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SU0007337_SSCRPT
Environmental Health - Public
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2600 - Land Use Program
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PA-0800244
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SU0007337_SSCRPT
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Last modified
11/19/2024 3:46:25 PM
Creation date
9/9/2019 10:28:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0007337
PE
2622
FACILITY_NAME
PA-0800244
STREET_NUMBER
9855
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240
APN
02508001
ENTERED_DATE
8/18/2008 12:00:00 AM
SITE_LOCATION
9855 W HWY 12
RECEIVED_DATE
8/18/2008 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\T\HWY 12\9855\PA-0800244\SU0007337\SSC RPT.PDF
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EHD - Public
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:TOXNET PIP-LAMBDA CYHALOTHRIN Page 3 of 4 <br /> population),for the eastern oyster of 0.59 ng/L has been reported (107). Bioconcentration is possible in aquatic <br /> species,but bioaccumulation is not likely. Bioconcentration in channel catfish has been reported as minimal, <br /> with rapid depuration(elimination) (111). A bioconcentration factor of 858 has been reported in fish(4, species <br /> unspecified),but concentration was confined to non-edible tissues and rapid depuration was observed (107). <br /> . Effects on Other Animals (Nontarget species): Lambda cyhalothrin is highly toxic to bees, with a reported oral <br /> LD50 of 38 ng/bee and reported contact LD50 of 909 ng/bee (0.9 ug/bee) (107). <br /> NVIRONMENTAL FATE <br /> reakdown of Chemical in Soil and Groundwater: Lambda cyhalothrin is moderately persistent in the soil <br /> ivironment. Reported field half-lives range from four to 12 weeks (107, 111, 112). Its field half-life is probably close <br /> 30 days in most soils (112). It shows a high affinity for soil;the reported Koc is 180,000 (112)..Lambda cyhalothrin <br /> not expected to be appreciably mobile in most soils. There is little potential for groundwater contamination. Soils <br /> ith high sand content or with very low organic matter content may tend to retain the compound to a lesser degree. In <br /> eld studies of Karate, leaching of lambda cyhalothrin and its degradates from the soil were minimal (12, 107). <br /> reakdown products formed in the soil environment are similar to those formed in mammalian systems, via the <br /> ydrolysis of the central ester bond and oxidation(12). Breakdown rates of both the technical product and Karate were <br /> milar under aerobic and anaerobic conditions (107, 111). <br />,reakdown of Chemical in Surface Water: Lambda cyhalothrin has extremely low water solubility and is tightly <br /> ound to soil,it is therefore not expected to be prevalent in surface waters. One possible source of infiltration into <br />.uface waters would be surface runoff. In this event,the compound would most probably remain bound to the solid <br /> article and settle to the bottom. <br /> reakdown of Chemical in Vegetation: No data were available regarding the breakdown of lambda cyhalothrin in <br /> egetation. <br />'HYSICAL PROPERTIES AND GUIDELINES <br />'hysical Properties: <br /> • Appearance: Lambda cyhalothrin is a colorless solid at room temperature, but may appear yellowish in solution. <br /> • Chemical Name: (RS)-alpha-cyano-3-phenoxybenzyl 3-(2-chloro-3,3,3-trifluoropropenyl)-2,2,- <br /> dimethylcyclopropanecarboxylate (12) <br /> • CAS Number: 91465-08-6 (12) <br /> • Molecular Weight: 449.9 (12) <br /> • Water Solubility: 0.005 mg/L @ pH 6.5 and 20 degrees C(12) <br /> • Solubility in Other Solvents: acetone v.s, methanol v.s.,toluene v.s., hexane v.s. (12) <br /> • Melting Point: 49.2 degrees C (12) <br /> • Vapor Pressure: negligible at 20 degrees C (12) <br /> • Partition Coefficient:10,000,000 (12) <br /> • Adsorption Coefficient: 180, 000 (112) <br /> Exposure Guidelines: <br /> • ADI: Not Available <br /> • MCL:Not Available <br /> • P.M: 0.005 mg/kg/day (106) <br /> • PEL: Not Available <br /> • HA:Not Available <br /> • TLV:Not Available <br /> BASIC MANUFACTURER <br />
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