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SU0006490_SSCRPT
Environmental Health - Public
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EHD Program Facility Records by Street Name
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120 (STATE ROUTE 120)
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2600 - Land Use Program
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PA-0700108
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SU0006490_SSCRPT
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Last modified
11/19/2024 3:59:59 PM
Creation date
9/8/2019 12:32:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0006490
PE
2622
FACILITY_NAME
PA-0700108
STREET_NUMBER
10800
Direction
E
STREET_NAME
STATE ROUTE 120
City
MANTECA
APN
22803024
ENTERED_DATE
3/27/2007 12:00:00 AM
SITE_LOCATION
10800 E HWY 120
RECEIVED_DATE
3/27/2007 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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\MIGRATIONS\O\HWY 120\10800\PA-0700108\SU0006490\SSC RPT.PDF
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EHD - Public
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EXTOXNET PIP - DDT Page 5 of 6 <br /> . Breakdown in Soil and Groundwater: DDT is very highly persistent in the environment, with a reported half life <br /> of between 2-15 years (83, 84) and is immobile in most soils. Routes of loss and degradation include runoff, <br /> volatilization,photolysis and biodegradation (aerobic and anaerobic) (73). These processes generally occur only <br /> very slowly. Breakdown products in the soil environment are DDE and DDD, which are also highly persistent and <br /> have similar chemical and physical properties (82, 84). Due to its extremely low solubility in water, DDT will be <br /> retained to a greater degree by soils and soil fractions with higher proportions of soil organic matter(82). It may <br /> accumulate in the top soil layer in situations where heavy applications are(or were) made annually; e.g., for apples <br /> (72). Generally DDT is tightly sorbed by soil organic matter,but it(along with its metabolites)has been detected in <br /> many locations in soil and groundwater where it may be available to organisms (82, 83). This is probably due to its <br /> high persistence; although it is immobile or only very slightly mobile, over very long periods of time it may be able <br /> to eventually leach into groundwater, especially in soils with little soil organic matter. Residues at the surface of the <br /> soil are much more likely to be broken down or otherwise dissipated than those below several inches (3). Studies in <br /> Arizona have shown that volatilization losses may be significant and rapid in soils with very low organic matter <br /> content (desert soils) and high irradiance of sunlight,with volatilization losses reported as high as 50% in 5 months <br /> (85). In other soils (Hood River and Medford) this rate may be as low as 17-18% over 5 years (85). Volatilization <br /> loss will vary with the amount of DDT applied, proportion of soil organic matter, proximity to soil-air interface and <br /> the amount of sunlight (82). <br /> . Breakdown of Chemical in Surface Water: DDT may reach surface waters primarily by runoff, atmospheric <br /> transport, drift, or by direct application (e.g. to control mosquito-borne malaria) (73). The reported half-life for <br /> DDT in the water environment is 56 days in lake water and approximately 28 days in river water(83). The main <br /> pathways for loss are volatilization, photodegradation, adsorption to water-borne particulates and sedimentation <br /> (73) Aquatic organisms, as noted above, also readily take up and store DDT and its metabolites. Field and <br /> laboratory studies in the United Kingdom demonstrated that very little breakdown of DDT occurred in estuary <br /> sediments over the course of 46 days (82). DDT has been widely detected in ambient surface water sampling in the <br /> United States at a median level of 1 ng/L (part per trillion) (73, 76). <br /> . Breakdown of Chemical in Vegetation: DDT does not appear to be taken up or stored by plants to a great extent. <br /> It was not translocated into alfalfa or soybean plants, and only trace amounts of DDT or its metabolites were <br /> observed in carrots,radishes and turnips all grown in DDT-treated soils (82). Some accumulation was reported in <br /> grain, maize and riceplants,but little translocation occured and residues were located primarily in the roots (73). <br /> PHYSICAL PROPERTIES AND GUIDELINES <br /> Physical Properties: <br /> . Appearance: The physical appearance of technical product p,pO-DDT is a waxy solid, although in its pure form it <br /> consists of colorless crystals (79) <br /> . Chemical Name: 1,1'-(2,2,2-trichloroethylidene)bis[4-chlorobenzene]; 1,1,1-trichloro-2,2-bis(4-chlorophenyl) <br /> ethane (79) <br /> . CAS Number: 50-29-3 (79) <br /> . Molecular Weight: 354.51 (79) <br /> . Water Solubility: < 1 mg/L @ 20 degrees C (79) <br /> . Solubility in Other Solvents: cyclohexanone v.s., dioxane v.s.,benzene v.s., xylene v.s., trichloroethylene v.s., <br /> dichloromethane v.s., acetone v.s., chloroform v.s., diethyl ether v.s., ethanol s. and methanol s. (79). <br /> . Melting Point: 108.5-109 degrees C (79) <br /> . Vapor Pressure: 0.025 mPa @ 25 degrees C (79) <br /> . Partition Coefficient: Not available <br /> . Adsorption Coefficient: 100,000 (84) <br /> Exposure Guidelines: <br /> . ADI: 0.02 mg/kg/d (73) <br /> http://extoxnet.orst.edu/pips/ddt.htm 3/7/200' <br />
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