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

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

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I. SUMMARY A risk assessment has been conducted on dichlorvos (2,2-dichlorovinyl dimethyl phosphate, DDVP) because of possible adverse effects identified in rat and mouse oncogenicity, neurotoxicity, and genotoxicity studies. DDVP is listed under Proposition 65 as a chemical known to the State of California to cause cancer. INTRODUCTION Chemical Identification- DDVP is an organophosphate insecticide used for the control of pests in enclosed spaces such as buildings and residents, on pets, on vegetables in greenhouses, on commodities during post-harvest storage, and on livestock. From 1991 to 1993, approximately 4000- 5000 pounds/year of DDVP were used primarily for structural and livestock pest control. DDVP exerts its toxicological activity primarily through the inhibition of acetylcholinesterase activity. Signs and symptoms associated with its toxicity included salivation, diarrhea, tremors, and death. Regulatory History- DDVP is currently under Special Review by the U.S. Environmental Protection Agency (USEPA). In 1989, the Scientific Advisory Panel of the USEPA recommended that DDVP oncogenicity classification be changed from a B2 carcinogen to a C carcinogen. Because of oncogenic risks, most of the food tolerances have been revoked. A revocation of tolerances for bagged or packaged nonperishable commodities has been proposed. In 1993, the registrations of DDVP in California for the use on fresh vegetables were voluntarily cancelled by the registrants. Environmental Fate- DDVP is not likely to persist in the environment since it is volatile, does not bind to soil, and is hydrolyzed. The half-life of DDVP was 5.2 days in aqueous buffered solution at pH 7. The half-lives ranged from 9 to 20 days for DDVP in tap water with pH 7.5 to 8.1. DDVP was also degraded by soil microorganisms with a half-life of 10.2 hours. After foliar application, DDVP residues on the leaves may be volatilized, hydrolyzed, and absorbed into the plants. TOXICOLOGY PROFILE Pharmacokinetics- DDVP was rapidly absorbed by the oral, intravenous, intraperitoneal, and inhalation routes and slowly absorbed by the dermal route. After absorption, the radioactivity distributed to major organs including the liver and kidneys. DDVP was metabolized completely by ester hydrolysis and demethylation. Initial metabolites were mono- and dimethyl phosphates, and desmethyl DDVP. Once formed, they may be further metabolized. Final metabolites were either incorporated in tissues or excreted. Major routes of excretion were in the urine and in the exhaled air, while to a lesser extent in the feces and in the milk. Excretion routes, tissue distribution, and urinary metabolites in rats were similar following inhalation or oral exposures. Acute Toxicity- DDVP was more toxic than its metabolites as determined by the magnitude of the 72 hour lethal dose after intraperitoneal administration. Human exposure of DDVP by ingestion and from the use of no-pest strips resulted in the inhibition of plasma cholinesterase (ChE) activity, but not erythrocyte ChE activity. Acute effects observed in laboratory animals from oral or inhalation exposures included diarrhea, irritability, salivation, lethargy, pupillary constriction, tremors, decreased neuromuscular functions, and death. Subchronic Toxicity- Subchronic exposures to DDVP resulted in the inhibition of brain, erythrocyte, or/and plasma ChE activities in humans, rats, mice, dogs, and cows. Clinical signs observed in laboratory animals were tremors, diarrhea, decreased body weight gain, increased frequency of salivation and urine staining in rats, and increased activity and urination in dogs. Other effects included statistically significant decreases in red blood cell parameters (cell counts, hemoglobin, and 1

hematocrit) in rats. From studies with lactating rats and milk cows after oral subchronic dosing, ChE activity depression and cholinergic signs were noted in the dams, but not in the offspring. Chronic Toxicity and Oncogenicity- DDVP caused the inhibition of plasma, erythrocyte, and brain ChE activities. Other non-oncogenic effects included hepatocellular lesions (vacuoles in the cytoplasm, cell swelling, prominence of cell membranes), reduced body weight, emesis, salivation, and ataxia. Oncogenic effects observed in rats and mice were pancreatic adenoma; mononuclear leukemia; mammary gland carcinoma, fibroadenoma, and adenoma; forestomach papillomas and carcinomas; and pituitary adenomas. DDVP also increased tumor growth rate in rats given leukemia transplant. Genotoxicity- DDVP was genotoxic in some in vitro systems, including assays with Salmonella TA 100 strain and Schizosaccharomyces pombe, mouse lymphoma forward mutation assay, and unscheduled DNA synthesis assay using human epithelial cells. However, DDVP was not genotoxic in the micronucleus, dominant lethal, in vivo chromosomal aberrations, and in vivo sister chromatid exchange assays. Studies conducted in the presence and absence of a liver preparation (S-9 fraction) showed that the decrease in genotoxicity in the presence of the preparation may be due to the inactivation of DDVP by liver esterases. Methylated DNA was detected in tissues of mice given DDVP by intraperitoneal injection, but not in rat tissues when DDVP was given by inhalation. Reproductive Toxicity- Exposure of rats to DDVP in the water during reproduction resulted in the inhibition of plasma, erythrocyte, and brain ChE. Clinical signs were observed in both parents and offsprings. Other toxicity included decreased body weights and decreased water consumption. Remating of the F 1 females after the F 2 generation showed that decreased estrous cycling and increased incidence of abnormal estrus cycling. Mice exposed to DDVP-containing resin strips showed only plasma ChE depression and no effect on reproduction. Developmental Toxicity- DDVP, given by oral or inhalation routes, was not teratogenic in rats, mice, or rabbits. Cholinergic signs (tremors, ataxia, diarrhea, and other effects) were observed in the pregnant rats and rabbits. Neurotoxicity- Possible adverse effects of nerve fiber degeneration and spinal cord degeneration were observed in chickens treated with DDVP. No acute delayed neurotoxicity in hens was reported, except at lethal doses. Acute neurotoxicity study in the rat given DDVP by gavage resulted in cholinergic effects which included gait alteration, constricted pupils, tremors, and salivation. RISK ASSESSMENT Hazard Identification- The no-observed-effects levels (NOELs) from both inhalation and oral studies, and oncogenic risk from an oral study were used to evaluate the health hazards from potential exposure by workers and the general population to DDVP. For non-oncogenic endpoints, acute and chronic inhalation and dietary exposures were considered. For oncogenic endpoints, inhalation and dietary exposures to DDVP were assessed. For acute inhalation exposure, the definitive NOEL was 1.25 ug/L or 0.65 mg/kg-day (NOEL adjusted for exposure duration and respiration rate). The NOEL was based on death in pregnant rabbits after 2 days of inhalation exposure to a LOEL of 2 ug/L DDVP. The NOEL for acute oral exposure was 0.5 mg/kg-day based on tremors, salivation, neuromuscular deficits, and other cholinergic signs observed in rats within 1 day after a single dose by gavage. The NOELs for chronic toxicity were based on the inhibition of brain ChE activity in a one-year dog oral study and a two-year rat inhalation study. The adjusted NOELs for inhalation and oral routes were 0.025 mg/kg-day, and 0.05 mg/kg-day, respectively. 2

hematocrit) in rats. From studies with lactating rats and milk cows after oral subchronic dosing, ChE<br />

activity depression and cholinergic signs were noted in the dams, but not in the offspring.<br />

Chronic Toxicity and Oncogenicity- <strong>DDVP</strong> caused the inhibition of plasma, erythrocyte, and brain<br />

ChE activities. Other non-oncogenic effects included hepatocellular lesions (vacuoles in the<br />

cytoplasm, cell swelling, prominence of cell membranes), reduced body weight, emesis, salivation,<br />

and ataxia. Oncogenic effects observed in rats and mice were pancreatic adenoma; mononuclear<br />

leukemia; mammary gland carcinoma, fibroadenoma, and adenoma; forestomach papillomas and<br />

carcinomas; and pituitary adenomas. <strong>DDVP</strong> also increased tumor growth rate in rats given leukemia<br />

transplant.<br />

Genotoxicity- <strong>DDVP</strong> was genotoxic in some in vitro systems, including assays with Salmonella TA<br />

100 strain and Schizosaccharomyces pombe, mouse lymphoma forward mutation assay, and<br />

unscheduled DNA synthesis assay using human epithelial cells. However, <strong>DDVP</strong> was not genotoxic<br />

in the micronucleus, dominant lethal, in vivo chromosomal aberrations, and in vivo sister chromatid<br />

exchange assays. Studies conducted in the presence and absence of a liver preparation (S-9<br />

fraction) showed that the decrease in genotoxicity in the presence of the preparation may be due to<br />

the inactivation of <strong>DDVP</strong> by liver esterases. Methylated DNA was detected in tissues of mice given<br />

<strong>DDVP</strong> by intraperitoneal injection, but not in rat tissues when <strong>DDVP</strong> was given by inhalation.<br />

Reproductive Toxicity- Exposure of rats to <strong>DDVP</strong> in the water during reproduction resulted in the<br />

inhibition of plasma, erythrocyte, and brain ChE. Clinical signs were observed in both parents and<br />

offsprings. Other toxicity included decreased body weights and decreased water consumption. Remating<br />

of the F 1 females after the F 2 generation showed that decreased estrous cycling and increased<br />

incidence of abnormal estrus cycling. Mice exposed to <strong>DDVP</strong>-containing resin strips showed only<br />

plasma ChE depression and no effect on reproduction.<br />

Developmental Toxicity- <strong>DDVP</strong>, given by oral or inhalation routes, was not teratogenic in rats, mice,<br />

or rabbits. Cholinergic signs (tremors, ataxia, diarrhea, and other effects) were observed in the<br />

pregnant rats and rabbits.<br />

Neurotoxicity- Possible adverse effects of nerve fiber degeneration and spinal cord degeneration<br />

were observed in chickens treated with <strong>DDVP</strong>. No acute delayed neurotoxicity in hens was reported,<br />

except at lethal doses. Acute neurotoxicity study in the rat given <strong>DDVP</strong> by gavage resulted in<br />

cholinergic effects which included gait alteration, constricted pupils, tremors, and salivation.<br />

RISK ASSESSMENT<br />

Hazard Identification- The no-observed-effects levels (NOELs) from both inhalation and oral studies,<br />

and oncogenic risk from an oral study were used to evaluate the health hazards from potential<br />

exposure by workers and the general population to <strong>DDVP</strong>. For non-oncogenic endpoints, acute and<br />

chronic inhalation and dietary exposures were considered. For oncogenic endpoints, inhalation and<br />

dietary exposures to <strong>DDVP</strong> were assessed.<br />

For acute inhalation exposure, the definitive NOEL was 1.25 ug/L or 0.65 mg/kg-day (NOEL adjusted<br />

for exposure duration and respiration rate). The NOEL was based on death in pregnant rabbits after 2<br />

days of inhalation exposure to a LOEL of 2 ug/L <strong>DDVP</strong>.<br />

The NOEL for acute oral exposure was 0.5 mg/kg-day based on tremors, salivation, neuromuscular<br />

deficits, and other cholinergic signs observed in rats within 1 day after a single dose by gavage.<br />

The NOELs for chronic toxicity were based on the inhibition of brain ChE activity in a one-year dog<br />

oral study and a two-year rat inhalation study. The adjusted NOELs for inhalation and oral routes<br />

were 0.025 mg/kg-day, and 0.05 mg/kg-day, respectively.<br />

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