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SU0003862 SSCRPT
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SU0003862 SSCRPT
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Last modified
5/7/2020 11:30:10 AM
Creation date
9/5/2019 11:15:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0003862
PE
2622
FACILITY_NAME
PA-0300662
STREET_NUMBER
17263
Direction
S
STREET_NAME
HENRY
STREET_TYPE
RD
City
ESCALON
ENTERED_DATE
5/11/2004 12:00:00 AM
SITE_LOCATION
17263 S HENRY RD
RECEIVED_DATE
12/30/2003 12:00:00 AM
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\H\HENRY\17263\PA-0300662\SU0003862\SSC RPT.PDF
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EHD - Public
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f <br /> I <br /> what would be encountered with a very sandy soil. The second source of information can be found on <br /> k <br /> USGmaps. The property is located on the Escalon Quadrangle map, found in the Appendix. <br /> Noted on the Environmental Questionnaire, is the response to the issue of agrichemicals applied to <br /> the trees. No agrichemicals, especially pesticides have been applied since Mr. Schimmel has <br /> owned the property. Therefore, an evaluation of environmental fate data for applied agrichemical <br /> residues as a nonpoint source of potential contamination was not done. <br /> The science of pesticide residues in soil, air, surface water and groundwater is extremely complex <br /> and variable. Environmental models that attempt to predict pesticide behavior and transport in the <br /> environment are beyond the scope of this investigation. However,pesticides with long half-lives <br /> that may have been used or drifted onto the property decades ago, primarily DDT, may be of a slight <br /> j concern. DDT was used extensively throughout the agricultural fields of the San Joaquin Valley and <br /> degradates of DDT can be found in nearly all these soils. Previous Exposure Assessments made on <br /> typical San Joaquin Valley soils suggest an extremely low probability of adverse health effects from <br /> soil DDT/DDD and DDE concentrations (if the concentrations even exist). <br /> It can be reasonably concluded that any DDT, DDE and DDD concentrations will continue to <br /> � degrade as reported in the published environmental fate data. The environmental fate data for DDT <br /> and its degradates DDD and DDE are illustrated below: <br /> DDT. Common name: Agritan, Anofex, Azotox, et al. <br /> Half-lives in the environment: <br /> Air: 17.7 -177 h. <br /> Surface water: 73.9 h for a pond 1 in deep. Degradation half-life of about 10 yr- <br /> average from loss rates determined in Lake Michigan. <br /> Groundwater: 16 d to 31.3 yr. <br /> ' Sediment: 3 to 5 yr <br /> Soil: 2-15.6 yrs based on observed rates of biodegradation in aerobic soils under field <br /> conditions. Avg. half life of-12 yrs in 3 different soils for 50 ppm in soil. <br /> (conversion of p,p'-DDT to p,p'-DDE). <br /> Environmental Fate Rate Constants or Half-Lives: <br /> Volatilization: Half-life of 3.7 d for water depth of 1 in, from soil w/h-1 of 578 h <br /> Oxidation: Photooxidation half-life of 168-8400 h in water, 17.7-177 h in air <br /> Hydrolysis: Estimated first-order half life of 22 yr <br /> Biodegradation: Aqueous aerobic half-life of 2-15.6 yrs <br /> DDE. Common name: DDE (p,p'-DDE; o,p'-DDE),product of DDT degradation. <br /> Half-lives in the environment: <br /> Air: Atmos. transformation lifetime est. to be < 1 d. <br /> Surface water: Hydrolytic half-life of >120 yr, est. half-life >300 d in lakes. <br /> Groundwater: NIA <br /> Sediment: NIA <br /> Soil: Field half life of 1000 d <br /> Biota: Elimination half-life of 340 d (rainbow trout), 300 d for birds. <br /> Environmental Fate Rate Constants or Half-Lives: <br /> Volatilization: NIA, Oxidation: N/A, Hydrolysis: >120 yr,Biodegradation: NIA <br /> Page -4- <br /> Chesney Consulting <br />
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