Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

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UNITED STATES ENVIRONMENTAL PROTECTION AGENCY 

WASHINGTON, D.C. 20460 

 OFFICE OF CHEMICAL SAFETY AND 

 POLLUTION PREVENTION

MEMORANDUM

DATE: 28-March-2011 

SUBJECT: Metconazole: Acute and Chronic Dietary (Food and Drinking Water) Exposure 

and Risk Assessment for Residues in/on Vegetables, Tuberous & Corm, Subgroup 

1C and Bushberry Subgroup 13-07B. 

FROM: Amelia M. Acierto 

 Risk Assessment Branch III (RAB3) 

Health Effects Division (HED) (7509P) 

THROUGH: David Soderberg, Chemist 

 Breann Hansen, Biologist 

Dietary Exposure Science Advisory Council (DESAC) 

HED (7509P) 

and 

Stephen Funk, Senior Science Advisor 

Risk Assessment Branch III (RAB3) 

Health Effects Division (HED) (7509P) 

 

TO: Barry O’Keefe, Risk Assessor 

Risk Assessment Branch III (RAB3) 

Health Effects Division (HED) (7509P) 

 

and 

 Barbara Madden, RM 05 

Risk Integration, Minor Use, & Emergency Response Branch 

Registration Division (RD; 7505P) 

PC Code: 125619 DP Num: D387504 

Decision No.: 436782 Registration Nos.: 59639-147 

Petition No.: 0E7743 Regulatory Action: Section 3 

Risk Assessment Type: Dietary Exposure Case No.: NA 

TXR No.: NA CAS No.: 125116-23-6 

MRID No.: NA 40 CFR: §180.617 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

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Executive Summary 

Acute and chronic dietary aggregate dietary (food and drinking water) exposure and risk 

assessments were conducted using the Dietary Exposure Evaluation Model (DEEM-FCIDTM, 

Version 2.03), which uses food consumption data from the USDA’s Continuing Surveys of Food 

Intakes by Individuals (CSFII) from 1994-1996 and 1998. The analyses were performed to 

support the proposed FIFRA sec. 3 amended registration of the fungicide metconazole (5-[(4-

chlorophenyl)methyl]-2,2-dimethyl-1-(1H-1,2,4-triazol-1-ylmethyl) cyclopentanol]), on 

vegetables, tuberous and corm subgroup 1C and bushberry subgroup 13-7B. 

Conservative acute and chronic dietary exposure assessments were conducted for all existing and 

proposed food uses of metconazole and drinking water. Residues of the proposed food 

commodities were based on field trial data on the representative crops (potato and blueberry). 

The conservative assessment assumed that metconazole residues are present in all registered and 

proposed food commodities at tolerance levels and that 100% of the crops were treated. All 

processing factors for the proposed tuberous/corm commodities were set to 1, based on the 

results of processing studies demonstrating that residues of metconazole in potato processed 

commodities would not exceed the raw agricultural commodity (RAC) tolerance. 

Estimated drinking water concentrations (EDWCs) were provided by EFED (DP# 375778 and 

380513, Khan, Faruque, Khan, et al, 16-Dec.-2010) and incorporated directly into the DEEM 

analyses. Both the acute and chronic analyses were conducted using estimated surface water 

residues generated using the PRZM/EXAMS models. Both the acute and chronic analyses were 

conducted using estimated surface water residues generated using the PRZM/EXAMS models. 

For the acute assessment, the 1-in-10 year annual peak concentration of 45.48 μg/Lwas used; for 

the chronic assessment, the 1-in-10 year annual mean concentration (non-cancer chronic) of 

38.16 μg/L was used. Ground water sources were not included, as the EDWCs for this water 

source are minimal in comparison to those for surface water. 

Acute Dietary (Food and Drinking Water) Exposure Results and Characterization 

The acute dietary exposure assessment was performed for female 13-49 years old only since an 

acute endpoint was not identified for the General U.S. population. Estimated acute dietary 

exposure to metconazole from food and drinking water is below HED’s level of concern. 

Combined dietary exposure from food and drinking water at the 95th percentile of exposure is 

estimated to be 0.004578 mg/kg/day for females13-49 years old, equivalent to 3.8% of the acute 

Population Adjusted Dose (aPAD); therefore, is not of concern to HED (i.e., <100% aPAD) 

Chronic Dietary (Food and Drinking Water) Exposure Results and Characterization 

Chronic dietary exposure estimates for food and drinking water combined are well below HED’s 

level of concern. Using EDWCs from the cranberry crop scenario, combined chronic dietary 

exposure is estimated at 0.002434 mg/kg/day for the general U.S. population (6.1% of the 

chronic Population Adjusted Dose (cPAD)) and 0.005026 mg/kg/day (12.6% of the cPAD) for 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

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children 1-2 years old, the population subgroup with the highest estimated chronic dietary 

exposure to metconazole. 

Cancer Exposure Results and Characterization 

Metconazole was classified as “Not likely to be carcinogenic to humans;” therefore, a cancer 

dietary assessment was not performed. 

I. Introduction

Dietary risk assessment incorporates both exposure and toxicity of a given pesticide. For acute 

and chronic assessments, the risk is expressed as a percentage of a maximum acceptable dose 

(i.e., the dose which HED has concluded will result in no unreasonable adverse health effects). 

This dose is referred to as the population adjusted dose (PAD). The PAD is equivalent to point 

of departure (POD, NOAEL, LOAEL, e.g.) divided by the required uncertainty or safety factors. 

For acute and non-cancer chronic exposures, HED is concerned when estimated dietary risk 

exceeds 100% of the PAD. HED is generally concerned when estimated cancer risk exceeds one 

in one million. References which discuss the acute and chronic risk assessments in more detail 

are available on the EPA/pesticides web site: “Available Information on Assessing Exposure 

from Pesticides, A User’s Guide,” 6/21/2000, web link: http://www.epa.gov/fedrgstr/EPAPEST/2000/July/Day-12/6061.pdf; or see SOP 99.6 (8/20/99). 

The most recent dietary risk assessment for metconazole was conducted on 21-September-2008 

(Memo, N. Dodd; DP# 350663). 

 

II. Residue Information 

Residues of Concern: The residues of concern for the tolerance expression and risk assessment 

for primary and rotational crops, except cereal grains is metconazole, residues of concern for the 

risk assessment for the risk assessment for cereal grain is metconazole and M11; residues of 

concern for the tolerance expression for livestock commodities is metconazole parent, residues 

of concern for the risk assessment for livestock commodities are metconazole and its metabolites 

M1 and its glucuronic conjugate; M12; M31 and its glucuronic acid conjugate. (Memo, C. 

Olinger; DP# 348234, 11-February-2008). 

Established Tolerances: Tolerances for residues of metconazole are established under 40 CFR 

§180.617 and are expressed in terms of the fungicide metconazole or in terms of the fungicide 

metconazole, including its metabolites and degradates determined by measuring only 

metconazole as the sum of its cis- and trans- isomers [40 CFR §180.617(a)(1) and (2). 

Permanent tolerances have been established for a variety of raw agricultural and processed 

commodities including tree nuts, banana, barley, sugar beet, stone fruits, cereal grains, peanuts, 

soybean, canola, corn, and cotton commodities at tolerance levels ranging from 0.01-18 ppm. 

Tolerances for meat byproducts of cattle, goat, horse, and sheep, and egg are established at 0.04 

ppm. Time-limited tolerances have also been established on sugarcane cane and molasses at 1.6 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

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and 3.2 ppm, respectively, in connection with FIFRA § 18 emergency exemptions (49 CFR 

§180.617(b)) which is set to expire on 12/31/2011. 

Recommended Tolerances: 

Valent , USA Corporation and IR-4 have proposed new tolerances for metconazole on tuberous 

and corm vegetables subgroup 1C and bushberry subgroup 13-07B. The proposed tolerances are 

summarized below together with HED’s recommendations based on review of field trial data (A. 

Acierto DP# 380990, 3/24/2011). The recommended tolerance of 0.40 ppm for bushberry is 

based on the Agency’s tolerance spreadsheet as specified by the Guidance for Setting Pesticide 

Tolerances. The tolerance spreadsheet was not used to calculate the tolerance for the tuberous 

and corm vegetables since the residues in potato (representative crop used) were <LOQ. HED 

recommended the tolerance of 0.04 ppm, reflecting the combined LOQs of the residues of 

metconazole isomers (cis- and trans-isomers). 

 

Table 1. Tolerance Summary for Metconazole. 

Commodity 

Proposed 

Tolerance (ppm) 

Recommended 

Tolerance (ppm) 

Comments; Correct Commodity 

Definition

Vegetable, tuberous and 

corm, subgroup 1C 

0.02 0.04 Vegetable, tuberous and corm, 

subgroup 1C 

Bushberry subgroup 13-

07B 

0.35 0.40 

Processed Commodities 

There are no processed commodities associated with bushberry (OPPTS 860.1000, Table 1). 

Potato processed commodities are potato flakes/granules, potato chips and potato wet peels. 

Processing studies were submitted from potato tubers treated at exaggerated rate of 5x the 

recommended seasonal rate. Based on the very low (<LOQ of 0.02 ppm) metconazole residues 

from the RAC samples, residues are not expected to occur in the processed commodities. 

Therefore, the DEEM default processing factors were not used. 

III. Drinking Water Data 

Reference: DP# 375778 and 380513, Khan, Faruque, Khan, et al, 16-Dec.-2010. 

 

The values used in the dietary risk assessment were provided by the Environmental Fate and 

Effects Division (EFED) in the following memo: Drinking Water Exposure Assessment to 

Establish Tolerances of Parent Metconazole for Tuberous/Corm (Subgroup 1C) and Bushberry 

(Subgroup 13-07BC) (DP# 375778 and 380513, Khan, Faruque, Khan, et al, 16-Dec.-2010). A 

Tier II drinking water assessment for the proposed use on the tuberous/corm vegetables and 

bushberry were performed using PRZM/EXAMS modeling. Estimated concentrations of 

metconazole in drinking water from use on the new crops were provided by EFED and 

incorporated directly into the acute and chronic assessments. 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

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Water residues were incorporated in the DEEM-FCIDTM in the food categories “water, direct, 

all sources” and “water, indirect, all sources.” 

The EDWCs are based on the maximum proposed rates specified on the label. For surface 

water, the EDWCs for the crops modeled in the assessment did not exceed the acute EDWC of 

45.48 ug/L for turf reported in the previous drinking water assessment (D340378, 2007). 

However, annual mean (chronic) concentration of 38.16 ug/L for cranberry scenario is higher 

than the previously reported EDWCs (31.25 ug/L). Since the EDWC for the crops modeled in 

the current assessment is lower than the acute EDWC for turf reported in the previous drinking 

water assessment, EFED recommended the use of the previous EDWC as follows: 

 45.48 μ/L for the 1 to 10 year annual peak concentration.(acute) 

 38.16 μ/L for the annual mean concentration (non-cancer chronic). \\\ 

The Environmental Fate and Effects Division (EFED) calculated screening level surface water 

and ground water estimates for metconazole using linked PRZM/EXAMS models and the SCIGROW model, respectively. The drinking water models and their descriptions are available at 

the EPA internet site: http://www.epa.gov/oppefed1/models/water/. 

IV. DEEM-FCIDTM Program and Consumption Information

Metconazole acute and chronic dietary exposure assessments were conducted using DEEMFCIDTM, Version 2.03, which incorporates consumption data from USDA’s CSFII, 1994-1996 

and 1998. The 1994-96 and 1998 data are based on the reported consumption of more than 

20,000 individuals over two non-consecutive survey days. Foods “as consumed” (e.g., apple pie) 

are linked to EPA-defined food commodities (e.g. apples, peeled fruit - cooked; fresh or N/S; 

baked; or wheat flour - cooked; fresh or N/S, baked) using publicly available recipe translation 

files developed jointly by USDA/ARS and EPA. For chronic exposure assessment, consumption 

data are averaged for the entire U.S. population and within population subgroups, but for acute 

exposure assessment are retained as individual consumption events. Based on analysis of the 

1994-96 and 1998 CSFII consumption data, which took into account dietary patterns and survey 

respondents, HED concluded that it is most appropriate to report risk for the following 

population subgroups: the general U.S. population, all infants (<1 year old), children 1-2, 

children 3-5, children 6-12, youth 13-19, adults 20-49, females 13-49, and adults 50+ years old. 

For chronic dietary exposure assessment, an estimate of the residue level in each food or foodform (e.g., orange or orange juice) on the food commodity residue list is multiplied by the 

average daily consumption estimate for that food/food form to produce a residue intake estimate. 

The resulting residue intake estimate for each food/food form is summed with the residue intake 

estimates for all other food/food forms on the commodity residue list to arrive at the total 

average estimated exposure. Exposure is expressed in mg/kg body weight/day and as a percent 

of the cPAD. This procedure is performed for each population subgroup. 

For acute exposure assessments, individual one-day food consumption data are used on an 

individual-by-individual basis. The reported consumption amounts of each food item can be 

multiplied by a residue point estimate and summed to obtain a total daily pesticide exposure for a 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

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deterministic exposure assessment, or “matched” in multiple random pairings with residue values 

and then summed in a probabilistic assessment. The resulting distribution of exposures is 

expressed as a percentage of the aPAD on both a user (i.e., only those who reported eating 

relevant commodities/food forms) and a per-capita (i.e., those who reported eating the relevant 

commodities as well as those who did not) basis. In accordance with HED policy, per capita 

exposure and risk are reported for all tiers of analysis. However, for Tiers 1 and 2, any 

significant differences in user vs. per capita exposure and risk are specifically identified and 

noted in the risk assessment. 

V. Toxicological Information 

Toxicity data for metconazole have been previously reviewed. The CARC for metconazole met 

on November 2, 2005 (memo, Gregory Akerman, Ph.D., TXR# 0054211, 4/14/06). The 

Metconazole Endpoint Selection meeting was held on December 21, 2005. The Toxicity 

Advisory Clinic (TAC) met on 1/10/06 to discuss the acute hazard endpoint selection and the 

FQPA selection. 

The doses and toxicological endpoints selected for dietary risk assessment are summarized in 

Table 2. 

Table 2. Summary of Toxicological Doses and Endpoints for Metconazole

for Use in Dietary Exposure Assessment

Exposure 

Scenario 

Dose Used in Risk 

Assessment, UF 

Hazard and Exposure 

Based Special FQPA 

Safety Factor

Study and Toxicological 

Effects 

Acute Dietary 

(General U.S. 

population) 

An appropriate dose/endpoint attributable to a single dose was not observed in the 

available oral toxicity studies reviewed. 

Acute Dietary 

(Females 13-49) 

NOAEL = 12 mg/kg/day 

UF = 100 

Acute RfD = 0.12 

mg/kg/day 

FQPA SF = 1X

aPAD = 0.12 

mg/kg/day 

Prenatal developmental study 

in rodents: LOAEL = 30

mg/kg/day based on increased 

incidence of skeletal variations 

(predominantly lumbar ribs). 

Chronic Dietary 

(All populations)

NOAEL= 4.3 mg/kg/day 

UF = 100 

Chronic RfD = 0.04 

mg/kg/day 

FQPA SF = 1X 

cPAD = 0.04 

mg/kg/day 

Chronic oral toxicity study in 

rats: LOAEL = 13.1 mg/kg/day 

based on increased liver (M) 

weights and associated 

hepatocellular lipid vacuolation 

(M) and centrilobular 

hypertrophy(M). Same effects 

seen in F at 54 mg/kg/d, plus 

increased spleen wt. 

Cancer 

Classification: “Not Likely to be Carcinogenic to Humans” based on convincing 

evidence that carcinogenic effects are not likely below a defined dose range. A nongenotoxic mode of action for mouse liver tumors was established. No quantification is 

required. 
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Point of Departure (POD) = A data point or an estimated point that is derived from observed dose-response data and used to 

mark the beginning of extrapolation to determine risk associated with lower environmentally relevant human exposures. 

NOAEL = no observed adverse effect level. LOAEL = lowest observed adverse effect level. UF = uncertainty factor. UFA

= extrapolation from animal to human (interspecies). UFH = potential variation in sensitivity among members of the human 

population (intraspecies). UFL = use of a LOAEL to extrapolate a NOAEL. UFS = use of a short-term study for long-term 

risk assessment. UFDB = to account for the absence of key date (i.e., lack of a critical study). FQPA SF = FQPA Safety 

Factor. PAD = population adjusted dose (a = acute, c = chronic). RfD = reference dose. MOE = margin of exposure. LOC 

= level of concern. N/A = not applicable. 

VI. Results/Discussion 

As stated above, for acute and chronic assessments, HED is concerned when dietary risk exceeds 

100% of the PAD. The DEEM-FCIDTM analyses estimate the dietary exposure of the U.S. 

population and various population subgroups. The acute results reported in Table 3 are for 

females 13- 49 years old. The acute and chronic results reported in Table 4 are for the general 

U.S. population, all infants (<1 year old), children 1-2, children 3-5, children 6-12, youth 13-19, 

females 13-49, adults 20-49, and adults 50+ years. 

Results of Acute Dietary (Food and Drinking Water) Exposure Analysis

The acute dietary (food and drinking water) exposure assessment was performed for female 13-

49 years old only since an acute endpoint was not identified for the General U.S. population. 

Based on the assumptions described above, acute dietary exposure of females 13-49 years old is 

well below HED’s level of concern. Combined dietary exposure from food and drinking water at 

the 95th percentile of exposure is estimated to be 0.004578 mg/kg/day for females13-49 years 

old, equivalent to 3.8% of the acute Population Adjusted Dose (aPAD); therefore, is not of 

concern to HED (i.e., <100% aPAD) 

Table 3. Results of Acute Dietary Exposure Analysis for Food and Drinking Water Using 

DEEM FCID

Population 

Subgroup

aPAD 

(mg/kg/day)

95th Percentile 99th Percentile 99.9th Percentile

Exposure 

(mg/kg/day)

% 

aPAD

Exposure 

(mg/kg/day)

% 

aPAD

Exposure 

(mg/kg/day)

% 

aPAD

Females 13-49 

years old 0.12 0.004578 3.8 0.007490 6.24 9.014659 12.22 

Results of Chronic Dietary (Food and Drinking Water) Exposure Analysis

The chronic dietary risk assessment shows that for all included commodities, the chronic dietary 

risk estimates are not of concern to HED [i.e., <100% chronic population-adjusted dose (cPAD)]. 

For the general U.S. population the exposure for food and water utilized 6% of the cPAD. The 

chronic dietary risk estimate for the highest reported exposed population subgroup, children 1-2 

years old, is 12.6% of the cPAD. 
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Table 4. Summary of Dietary (Food and Drinking Water) Exposure Risk for Metconazolet1. 

Population Subgroup 

Acute Dietary 

(95th Percentile) Chronic Dietary 

Dietary Exposure 

(mg/kg/day) % aPAD Dietary Exposure 

(mg/kg/day) % cPAD 

General U.S. Population 0.002434 6 

All Infants (<1 year old) 0.004831 12.1 

Children 1-2 years old 0.005026 12.6 

Children 3-5 years old 0..004800 12 

Children 6-12 years old 0.003289 8.2 

Youth 13-19 years old 0.001961 4.9 

Adults 20-49 years old 0.002158 5.4 

Adults 50+ years old 0.001868 4.7 

Females 13-49 years old 0.004578 3.8 0.001874 4.7 

1 The values for the highest exposed population for each type of risk assessment are bolded. 

These analyses are considered to be very conservative dietary exposure assessments. Residues in 

foods were assumed to be equivalent to the tolerance levels. Tolerance-level residues should 

always exceed the residue levels found on food commodities at the time of consumption. When 

field trials are performed, the maximum allowable application rate is used and crops are 

harvested at the minimum PHI. Samples are stored frozen until analysis to ensure minimal 

degradation of residues. In actual practice, however, growers will not usually use the maximum 

application rates for economic reasons. In addition, most crops are not harvested and 

immediately stored frozen. Also, 100% CT was assumed and DEEMTM 7.81 default processing 

factors were used (where provided). For these reasons, HED is confident that this analysis does 

not underestimate risk to the general U.S. population or any population subgroup. Further 

refinement to the analyses could be made through the use of anticipated residues, empirical 

processing factors, and incorporation of percentages of crops treated with metconazole. Since 

risk estimates are not of concern to HED, a more highly refined analysis is not needed at this 

time. 

VII. Characterization of Inputs/Outputs

The acute and chronic dietary exposure and risk estimates are conservative since they assume 

that 100% of crops are treated with metconazole and that the residues are present at tolerance 

levels. In addition, drinking water exposure estimates were based on screening level estimates 

generated by the PRIZM-EXAMS model. Although not needed at this time, HED could refine 

the exposure and risk estimates through the use of anticipated residues and percent crop treated 

data as well as refined estimated drinking water concentrations. However, since estimated 

exposures and risks using conservative assumptions are well below HED’s level of concern, such 

refinement is not warranted. 
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VIII. Conclusions

These unrefined dietary exposure analyses using DEEM-FCIDTM indicate that acute and chronic 

dietary exposure to metconazole from food and drinking water are well below HED’s level of 

concern for this pesticide. The estimated acute exposure of females 13-49 years old, the only 

population subgroup of concern for acute exposure, represents 3.8% of the aPAD at the 95th

percentile of exposure. The chronic dietary (food + drinking water) exposure to metconazole is 

below HED’s level of concern for the general U.S. population and all population subgroups. The 

chronic dietary exposure utilized 6% cPAD for the general U.S. population and <13% of the 

cPAD for children 1-2 years old, the most highly exposed population subgroup. 

IX. List of Attachments

Attachment 1: Acute Food plus Water Residue Input File 

Attachment 2: Acute Food plus Water Results File 

Attachment 3: Chronic Food plus Water Residue Input File 

Attachment 4: Chronic Food plus Water Residue Results File 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

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Attachment 1: Acute Food plus Water Residue Input File 

U.S. Environmental Protection Agency Ver. 2.02 

DEEM-FCID Acute analysis for METCONAZOLE 

Residue file name: C:\Documents and Settings\aacierto\Desktop\DEEM-FCID 

Files\2011\MetconazoleTuberousCormBushberry Accute.R98 

Analysis Date 04-05-2011 Residue file dated: 04-05-2011/13:12:04/8 

Reference dose: aRfD = 0.12 mg/kg bw/day NOEL = 12 mg/kg bw/day 

Comment:Vegetables,Tuberous & Corm,Subgroup 1C and Bushberry Subgroup 13-07B 

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

 EPA Crop Def Res Adj.Factors Comment 

 Code Grp Food Name (ppm) #1 #2 

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

14000030 14 Almond 0.040000 1.000 1.000 

14000031 14 Almond-babyfood 0.040000 1.000 1.000 

14000040 14 Almond, oil 0.040000 1.000 1.000 

14000041 14 Almond, oil-babyfood 0.040000 1.000 1.000 

12000120 12 Apricot 0.200000 1.000 1.000 

12000121 12 Apricot-babyfood 0.200000 1.000 1.000 

12000130 12 Apricot, dried 0.200000 6.000 1.000 

12000140 12 Apricot, juice 0.200000 1.000 1.000 

12000141 12 Apricot, juice-babyfood 0.200000 1.000 1.000 

01030150 1CD Arrowroot, flour 0.040000 1.000 1.000 

01030151 1CD Arrowroot, flour-babyfood 0.040000 1.000 1.000 

01030170 1CD Artichoke, Jerusalem 0.040000 1.000 1.000 

95000230 O Banana 0.100000 1.000 1.000 

95000231 O Banana-babyfood 0.100000 1.000 1.000 

95000240 O Banana, dried 0.100000 3.900 1.000 

95000241 O Banana, dried-babyfood 0.100000 3.900 1.000 

15000250 15 Barley, pearled barley 2.830000 1.000 1.000 

15000251 15 Barley, pearled barley-babyfood 2.830000 1.000 1.000 

15000260 15 Barley, flour 2.830000 1.000 1.000 

15000261 15 Barley, flour-babyfood 2.830000 1.000 1.000 

15000270 15 Barley, bran 2.830000 1.900 1.000 

21000460 M Beef, meat byproducts 0.100000 1.000 1.000 

21000461 M Beef, meat byproducts-babyfood 0.100000 1.000 1.000 

21000480 M Beef, kidney 0.100000 1.000 1.000 

21000490 M Beef, liver 0.100000 1.000 1.000 

21000491 M Beef, liver-babyfood 0.100000 1.000 1.000 

01010520 1A Beet, sugar 0.070000 1.000 1.000 

01010521 1A Beet, sugar-babyfood 0.070000 1.000 1.000 

01010530 1A Beet, sugar, molasses 0.080000 1.000 1.000 

01010531 1A Beet, sugar, molasses-babyfood 0.080000 1.000 1.000 

13020570 13B Blueberry 0.400000 1.000 1.000 

13020571 13B Blueberry-babyfood 0.400000 1.000 1.000 

14000590 14 Brazil nut 0.040000 1.000 1.000 

14000680 14 Butternut 0.040000 1.000 1.000 

14000810 14 Cashew 0.040000 1.000 1.000 

01030820 1CD Cassava 0.040000 1.000 1.000 

01030821 1CD Cassava-babyfood 0.040000 1.000 1.000 

12000900 12 Cherry 0.200000 1.000 1.000 

12000901 12 Cherry-babyfood 0.200000 1.000 1.000 

12000910 12 Cherry, juice 0.200000 1.500 1.000 

12000911 12 Cherry, juice-babyfood 0.200000 1.500 1.000 

14000920 14 Chestnut 0.040000 1.000 1.000 

15001200 15 Corn, field, flour 0.030000 1.000 1.000 

15001201 15 Corn, field, flour-babyfood 0.030000 1.000 1.000 

15001210 15 Corn, field, meal 0.030000 1.000 1.000 

15001211 15 Corn, field, meal-babyfood 0.030000 1.000 1.000 

15001220 15 Corn, field, bran 0.030000 1.000 1.000 

15001230 15 Corn, field, starch 0.030000 1.000 1.000 

15001231 15 Corn, field, starch-babyfood 0.030000 1.000 1.000 

15001240 15 Corn, field, syrup 0.030000 1.500 1.000 

15001241 15 Corn, field, syrup-babyfood 0.030000 1.500 1.000 

15001250 15 Corn, field, oil 0.030000 1.000 1.000 

15001251 15 Corn, field, oil-babyfood 0.030000 1.000 1.000 

15001260 15 Corn, pop 0.030000 1.000 1.000 

15001270 15 Corn, sweet 0.020000 1.000 1.000 

15001271 15 Corn, sweet-babyfood 0.020000 1.000 1.000 

95001280 O Cottonseed, oil 0.250000 1.000 1.000 
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95001281 O Cottonseed, oil-babyfood 0.250000 1.000 1.000 

95001300 O Cranberry 0.400000 1.000 1.000 

95001301 O Cranberry-babyfood 0.400000 1.000 1.000 

95001310 O Cranberry, dried 0.400000 1.000 1.000 

13021360 13B Currant 0.400000 1.000 1.000 

13021370 13B Currant, dried 0.400000 1.000 1.000 

01031390 1CD Dasheen, corm 0.040000 1.000 1.000 

13021490 13B Elderberry 0.400000 1.000 1.000 

14001550 14 Filbert 0.040000 1.000 1.000 

14001560 14 Filbert, oil 0.040000 1.000 1.000 

01031660 1CD Ginger 0.040000 1.000 1.000 

01031661 1CD Ginger-babyfood 0.040000 1.000 1.000 

01031670 1CD Ginger, dried 0.040000 1.000 1.000 

23001700 M Goat, meat byproducts 0.100000 1.000 1.000 

23001720 M Goat, kidney 0.100000 1.000 1.000 

23001730 M Goat, liver 0.100000 1.000 1.000 

13021740 13B Gooseberry 0.400000 1.000 1.000 

14001850 14 Hickory nut 0.040000 1.000 1.000 

13021910 13B Huckleberry 0.400000 1.000 1.000 

14002130 14 Macadamia nut 0.040000 1.000 1.000 

12002300 12 Nectarine 0.200000 1.000 1.000 

15002310 15 Oat, bran 1.340000 1.900 1.000 

15002320 15 Oat, flour 1.340000 1.000 1.000 

15002321 15 Oat, flour-babyfood 1.340000 1.000 1.000 

15002330 15 Oat, groats/rolled oats 1.340000 1.000 1.000 

15002331 15 Oat, groats/rolled oats-babyfood 1.340000 1.000 1.000 

12002600 12 Peach 0.200000 1.000 1.000 

12002601 12 Peach-babyfood 0.200000 1.000 1.000 

12002610 12 Peach, dried 0.200000 7.000 1.000 

12002611 12 Peach, dried-babyfood 0.200000 7.000 1.000 

12002620 12 Peach, juice 0.200000 1.000 1.000 

12002621 12 Peach, juice-babyfood 0.200000 1.000 1.000 

95002630 O Peanut 0.040000 1.000 1.000 

95002640 O Peanut, butter 0.050000 1.890 1.000 

95002650 O Peanut, oil 0.050000 1.300 1.000 

14002690 14 Pecan 0.040000 1.000 1.000 

14002820 14 Pistachio 0.040000 1.000 1.000 

95002830 O Plantain 0.100000 1.000 1.000 

95002840 O Plantain, dried 0.100000 3.900 1.000 

12002850 12 Plum 0.200000 1.000 1.000 

12002851 12 Plum-babyfood 0.200000 1.000 1.000 

12002860 12 Plum, prune, fresh 0.200000 1.000 1.000 

12002861 12 Plum, prune, fresh-babyfood 0.200000 1.000 1.000 

12002870 12 Plum, prune, dried 0.200000 2.300 1.000 

12002871 12 Plum, prune, dried-babyfood 0.200000 2.300 1.000 

12002880 12 Plum, prune, juice 0.200000 1.400 1.000 

12002881 12 Plum, prune, juice-babyfood 0.200000 1.400 1.000 

01032960 1C Potato, chips 0.040000 1.000 1.000 

01032970 1C Potato, dry (granules/ flakes) 0.040000 1.000 1.000 

01032971 1C Potato, dry (granules/ flakes)-b 0.040000 1.000 1.000 

01032980 1C Potato, flour 0.040000 1.000 1.000 

01032981 1C Potato, flour-babyfood 0.040000 1.000 1.000 

01032990 1C Potato, tuber, w/peel 0.040000 1.000 1.000 

01032991 1C Potato, tuber, w/peel-babyfood 0.040000 1.000 1.000 

01033000 1C Potato, tuber, w/o peel 0.040000 1.000 1.000 

01033001 1C Potato, tuber, w/o peel-babyfood 0.040000 1.000 1.000 

20003190 20 Rapeseed, oil 0.040000 1.000 1.000 

20003191 20 Rapeseed, oil-babyfood 0.040000 1.000 1.000 

15003280 15 Rye, grain 0.290000 1.000 1.000 

15003290 15 Rye, flour 0.290000 1.000 1.000 

26003400 M Sheep, meat byproducts 0.100000 1.000 1.000 

26003420 M Sheep, kidney 0.100000 1.000 1.000 

26003430 M Sheep, liver 0.100000 1.000 1.000 

06003470 6 Soybean, seed 0.050000 1.000 1.000 

06003480 6 Soybean, flour 0.050000 1.000 1.000 

06003481 6 Soybean, flour-babyfood 0.050000 1.000 1.000 

06003490 6 Soybean, soy milk 0.050000 1.000 1.000 

06003491 6 Soybean, soy milk-babyfood or in 0.050000 1.000 1.000 

06003500 6 Soybean, oil 0.050000 1.000 1.000 

06003501 6 Soybean, oil-babyfood 0.050000 1.000 1.000 

95003620 O Sugarcane, sugar 1.600000 1.000 1.000 

95003621 O Sugarcane, sugar-babyfood 1.600000 1.000 1.000 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 12 of 17 

95003630 O Sugarcane, molasses 3.200000 2.000 1.000 

95003631 O Sugarcane, molasses-babyfood 3.200000 2.000 1.000 

01033660 1CD Sweet potato 0.040000 1.000 1.000 

01033661 1CD Sweet potato-babyfood 0.040000 1.000 1.000 

01033710 1CD Tanier, corm 0.040000 1.000 1.000 

01033870 1CD Turmeric 0.040000 1.000 1.000 

14003910 14 Walnut 0.040000 1.000 1.000 

86010000 O Water, direct, all sources 0.045480 1.000 1.000 

86020000 O Water, indirect, all sources 0.045480 1.000 1.000 

15004010 15 Wheat, grain 0.180000 1.000 1.000 

15004011 15 Wheat, grain-babyfood 0.180000 1.000 1.000 

15004020 15 Wheat, flour 0.180000 1.000 1.000 

15004021 15 Wheat, flour-babyfood 0.180000 1.000 1.000 

15004030 15 Wheat, germ 0.180000 1.000 1.000 

15004040 15 Wheat, bran 0.180000 1.900 1.000 

01034060 1CD Yam, true 0.040000 1.000 1.000 

01034070 1CD Yam bean 0.040000 1.000 1.000 

Attachment 2: Acute Food plus Water Results File 

U.S. Environmental Protection Agency Ver. 2.02 

DEEM-FCID ACUTE Analysis for METCONAZOLE (1994-98 data) 

Residue file: MetconazoleTuberousCormBushberry Accute.R98 

Adjustment factor #2 NOT used. 

Analysis Date: 04-05-2011/13:13:30 Residue file dated: 04-05-2011/13:12:04/8 

NOEL (Acute) = 12.000000 mg/kg body-wt/day 

Daily totals for food and foodform consumption used. 

Run Comment: "Vegetables, Tuberous & Corm, Subgroup 1C and Bushberry Subgroup 

13-07B " 

=============================================================================== 

Summary calculations (per capita): 

 95th Percentile 99th Percentile 99.9th Percentile 

 Exposure % aRfD MOE Exposure % aRfD MOE Exposure % aRfD MOE 

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

Females 13-49 yrs: 

 0.004578 3.81 2621 0.007573 6.31 1584 0.014748 12.29 813 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 13 of 17 

Attachment 3: Chronic Food plus Water Residue Input File 

U.S. Environmental Protection Agency Ver. 2.00 

DEEM-FCID Chronic analysis for METCONAZOLE 1994-98 data 

Residue file: C:\Documents and Settings\aacierto\Desktop\DEEM-FCID 

Files\2011\MetconazoleTuberousCormBushberry Chronic.R98 

 Adjust. #2 NOT used 

Analysis Date 04-05-2011 Residue file dated: 04-05-2011/13:20:02/8 

Reference dose (RfD) = 0.04 (NOEL) = 4.3 mg/kg bw/day 

Comment:Vegetables, Tuberous & Corm, Subgroup 1C and Bushberry Subgroup 13-07B 

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

Food Crop Residue Adj.Factors Comment 

EPA Code Grp Food Name (ppm) 

 #1 #2 

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

14000030 14 Almond 0.040000 1.000 1.000 

14000031 14 Almond-babyfood 0.040000 1.000 1.000 

14000040 14 Almond, oil 0.040000 1.000 1.000 

14000041 14 Almond, oil-babyfood 0.040000 1.000 1.000 

12000120 12 Apricot 0.200000 1.000 1.000 

12000121 12 Apricot-babyfood 0.200000 1.000 1.000 

12000130 12 Apricot, dried 0.200000 6.000 1.000 

12000140 12 Apricot, juice 0.200000 1.000 1.000 

12000141 12 Apricot, juice-babyfood 0.200000 1.000 1.000 

01030150 1CD Arrowroot, flour 0.040000 1.000 1.000 

01030151 1CD Arrowroot, flour-babyfood 0.040000 1.000 1.000 

01030170 1CD Artichoke, Jerusalem 0.040000 1.000 1.000 

95000230 O Banana 0.100000 1.000 1.000 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 14 of 17 

95000231 O Banana-babyfood 0.100000 1.000 1.000 

95000240 O Banana, dried 0.100000 3.900 1.000 

95000241 O Banana, dried-babyfood 0.100000 3.900 1.000 

15000250 15 Barley, pearled barley 2.830000 1.000 1.000 

15000251 15 Barley, pearled barley-babyfood 2.830000 1.000 1.000 

15000260 15 Barley, flour 2.830000 1.000 1.000 

15000261 15 Barley, flour-babyfood 2.830000 1.000 1.000 

15000270 15 Barley, bran 2.830000 1.900 1.000 

21000460 M Beef, meat byproducts 0.100000 1.000 1.000 

21000461 M Beef, meat byproducts-babyfood 0.100000 1.000 1.000 

21000480 M Beef, kidney 0.100000 1.000 1.000 

21000490 M Beef, liver 0.100000 1.000 1.000 

21000491 M Beef, liver-babyfood 0.100000 1.000 1.000 

01010520 1A Beet, sugar 0.070000 1.000 1.000 

01010521 1A Beet, sugar-babyfood 0.070000 1.000 1.000 

01010530 1A Beet, sugar, molasses 0.080000 1.000 1.000 

01010531 1A Beet, sugar, molasses-babyfood 0.080000 1.000 1.000 

13020570 13B Blueberry 0.400000 1.000 1.000 

13020571 13B Blueberry-babyfood 0.400000 1.000 1.000 

14000590 14 Brazil nut 0.040000 1.000 1.000 

14000680 14 Butternut 0.040000 1.000 1.000 

14000810 14 Cashew 0.040000 1.000 1.000 

01030820 1CD Cassava 0.040000 1.000 1.000 

01030821 1CD Cassava-babyfood 0.040000 1.000 1.000 

12000900 12 Cherry 0.200000 1.000 1.000 

12000901 12 Cherry-babyfood 0.200000 1.000 1.000 

12000910 12 Cherry, juice 0.200000 1.500 1.000 

12000911 12 Cherry, juice-babyfood 0.200000 1.500 1.000 

14000920 14 Chestnut 0.040000 1.000 1.000 

15001200 15 Corn, field, flour 0.030000 1.000 1.000 

15001201 15 Corn, field, flour-babyfood 0.030000 1.000 1.000 

15001210 15 Corn, field, meal 0.030000 1.000 1.000 

15001211 15 Corn, field, meal-babyfood 0.030000 1.000 1.000 

15001220 15 Corn, field, bran 0.030000 1.000 1.000 

15001230 15 Corn, field, starch 0.030000 1.000 1.000 

15001231 15 Corn, field, starch-babyfood 0.030000 1.000 1.000 

15001240 15 Corn, field, syrup 0.030000 1.500 1.000 

15001241 15 Corn, field, syrup-babyfood 0.030000 1.500 1.000 

15001250 15 Corn, field, oil 0.030000 1.000 1.000 

15001251 15 Corn, field, oil-babyfood 0.030000 1.000 1.000 

15001260 15 Corn, pop 0.030000 1.000 1.000 

15001270 15 Corn, sweet 0.020000 1.000 1.000 

15001271 15 Corn, sweet-babyfood 0.020000 1.000 1.000 

95001280 O Cottonseed, oil 0.250000 1.000 1.000 

95001281 O Cottonseed, oil-babyfood 0.250000 1.000 1.000 

95001300 O Cranberry 0.400000 1.000 1.000 

95001301 O Cranberry-babyfood 0.400000 1.000 1.000 

95001310 O Cranberry, dried 0.400000 1.000 1.000 

13021360 13B Currant 0.400000 1.000 1.000 

13021370 13B Currant, dried 0.400000 1.000 1.000 

01031390 1CD Dasheen, corm 0.040000 1.000 1.000 

13021490 13B Elderberry 0.400000 1.000 1.000 

14001550 14 Filbert 0.040000 1.000 1.000 

14001560 14 Filbert, oil 0.040000 1.000 1.000 

01031660 1CD Ginger 0.040000 1.000 1.000 

01031661 1CD Ginger-babyfood 0.040000 1.000 1.000 

01031670 1CD Ginger, dried 0.040000 1.000 1.000 

23001700 M Goat, meat byproducts 0.100000 1.000 1.000 

23001720 M Goat, kidney 0.100000 1.000 1.000 

23001730 M Goat, liver 0.100000 1.000 1.000 

13021740 13B Gooseberry 0.400000 1.000 1.000 

14001850 14 Hickory nut 0.040000 1.000 1.000 

13021910 13B Huckleberry 0.400000 1.000 1.000 

14002130 14 Macadamia nut 0.040000 1.000 1.000 

12002300 12 Nectarine 0.200000 1.000 1.000 

15002310 15 Oat, bran 1.340000 1.900 1.000 

15002320 15 Oat, flour 1.340000 1.000 1.000 

15002321 15 Oat, flour-babyfood 1.340000 1.000 1.000 

15002330 15 Oat, groats/rolled oats 1.340000 1.000 1.000 

15002331 15 Oat, groats/rolled oats-babyfood 1.340000 1.000 1.000 

12002600 12 Peach 0.200000 1.000 1.000 

12002601 12 Peach-babyfood 0.200000 1.000 1.000 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 15 of 17 

12002610 12 Peach, dried 0.200000 7.000 1.000 

12002611 12 Peach, dried-babyfood 0.200000 7.000 1.000 

12002620 12 Peach, juice 0.200000 1.000 1.000 

12002621 12 Peach, juice-babyfood 0.200000 1.000 1.000 

95002630 O Peanut 0.040000 1.000 1.000 

95002640 O Peanut, butter 0.050000 1.890 1.000 

95002650 O Peanut, oil 0.050000 1.300 1.000 

14002690 14 Pecan 0.040000 1.000 1.000 

14002820 14 Pistachio 0.040000 1.000 1.000 

95002830 O Plantain 0.100000 1.000 1.000 

95002840 O Plantain, dried 0.100000 3.900 1.000 

12002850 12 Plum 0.200000 1.000 1.000 

12002851 12 Plum-babyfood 0.200000 1.000 1.000 

12002860 12 Plum, prune, fresh 0.200000 1.000 1.000 

12002861 12 Plum, prune, fresh-babyfood 0.200000 1.000 1.000 

12002870 12 Plum, prune, dried 0.200000 2.300 1.000 

12002871 12 Plum, prune, dried-babyfood 0.200000 2.300 1.000 

12002880 12 Plum, prune, juice 0.200000 1.400 1.000 

12002881 12 Plum, prune, juice-babyfood 0.200000 1.400 1.000 

01032960 1C Potato, chips 0.040000 1.000 1.000 

01032970 1C Potato, dry (granules/ flakes) 0.040000 1.000 1.000 

01032971 1C Potato, dry (granules/ flakes)-b 0.040000 1.000 1.000 

01032980 1C Potato, flour 0.040000 1.000 1.000 

01032981 1C Potato, flour-babyfood 0.040000 1.000 1.000 

01032990 1C Potato, tuber, w/peel 0.040000 1.000 1.000 

01032991 1C Potato, tuber, w/peel-babyfood 0.040000 1.000 1.000 

01033000 1C Potato, tuber, w/o peel 0.040000 1.000 1.000 

01033001 1C Potato, tuber, w/o peel-babyfood 0.040000 1.000 1.000 

20003190 20 Rapeseed, oil 0.040000 1.000 1.000 

20003191 20 Rapeseed, oil-babyfood 0.040000 1.000 1.000 

15003280 15 Rye, grain 0.290000 1.000 1.000 

15003290 15 Rye, flour 0.290000 1.000 1.000 

26003400 M Sheep, meat byproducts 0.100000 1.000 1.000 

26003420 M Sheep, kidney 0.100000 1.000 1.000 

26003430 M Sheep, liver 0.100000 1.000 1.000 

06003470 6 Soybean, seed 0.050000 1.000 1.000 

06003480 6 Soybean, flour 0.050000 1.000 1.000 

06003481 6 Soybean, flour-babyfood 0.050000 1.000 1.000 

06003490 6 Soybean, soy milk 0.050000 1.000 1.000 

06003491 6 Soybean, soy milk-babyfood or in 0.050000 1.000 1.000 

06003500 6 Soybean, oil 0.050000 1.000 1.000 

06003501 6 Soybean, oil-babyfood 0.050000 1.000 1.000 

95003620 O Sugarcane, sugar 1.600000 1.000 1.000 

95003621 O Sugarcane, sugar-babyfood 1.600000 1.000 1.000 

95003630 O Sugarcane, molasses 3.200000 2.000 1.000 

95003631 O Sugarcane, molasses-babyfood 3.200000 2.000 1.000 

01033660 1CD Sweet potato 0.040000 1.000 1.000 

01033661 1CD Sweet potato-babyfood 0.040000 1.000 1.000 

01033710 1CD Tanier, corm 0.040000 1.000 1.000 

01033870 1CD Turmeric 0.040000 1.000 1.000 

14003910 14 Walnut 0.040000 1.000 1.000 

86010000 O Water, direct, all sources 0.038160 1.000 1.000 

86020000 O Water, indirect, all sources 0.038160 1.000 1.000 

15004010 15 Wheat, grain 0.180000 1.000 1.000 

15004011 15 Wheat, grain-babyfood 0.180000 1.000 1.000 

15004020 15 Wheat, flour 0.180000 1.000 1.000 

15004021 15 Wheat, flour-babyfood 0.180000 1.000 1.000 

15004030 15 Wheat, germ 0.180000 1.000 1.000 

15004040 15 Wheat, bran 0.180000 1.900 1.000 

01034060 1CD Yam, true 0.040000 1.000 1.000 

01034070 1CD Yam bean 0.040000 1.000 1.000 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 16 of 17 

Attachment 4: Chronic Food plus Water Residue Results File 

U.S. Environmental Protection Agency Ver. 2.00 

DEEM-FCID Chronic analysis for METCONAZOLE (1994-98 data) 

Residue file name: C:\Documents and Settings\aacierto\Desktop\DEEM-FCID 

Files\2011\MetconazoleTuberousCormBushberry Chronic.R98 

 Adjustment factor #2 NOT used. 

Analysis Date 04-05-2011/15:42:35 Residue file dated: 04-05-2011/13:20:02/8 

Reference dose (RfD, Chronic) = .04 mg/kg bw/day 

NOEL (Chronic) = 4.3 mg/kg bw/day 

COMMENT 1: Vegetables, Tuberous & Corm, Subgroup 1C and Bushberry Subgroup 13-07B 

=============================================================================== 

 Total exposure by population subgroup 

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

 Total Exposure 

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

 Population mg/kg Margin of Percent 

 Subgroup body wt/day Exposure 1/ of RfD 

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

U.S. Population (total) 0.002434 1,766 6.1% 

U.S. Population (spring season) 0.002505 1,716 6.3% 

U.S. Population (summer season) 0.002499 1,721 6.2% 

U.S. Population (autumn season) 0.002363 1,820 5.9% 

U.S. Population (winter season) 0.002372 1,813 5.9% 

Northeast region 0.002325 1,850 5.8% 

Midwest region 0.002584 1,664 6.5% 

Southern region 0.002294 1,874 5.7% 

Western region 0.002595 1,657 6.5% 

Hispanics 0.002447 1,758 6.1% 

Non-hispanic whites 0.002462 1,747 6.2% 

Non-hispanic blacks 0.002295 1,874 5.7% 

Non-hisp/non-white/non-black 0.002359 1,823 5.9% 

All infants (< 1 year) 0.004831 890 12.1% 

Nursing infants 0.002219 1,938 5.5% 

Non-nursing infants 0.005823 738 14.6% 

Children 1-6 yrs 0.004787 898 12.0% 

Children 7-12 yrs 0.003113 1,381 7.8% 

Females 13-19 (not preg or nursing) 0.001774 2,424 4.4% 

Females 20+ (not preg or nursing) 0.001840 2,337 4.6% 

Females 13-50 yrs 0.001985 2,167 5.0% 

Females 13+ (preg/not nursing) 0.002024 2,124 5.1% 

Females 13+ (nursing) 0.002381 1,806 6.0% 

Males 13-19 yrs 0.002137 2,012 5.3% 

Males 20+ yrs 0.002275 1,890 5.7% 

Seniors 55+ 0.001840 2,337 4.6% 

Children 1-2 yrs 0.005026 856 12.6% 
Metconazole Dietary-Exposure and Risk Assessment DP #: D387504 

PC Code: 125619 

_____________________________________________________________________________________________ 

Page 17 of 17 

Children 3-5 yrs 0.004800 896 12.0% 

Children 6-12 yrs 0.003289 1,307 8.2% 

Youth 13-19 yrs 0.001961 2,193 4.9% 

Adults 20-49 yrs 0.002158 1,992 5.4% 

Adults 50+ yrs 0.001868 2,302 4.7% 

Females 13-49 yrs 0.001874 2,295 4.7%