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EXTOXNET PIP - IMIDACLOPRID Page 2 of 4 <br /> ,*.e %000 <br /> (223), and 131 mg/kg in mice (1). The 24-hour dermal LD50 in rats is >5,000 mg/kg. It is <br /> considered non-irritating to eyes and skin (rabbits), and non-sensitizing to skin (guinea pigs) (1). <br /> Some granular formulations may contain clays as inert ingredients that may act as eye irritants. In <br /> acute inhalation toxicity tests with rats, the airborne concentration of imidacloprid that resulted in <br /> mortality to half of the test organisms (LC50) is> 69 mg/meters cubed air in the form of an <br /> aerosol, and>5323 mg/meters cubed air in the form of dust. These values represent the maximum <br /> attainable airborne concentrations (1). <br /> • Signs and Symptoms of Poisoning: Although no account of human poisoning was found in the <br /> literature, signs and symptoms of poisoning would be expected to be similar to nicotinic signs and <br /> symptoms, including fatigue, twitching, cramps, and muscle weakness including the muscles <br /> necessary for breathing (330). <br /> • Chronic Toxicity: A 2-year feeding study in rats fed up to 1,800 ppm resulted in a No <br /> Observable Effect Level (NOEL) of 100 ppm (5.7 mg/kg body weight in males and 7.6 mg/kg in <br /> females). Adverse effects included decreased body weight gain in females at 300 ppm, and <br /> increased thyroid lesions in males at 300 ppm and females at 900 ppm. A 1-year feeding study in <br /> dogs fed up to 2,500 ppm resulted in a NOEL of 1,250 ppm (41 mg/kg). Adverse effects included <br /> increased cholesterol levels in the blood, and some stress to the liver(measured by elevated liver <br /> cytochrome p-450 levels) (331). <br /> • Reproductive Effects: A three generation reproduction study in rats fed up to 700 ppm <br /> imidacloprid resulted in a NOEL of 100 ppm (equivalent to 8 mg/kg/day) based on decreased pup <br /> body weight observed at the 250 ppm dose level (331). <br /> • Teratogenic Effects: A developmental toxicity study in rats given doses up to 100 ppm by <br /> gavage on days 6 to 16 of gestation resulted in a NOEL of 30 mg/kg/day (based on skeletal <br /> abnormalities observed at the next highest dose tested of 100 ppm) (329). In a developmental <br /> toxicity study with rabbits given doses of imidacloprid by gavage during days 6 through 19 of <br /> gestation, resulted in a NOEL of 24 mg/kg/day based on decreased body weight and skeletal <br /> abnormalities observed at 72 mg/kg/day (highest dose tested) (331). <br /> • Mutagenic Effects: Imidacloprid may be weakly mutagenic. In a battery of 23 laboratory <br /> mutagenicity assays, imidacloprid tested negative for mutagenic effects in all but two of the <br /> assays. It did test positive for causing changes in chromosomes in human lymphocytes, as well as <br /> testing positive for genotoxicity in Chinese hamster ovary cells (331). <br /> • Carcinogenic Effects: Imidacloprid is considered to be of minimal carcinogenic risk, and is thus <br /> categorized by EPA as a "Group E" carcinogen (evidence of noncarcinogenicity for humans). <br /> There were no carcinogenic effects in a 2-year carcinogenicity study in rats fed up to 1,800 ppm <br /> imidacloprid (328). <br /> • Organ Toxicity: In short-term feeding studies in rats, there were thyroid lesions associated with <br /> very high doses of imidacloprid (331). <br /> • Fate in Humans and Animals: Imidacloprid is quickly and almost completely absorbed from the <br /> gastrointestinal tract, and eliminated via urine and feces (70-80% and 20-30%, respectively, of the <br /> 96% of the parent compound administered within 48 hours). The most important metabolic steps <br /> include the degradation to 6-chloronicotinic acid, a compound that acts on the nervous system as <br /> described above. This compound may be conjugated with glycine and eliminated, or reduced to <br /> guanidine (1). <br /> ECOLOGICAL EFFECTS <br /> • Effects on Birds: Imidacloprid is toxic to upland game birds. The LD50 is 152 mg/kg for <br /> bobwhite quail, and 31 mg/kg in Japanese quail (223, 1). In studies with red-winged blackbirds <br /> and brown-headed cowbirds, it was observed that birds learned to avoid imidacloprid treated seeds <br /> after experiencing transitory gastrointestinal distress (retching) and ataxia(loss of coordination). It <br /> was concluded that the risk of dietary exposure to birds via treated seeds was minimal. Based on <br /> http://extoxnet.orst.edu/pips/imidaclo.htm 11/22/2004 <br />