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SU0006490_SSCRPT
EnvironmentalHealth
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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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SJGOV\rtan
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FilePath
\MIGRATIONS\O\HWY 120\10800\PA-0700108\SU0006490\SSC RPT.PDF
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EHD - Public
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NOW <br /> § 3.4 Description of all past off-site potential and/or known above and below ground sources of <br /> contamination identified in the area of the project site that has or may impact the project <br /> site includes: Information conveyed by the March 8, 2007 Envisions Program Documents <br /> illustrating no listings on or in proximity to the subject property. The closest Leaking <br /> Underground Storage Tank is on Yosemite Boulevard, 2000 feet to the west,which can be <br /> considered crossgradient to the subject property. In addition, the Envisions Program <br /> Documents show that Mr. Davis has an Underground Storage Tank at his main RV sales <br /> facility approximately one-fourth mile to the west from the property on Yosemite <br /> Boulevard. This can also be considered crossgradient to the property. These tanks and any <br /> leaking contents could not affect the property due to the distances involved. <br /> Agricultural spray drift (non-target) from the nearest agricultural production land affecting <br /> the property could be a possibility, since agricultural production still occurs to the east and <br /> to the south. The region has been, and continues to be intensely farmed, so nitrate <br /> contamination to the underlying groundwater from nitrogen fertilization is always a <br /> possibility. <br /> The science of pesticide residues in soil, air, surface water and groundwater is extremely <br /> complex and variable. Environmental models that attempt to predict pesticide behavior and <br /> transport in the environment are beyond the scope of this investigation. <br /> Pesticides with long half-lives that may have been used or drifted onto the property decades <br /> ago,primarily DDT, may be of an extremely slight concern. DDT was used extensively / <br /> throughout the agricultural fields of the San Joaquin Valley and degradates of DDT can be <br /> found in nearly all these soils. Previous Exposure Assessments made on typical San Joaquin <br /> Valley soils suggest an extremely low probability of adverse health effects from soil <br /> DDT/DDD and DDE concentrations (if the concentrations even exist). The environmental <br /> fate data are presented below for DDT, and its degradates DDD and DDE. <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-average from loss <br /> 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 conditions. <br /> Avg.half life of-12 yrs in 3 different soils for -50 ppm in soil.(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 m,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 /> Page -5- <br /> Chesney Consulting <br />
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