Set to 0 or delete line for single app.

Record 17:	FILTRA	

IPSCND	

UPTKF	

Record 18:	PLVKRT	

PLDKRT	

FEXTRC	0.5

Flag for Index Res. Run	IR	Pond

Flag for runoff calc.	RUNOFF	none	none, monthly or total(average of
entire run)

Appendix B.  SCI-GROW Print-out

	SCIGROW -  VERSION 2.3

	ENVIRONMENTAL FATE AND EFFECTS DIVISION

	OFFICE OF PESTICIDE PROGRAMS

U.S. ENVIRONMENTAL PROTECTION AGENCY

	SCREENING MODEL FOR AQUATIC PESTICIDE EXPOSURE

 

 SciGrow version 2.3

 chemical:flutriafol

 time is 11/25/2005  13:39:43

 -----------------------------------------------------------------------
----------------------------------------------------------------

  Application	Number of	Total Use	 Koc	    Soil Aerobic

  rate (lb/acre)	applications	(lb/acre/yr)	(ml/g)	 metabolism (days)

 -----------------------------------------------------------------------
------------------------------------------------------------

      0.057	      2.0	   0.114	2.95E+02	      1747.0

 -----------------------------------------------------------------------
-------------------------------

 groundwater screening cond (ppb) =   5.83E-01 

 ***********************************************************************
*

 

Appendix C.  Identity of Endangered Avian and Mammalian Species Located
in Soybean Producing Counties.  

Species Details by State for Preliminary Assessment

 ADVANCE \d1 	Soybeans (176)

 ADVANCE \d1 	Minimum of 1 Acre.

 ADVANCE \d19 	Alabama	(8 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	MOUSE, ALABAMA BEACH	Mammal	Yes

 ADVANCE \d4 	MOUSE, PERDIDO KEY BEACH	Mammal	Yes

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	STORK, WOOD	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Arkansas	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Delaware	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	SQUIRREL, DELMARVA PENINSULA FOX	Mammal	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d11 	Florida	(12 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d18 Thursday, July 28, 2005	Page 1 of 9

 ADVANCE \d2 	JAY, FLORIDA SCRUB	Bird	No

 ADVANCE \d4 	KITE, EVERGLADE SNAIL	Bird	Yes

 ADVANCE \d4 	MANATEE, WEST INDIAN (FLORIDA)	Mammal	Yes

 ADVANCE \d4 	MOUSE, CHOCTAWHATCHEE BEACH	Mammal	Yes

 ADVANCE \d4 	MOUSE, PERDIDO KEY BEACH	Mammal	Yes

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	STORK, WOOD	Bird	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Georgia	(8 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	MANATEE, WEST INDIAN (FLORIDA)	Mammal	Yes

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	STORK, WOOD	Bird	No

 ADVANCE \d4 	WARBLER (WOOD), KIRTLAND'S	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Illinois	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Indiana	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d13 Thursday, July 28, 2005	Page 2 of 9

 ADVANCE \d9 	Iowa	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Kansas	(7 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	FERRET, BLACK-FOOTED	Mammal	No

 ADVANCE \d4 	PLOVER, MOUNTAIN	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Kentucky	(6 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	BAT, VIRGINIA BIG-EARED	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Louisiana	(8 species)

Group	Critical Habitat

 ADVANCE \d3 	BEAR, AMERICAN BLACK	Mammal	No

 ADVANCE \d4 	BEAR, LOUISIANA BLACK	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PELICAN, BROWN	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, CALIFORNIA LEAST	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d13 Thursday, July 28, 2005	Page 3 of 9

 ADVANCE \d2 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Maine	(3 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	LYNX, CANADA	Mammal	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d11 	Maryland	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	SQUIRREL, DELMARVA PENINSULA FOX	Mammal	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d11 	Massachusetts	(2 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d11 	Michigan	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	WARBLER (WOOD), KIRTLAND'S	Bird	No

 ADVANCE \d4 	WOLF, GRAY	Mammal	Yes

 ADVANCE \d11 	Minnesota	(3 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	WOLF, GRAY	Mammal	Yes

 ADVANCE \d11 	Mississippi	(6 species)

Group	Critical Habitat

 ADVANCE \d3 	BEAR, LOUISIANA BLACK	Mammal	Yes

 ADVANCE \d12 Thursday, July 28, 2005	Page 4 of 9

 ADVANCE \d2 	CRANE, MISSISSIPPI SANDHILL	Bird	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PELICAN, BROWN	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Missouri	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Nebraska	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	FERRET, BLACK-FOOTED	Mammal	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	New Jersey	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d11 	New York	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d32 Thursday, July 28, 2005	Page 5 of 9

 ADVANCE \d9 	North Carolina	(11 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	CAHOW	Bird	No

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	MANATEE, WEST INDIAN (FLORIDA)	Mammal	Yes

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	SQUIRREL, CAROLINA NORTHERN FLYING	Mammal	No

 ADVANCE \d4 	STORK, WOOD	Bird	No

 ADVANCE \d4 	TERN, ROSEATE	Bird	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d4 	WOLF, RED	Mammal	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	North Dakota	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Ohio	(3 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d11 	Oklahoma	(10 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	BAT, OZARK BIG-EARED	Mammal	No

 ADVANCE \d4 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	CURLEW, ESKIMO	Bird	No

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d13 Thursday, July 28, 2005	Page 6 of 9

 ADVANCE \d2 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	VIREO, BLACK-CAPPED	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Pennsylvania	(4 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	SQUIRREL, DELMARVA PENINSULA FOX	Mammal	No

 ADVANCE \d11 	South Carolina	(7 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	MANATEE, WEST INDIAN (FLORIDA)	Mammal	Yes

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	STORK, WOOD	Bird	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d4 	WOLF, RED	Mammal	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	South Dakota	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	FERRET, BLACK-FOOTED	Mammal	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d11 	Tennessee	(7 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	SQUIRREL, CAROLINA NORTHERN FLYING	Mammal	No

 ADVANCE \d13 Thursday, July 28, 2005	Page 7 of 9

 ADVANCE \d2 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	WOLF, RED	Mammal	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Texas	(15 species)

Group	Critical Habitat

 ADVANCE \d3 	BEAR, LOUISIANA BLACK	Mammal	Yes

 ADVANCE \d4 	CRANE, WHOOPING	Bird	Yes

 ADVANCE \d4 	CURLEW, ESKIMO	Bird	No

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	FALCON, NORTHERN APLOMADO	Bird	No

 ADVANCE \d4 	JAGUARUNDI, Gulf Coast	Mammal	No

 ADVANCE \d4 	OCELOT	Mammal	No

 ADVANCE \d4 	PELICAN, BROWN	Bird	No

 ADVANCE \d4 	PLOVER, MOUNTAIN	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	PRAIRIE-CHICKEN, ATTWATER'S GREATER	Bird	No

 ADVANCE \d4 	TERN, INTERIOR (POPULATION) LEAST	Bird	No

 ADVANCE \d4 	VIREO, BLACK-CAPPED	Bird	No

 ADVANCE \d4 	WARBLER (WOOD), GOLDEN-CHEEKED	Bird	No

 ADVANCE \d4 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	Vermont	(2 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d11 	Virginia	(7 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	BAT, VIRGINIA BIG-EARED	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	PLOVER, PIPING	Bird	Yes

 ADVANCE \d4 	SQUIRREL, DELMARVA PENINSULA FOX	Mammal	No

 ADVANCE \d4 	WHALE, NORTHERN RIGHT	Mammal	Yes

 ADVANCE \d13 Thursday, July 28, 2005	Page 8 of 9

 ADVANCE \d2 	WOODPECKER, RED-COCKADED	Bird	No

 ADVANCE \d11 	West virginia	(5 species)

Group	Critical Habitat

 ADVANCE \d3 	BAT, GRAY	Mammal	No

 ADVANCE \d4 	BAT, INDIANA	Mammal	Yes

 ADVANCE \d4 	BAT, VIRGINIA BIG-EARED	Mammal	Yes

 ADVANCE \d4 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	SQUIRREL, VIRGINIA NORTHERN FLYING	Mammal	No

 ADVANCE \d11 	Wisconsin	(3 species)

Group	Critical Habitat

 ADVANCE \d3 	EAGLE, BALD	Bird	No

 ADVANCE \d4 	WARBLER (WOOD), KIRTLAND'S	Bird	No

 ADVANCE \d4 	WOLF, GRAY	Mammal	Yes

 ADVANCE \d380 Thursday, July 28, 2005	Page 9 of 9

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