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EXTOXNET PIP - CHLORPYRIFOS Page 3 of 4 <br /> 0.304 ppm [2]. In a rat study, chlorpyrifos did not accumulate in any tissue except fat [49]. <br /> Ecological Effects: <br /> • Effects on birds: Chlorpyrifos is moderately to very highly toxic to birds [43]. Its oral LD50 is 8.41 mg/kg in <br /> pheasants, 112 mg/kg in mallard ducks, 21.0 mg/kg in house sparrows, and 32 mg/kg in chickens [8,13,43]. The <br /> LD50 for a granular product(15G) in bobwhite quail is 108 mg/kg [13,43]. At 125 ppm, mallards laid significantly <br /> fewer eggs [43]. There was no evidence of changes in weight gain, or in the number,weight, and quality of eggs <br /> produced by hens fed dietary levels of 50 ppm of chlorpyrifos [8]. <br /> • Effects on aquatic organisms: Chlorpyrifos is very highly toxic to freshwater fish, aquatic invertebrates and <br /> estuarine and marine organisms [43]. Cholinesterase inhibition was observed in acute toxicity tests of fish exposed <br /> to very low concentrations of this insecticide. Application of concentrations as low as 0.01 pounds of active <br /> ingredient per acre may cause fish and aquatic invertebrate deaths [43]. Chlorpyrifos toxicity to fish may be related <br /> to water temperature. The 96-hour LC50 for chlorpyrifos is 0.009 mg/L in mature rainbow trout, 0.098 mg/L in lake <br /> trout, 0.806 mg/L in goldfish, 0.01 mg/L in bluegill, and 0.331 mg/L in fathead minnow [50]. When fathead <br /> minnows were exposed to Dursban for a 200-day period during which they reproduced,the first generation of <br /> offspring had decreased survival and growth, as well as a significant number of deformities. This occurred at <br /> approximately 0.002 mg/L exposure for a 30-day period [8]. Chlorpyrifos accumulates in the tissues of aquatic <br /> organisms. Studies involving continuous exposure of fish during the embryonic through fry stages have shown <br /> bioconcentration values of 58 to 5100 [51]. Due to its high acute toxicity and its persistence in sediments, <br /> chlorpyrifos may represent a hazard to sea bottom dwellers [52]. Smaller organisms appear to be more sensitive <br /> than larger ones [50]. <br /> • Effects on other organisms: Aquatic and general agricultural uses of chlorpyrifos pose a serious hazard to wildlife <br /> and honeybees [13,48]. <br /> Environmental Fate: <br /> • Breakdown in soil and groundwater: Chlorpyrifos is moderately persistent in soils. The half-life of chlorpyrifos <br /> in soil is usually between 60 and 120 days,but can range from 2 weeks to over 1 year, depending on the soil type, <br /> climate, and other conditions [12,19]. The soil half-life of chlorpyrifos was from 11 to 141 days in seven soils <br /> ranging in texture from loamy sand to clay and with soil pHs from 5.4 to 7.4. Chlorpyrifos was less persistent in the <br /> soils with a higher pH [51]. Soil half-life was not affected by soil texture or organic matter content. In anaerobic <br /> soils,the half-life was 15 days in loam and 58 days in clay soil [43]. Adsorbed chlorpyrifos is subject to degradation <br /> by UV light, chemical hydrolysis and by soil microbes. When applied to moist soils, the volatility half-life of <br /> chlorpyrifos was 45 to 163 hours, with 62 to 89% of the applied chlorpyrifos remaining on the soil after 36 hours <br /> [51]. In another study, 2.6 and 9.3% of the chlorpyrifos applied to sand or silt loam soil remained after 30 days [51]. <br /> Chlorpyrifos adsorbs strongly to soil particles and it is not readily soluble in water [19,51]. It is therefore immobile <br /> in soils and unlikely to leach or to contaminate groundwater [51]. TCP, the principal metabolite of chlorpyrifos, <br /> adsorbs weakly to soil particles and appears to be moderately mobile and persistent in soils[43]. <br /> • Breakdown in water: The concentration and persistence of chlorpyrifos in water will vary depending on the type <br /> of formulation. For example, a large increase in chlorpyrifos concentrations occurs when emulsifiable <br /> concentrations and wettable powders are released into water. As the pesticide adheres to sediments and suspended <br /> organic matter, concentrations rapidly decline. The increase in the concentration of insecticide is not as rapid for <br /> granules and controlled release formulations in the water,but the resulting concentration persists longer[50]. <br /> Volatilization is probably the primary route of loss of chlorpyrifos from water. Volatility half-lives of 3.5 and 20 <br /> days have been estimated for pond water [51]. The photolysis half-life of chlorpyrifos is 3 to 4 weeks during <br /> midsummer in the U.S. Its change into other natural forms is slow [52]. Research suggests that this insecticide is <br /> unstable in water, and the rate at which it is hydrolyzed increases with temperature, decreasing by 2.5- to 3-fold <br /> with each 10 C drop in temperature. The rate of hydrolysis is constant in acidic to neutral waters,but increases in <br /> alkaline waters. In water at pH 7.0 and 25 C, it had a half-life of 35 to 78 days [12]. <br /> http://extoxnet.orst.edu/pips/chlorpyr.htm ✓ 3/13/200( <br />