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SU0003944 SSCRPT
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SU0003944 SSCRPT
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Last modified
5/7/2020 11:30:22 AM
Creation date
9/4/2019 10:18:08 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0003944
PE
2611
FACILITY_NAME
PA-0400228
STREET_NUMBER
7770
Direction
W
STREET_NAME
BATES
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
24809009
ENTERED_DATE
5/11/2004 12:00:00 AM
SITE_LOCATION
7770 W BATES RD
RECEIVED_DATE
5/10/2004 12:00:00 AM
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\B\BATES\7770\PA-0400228\SU0003944\SSC RPT.PDF
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EHD - Public
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EXfiOXNET PIP - CHLORPYRIFOS Page 3 of 4 <br /> 4 „ active ingredient per acre may cause fish and aquatic invertebrate deaths [43]. Chlorpyrifos toxicity to fish <br /> may be related to water temperature. The 96-hour LC50 for chlorpyrifos is 0.009 mg/L in mature rainbow <br /> trout, 0.098 mg/L in lake trout, 0.806 mg/L in goldfish, 0.01 mg/L in bluegill, and 0.331 mg/L in fathead <br /> minnow [50]. When fathead minnows were exposed to Dursban for a 200-day period during which they <br /> reproduced, the first generation of offspring had decreased survival and growth, as well as a significant <br /> number of deformities. This occurred at approximately 0.002 mg/L exposure fora 30-day period [8]. <br /> Chlorpyrifos accumulates in the tissues of aquatic organisms. Studies involving continuous exposure of fish <br /> during the embryonic through fry stages have shown bioconcentration values of 58 to 5100 [51]. Due to its <br /> high acute toxicity and its persistence in sediments, chlorpyrifos may represent a hazard to sea bottom <br /> dwellers [52]. Smaller organisms appear to be more sensitive than larger ones [50]. <br /> . Effects on other organisms: Aquatic and general agricultural uses of chlorpyrifos pose a serious hazard to <br />' wildlife and honeybees [13,48]. <br /> N <br /> t Environmental Fate: <br /> . Breakdown in soil and groundwater: Chlorpyrifos is moderately persistent in soils. The half-life of <br /> chlorpyrifos in soil is usually between 60 and 120 days, but can range from 2 weeks to over 1 year, depending <br /> on the soil type, climate, and other conditions [12,19]. The soil half-life of chlorpyrifos was from 11 to 141 <br /> days in seven soils ranging in texture from loamy sand to clay and with soil pHs from 5.4 to 7.4. Chlorpyrifos <br /> was less persistent in the soils with a higher pH [51]. Soil half-life was not affected by soil texture or organic <br /> matter content. In anaerobic soils, the half-life was 15 days in loam and 58 days in clay soil [43]. Adsorbed <br /> chlorpyrifos is subject to degradation by UV light, chemical hydrolysis and by soil microbes. When applied to <br /> moist soils, the volatility half-life of chlorpyrifos was 45 to 163 hours, with 62 to 89% of the applied <br /> chlorpyrifos remaining on the soil after 36 hours [51]. In another study, 2.6 and 9.3% of the chlorpyrifos <br /> applied to sand or silt loam soil remained after 30 days [51]. Chlorpyrifos adsorbs strongly to soil particles <br /> and it is not readily soluble in water [19,51]. It is therefore immobile in soils and unlikely to leach or to <br /> contaminate groundwater [51]. TCP,the principal metabolite of chlorpyrifos, adsorbs weakly to soil particles <br /> 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 <br /> type 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 <br /> suspended organic matter, concentrations rapidly decline. The increase in the concentration of insecticide is <br /> not as rapid for granules and controlled release formulations in the water, but the resulting concentration <br /> r persists longer [50]. Volatilization is probably the primary route of loss of chlorpyrifos from water. Volatility <br /> half-lives of 3.5 and 20 days have been estimated for pond water [51]. The photolysis half-life of chlorpyrifos <br /> is 3 to 4 weeks during midsummer in the U.S. Its change into other natural forms is slow [52]. Research <br /> suggests that this insecticide is unstable in water, and the rate at which it is hydrolyzed increases with <br /> temperature, decreasing by 2.5-to 3-fold with'each 10 C drop in temperature. The rate of hydrolysis is <br /> constant in acidic to neutral waters, but increases in alkaline waters. In water at pH 7.0 and 25 C, it had a half- <br /> life of 35 to 78 days [12]. <br /> Breakdown in vegetation: Chlorpyrifos may be toxic to some plants, such as lettuce [36]. Residues remain <br /> on plant surfaces for approximately 10 to 14 days. Data indicate that this insecticide and its soil metabolites <br /> can accumulate in certain crops [8]. <br /> Physical Properties: <br /> . Appearance: Technical chlorpyrifos is an amber to white crystalline solid with a mild sulfur odor [13]. <br /> _ to <br /> . Chemical Name. 0,0-diethyl 0-3,5,6 tnchloro-2-pyndyl phospharothioa [13 <br /> ] <br /> I . CAS Number: 2921-88-2 <br /> . Molecular Weight: 350.62 <br /> . Water Solubility: 2 mg/L @ 25 C [13] <br /> . Solubility in Other Solvents: benzene s.; acetone s.; chloroform s.; carbon disulfide s.; diethyl ether s.; <br /> xylene s.; methylene chloride s.; methanol s. [13] <br /> Melting Point: 41.5-44 C [13] <br /> . Vapor Pressure: 2.5 mPa @ 25 C [13] <br /> . Partition Coefficient: 4.6990 [13] <br /> . Adsorption Coefficient: 6070 [19] <br /> Exposure Guidelines: <br />
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