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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
Fields
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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1 <br /> 77X`TOXNET PIP - AZINOPHOS-METHYL Page 3 of 4 <br /> methyl is 136 mg/kg in young mallards, 74.9 mg/kg in young pheasant, 84.2 mg/kg in young chukar <br /> partridges, 262.0 mg/kg in chickens, and 32.2 mg/kg in bobwhite quail [13,17,27]. The dietary LC50 for <br /> azinphos-methyl is 639 ppm in Japanese quail, 1821 ppm in ring necked pheasant, and 1940 ppm in mallard <br /> duck [13,17]. <br /> . Effects on aquatic organisms: Azinphos-methyl is moderately to very highly toxic to freshwater fish. For most <br /> species,the LC50 values are less than 1 mg/L. The 96-hour LC50 for azinphos-methyl in rainbow trout is <br /> 0.003 mg/L [8,13]. Guthion-poisoned fish exhibit central nervous system impairment, including erratic <br /> swizi-iming accompanied by uncontrolled convulsions. Rapid gill movements, paralysis, and death follow in <br /> rapid succession [8]. Azinphos-methyl is highly toxic to aquatic invertebrates, shellfish, frogs, and toads [8]. <br /> The LC50 values are below 1 ug/L for many of the species [8,17]. <br /> . Effects on other organisms: Several studies have indicated that azinphos-methyl causes adverse effects in <br /> wildlife. Wild mammals and aquatic organisms appear to be more vulnerable than birds to hazards created by <br /> this material [29]. The EPA requires endangered species labeling for certain azinphos-methyl uses [17]. <br /> + Azinphos-methyl is toxic to honeybees and other beneficial insects [8,24]. It will cause severe bee losses if <br /> used when bees are present at treatment time or within a day thereafter [30]. A 90%mortality rate is seen in <br /> ! pollinating leaf cutting bees after a 9-day exposure to greenhouse alfalfa treated with azinphos-methyl [27]. <br /> Environfnental-'Fate: <br /> . Breakd6wn'in'soil and groundwater. Persistence of azinphos-methyl in soil is quite variable but is generally <br /> low under field conditions [19,31]. The half-life in sandy loam soil is 5 days. Its half-life in nonsterile soil is <br /> 21 days when oxygen is present or 68 days under oxygen-free conditions. In sterile soil, the half-life is <br /> reported to be 355 days. Azinphos-methyl is fairly immobile in soil because it adsorbs strongly to soil <br /> particles and has low water solubility. It has low leaching potential and is unlikely to contaminate <br /> groundwater [19,31]. It was not detected in 54 groundwater samples collected in New York state [32]. <br /> Azinphos-methyl is one of 118 synthetic organic chemicals that the state of Florida has designated for <br /> groundwater monitoring [33]. It was detected in only 5 out of 1628 wells sampled in 10 states from 1983 to <br /> 1991 [34]. The disappearance of azinphos-methyl from soil is more rapid in the surface layers (0 2.5 <br /> centimeters deep) than it is in the next deeper layer (2.4 to 7.5 cm). Biodegradation and evaporation are the <br /> primary routes of disappearance for azinphos-methyl. Azinphos-methyl is also subject to degradation by <br /> ultraviolet (UV) light from the sun and hydrolytic decomposition. Photodecomposrtion is particularly rapid at <br /> high levels of soil moisture and in the presence of UV light [31]. Rapid degradation of Gusathion was <br /> observed at temperatures higher than 37 C [29]. <br /> . Breakdown in water: In general, organophosphates, such as azinphos-methyl, are dissipated rapidly in water <br /> [35]. In pond water, it is subject to degradation by sunlight and microorganisms, with a half-life of up to 2 <br /> days. Volatilization from water is unlikely. Chemical hydrolysis is important in alkaline waters [12]. <br /> Azinphos-methyl is very stable in water below pH 10.0. Above pH 11.0, it is rapidly hydrolyzed to anthranilic <br /> acid, benzamide, and other metabolites. Azinphos-methyl has a low to medium tendency to adsorb to <br /> f sediments or suspended solids [12]. <br /> . Breakdown in vegetation: Residue levels of azinphos-methyl in crops are dependent on the rate and <br /> frequency of application, nature of the plant surface, and weather conditions such as rainfall, temperature, <br /> sunlight, humidity, and wind [24]. The half-life on vegetable and forage crops is 3 to 5 days under field <br /> conditions [24]. It gives effective protection for 2 or more weeks [36]. On treated apple trees, the half-life of <br /> ' this pesticide was about 2.6 to 6.3 days [28]. Hawthorn and American Linden trees have been injured by this <br /> material. It has also caused russeting on certain varieties of fruit [24]. <br /> Ph sical Pro ernes: <br /> . Appearance: Pure azinphos-methyl is a white crystalline solid. Technical azinphos-methyl is a brown waxy <br /> solid [13,37]. <br /> . Chemical Name: S-(3,4-dihydro-4-oxobenzo[d]-[1,2,3]-triazin-3-ylmethyl) 0,0-dimethyl phosphordithioate <br /> [13] <br /> . CAS Number: 86-50-0 <br /> . Molecular Weight: 317.33 <br /> . Water Solubility: 30 mg/L @ 25 C [13] <br /> . Solubility in Other Solvents: dichloromethane v.s.; toluene v.s. [13] <br /> . Melting Point: 65-68 C (technical) [13]; 73-74 C (pure form) [13] <br /> . Vapor Pressure: <1 mPa @ 20 C [13] <br />
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