Dichlorvos (DDVP) Risk Characterization Document - California ...

Dichlorvos (DDVP) Risk Characterization Document - California ... Dichlorvos (DDVP) Risk Characterization Document - California ...

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Table 17. DDVP residue database. Residue Levels Commodity number highest mean a of samples (ppm) (ppm) RAC b cucumbers 10 0.055 0.0103 lettuce 8 0.026 0.0035 radishes 7 0.003 0.0015 tomatoes 9 0.023 0.0065 Meat Products c cattle d - 0.01 0.005 eggs - 0.05 0.05 goats - 0.02 0.02 horses - 0.02 0.02 milk d - 0.01 0.005 poultry - 0.05 0.05 sheep - 0.02 0.02 swine - 0.10 0.10 Processed commodities e chocolate chips 2 0.098 0.098 cocoa beans 2 0.025 0.0175 coconut 2 0.025 0.0175 flour 2 0.082 0.048 oats 1

Acute Exposure Estimates of potential acute dietary exposure used the highest measured residue values at or below the tolerance levels for each commodity except for the use of tolerance levels for meat products (Table 17 and Appendix A). The following assumptions are used to estimate potential acute dietary exposure from measured residues: (1) the residue does not change over time, (2) the concentration of residue does not decrease when the RAC is washed or cooked, and (3) all foods that are consumed will contain the highest reported residue. Chronic Exposure Estimates of potential average annual chronic dietary exposure used the mean of measured and "below detection limit" residue values for each commodity. The default procedure assumed that "below detection limit" residues were equal to one-half (50%) of the MDL for each commodity. The following assumptions were used to estimate potential chronic dietary exposures from measured residues: (1) the residue level does not change over time, (2) residue are not reduced by washing or cooking, and (3) exposures to a commodity at all reported residue levels do occur, i.e. a commodity with the average calculated residue is consumed every day at an average annual level (dosage). The actual residue values used are presented in Table 17. Lifetime Exposure Estimate of potential lifetime dietary exposure used the result for the US general population from the chronic dietary analysis. Dietary Assessment Dietary assessment of DDVP was conducted for acute, chronic, and lifetime exposures. Copies of the exposure analyses are available upon request to the Medical Toxicology Branch. Acute Exposure Acute dietary exposure analyses were conducted using the Exposure-4 software program developed by Technical Assessment Systems, Inc. (TAS). The Exposure-4 program estimates the distribution of user-day (consumer-day) exposure for the overall U.S. population and specific population subgroups (TAS, 1992a). A user-day is any day in which at least one food from the specific commodity list is consumed. The consumption analysis uses individual food consumption data as reported in the 1987-88 USDA Nationwide Food Consumption Survey (USDA, 1987-88). Based on the 95th percentile of user-days exposures for all specific population subgroups, the potential acute dietary exposure of DDVP from all labeled uses ranged from 0.50 to 1.65 ug/kg-day (Table 18). Children (1-6 years old) had the highest potential acute dietary exposure (1.65 ug/kg-day) to DDVP residues. Chronic Exposure The potential chronic dietary exposure was calculated using the Exposure-1 software program developed by TAS, Inc. (TAS, 1992b). The food consumption data for the chronic analysis were also based on the 1987-88 USDA Nationwide Food Consumption Survey (USDA, 1987-88). The program estimates the average annual exposure for all members of a designated population subgroup. The mean potential chronic dietary exposure for all population subgroups ranged from 0.06 to 0.53 ug/kgday (Table 18). The population subgroup of children (1-6 years) had the highest potential exposure (0.53 ug/kg-day). This level is 5,300-fold higher than the level (0.0001 ug/kg-day) estimated by the 66

Acute Exposure<br />

Estimates of potential acute dietary exposure used the highest measured residue values at or below<br />

the tolerance levels for each commodity except for the use of tolerance levels for meat products<br />

(Table 17 and Appendix A). The following assumptions are used to estimate potential acute dietary<br />

exposure from measured residues: (1) the residue does not change over time, (2) the concentration<br />

of residue does not decrease when the RAC is washed or cooked, and (3) all foods that are<br />

consumed will contain the highest reported residue.<br />

Chronic Exposure<br />

Estimates of potential average annual chronic dietary exposure used the mean of measured and<br />

"below detection limit" residue values for each commodity. The default procedure assumed that<br />

"below detection limit" residues were equal to one-half (50%) of the MDL for each commodity. The<br />

following assumptions were used to estimate potential chronic dietary exposures from measured<br />

residues: (1) the residue level does not change over time, (2) residue are not reduced by washing or<br />

cooking, and (3) exposures to a commodity at all reported residue levels do occur, i.e. a commodity<br />

with the average calculated residue is consumed every day at an average annual level (dosage). The<br />

actual residue values used are presented in Table 17.<br />

Lifetime Exposure<br />

Estimate of potential lifetime dietary exposure used the result for the US general population from the<br />

chronic dietary analysis.<br />

Dietary Assessment<br />

Dietary assessment of <strong>DDVP</strong> was conducted for acute, chronic, and lifetime exposures. Copies of the<br />

exposure analyses are available upon request to the Medical Toxicology Branch.<br />

Acute Exposure<br />

Acute dietary exposure analyses were conducted using the Exposure-4 software program developed<br />

by Technical Assessment Systems, Inc. (TAS). The Exposure-4 program estimates the distribution<br />

of user-day (consumer-day) exposure for the overall U.S. population and specific population<br />

subgroups (TAS, 1992a). A user-day is any day in which at least one food from the specific<br />

commodity list is consumed. The consumption analysis uses individual food consumption data as<br />

reported in the 1987-88 USDA Nationwide Food Consumption Survey (USDA, 1987-88).<br />

Based on the 95th percentile of user-days exposures for all specific population subgroups, the<br />

potential acute dietary exposure of <strong>DDVP</strong> from all labeled uses ranged from 0.50 to 1.65 ug/kg-day<br />

(Table 18). Children (1-6 years old) had the highest potential acute dietary exposure (1.65 ug/kg-day)<br />

to <strong>DDVP</strong> residues.<br />

Chronic Exposure<br />

The potential chronic dietary exposure was calculated using the Exposure-1 software program<br />

developed by TAS, Inc. (TAS, 1992b). The food consumption data for the chronic analysis were also<br />

based on the 1987-88 USDA Nationwide Food Consumption Survey (USDA, 1987-88). The program<br />

estimates the average annual exposure for all members of a designated population subgroup. The<br />

mean potential chronic dietary exposure for all population subgroups ranged from 0.06 to 0.53 ug/kgday<br />

(Table 18). The population subgroup of children (1-6 years) had the highest potential exposure<br />

(0.53 ug/kg-day). This level is 5,300-fold higher than the level (0.0001 ug/kg-day) estimated by the<br />

66

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