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SU0007737 SSCRPT
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SU0007737 SSCRPT
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Last modified
5/7/2020 11:33:13 AM
Creation date
9/6/2019 10:21:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0007737
PE
2622
FACILITY_NAME
PA-0900124
STREET_NUMBER
10549
Direction
N
STREET_NAME
JACK TONE
STREET_TYPE
RD
City
LODI
APN
06321022, 23
ENTERED_DATE
5/22/2009 12:00:00 AM
SITE_LOCATION
10549 N JACK TONE RD
RECEIVED_DATE
5/22/2009 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\J\JACK TONE\10549\PA-0900124\SU0007737\SSC RPT.PDF
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EHD - Public
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F <br /> ources of current observable above-ground contamination exist to the soil from the two <br /> e-ground fuel storage tanks or from the waste oil storage tank. Subsurface <br /> amination may be possible from the referenced agricultural nitrogen fertilization <br /> ces. The on-site septic tank/leachfields and surrounding leachfields may be considered <br /> ave a very slight impact due to sparse density. The referenced electrical transformers <br /> adjacent to the west property border, as illustrated in the attached photographs, probably do <br /> not contain polychloride biphenyls (PCBs) based upon their age. If there was a leak or <br /> explosion, it would be the responsibility of the transformer owner to mitigate <br /> contamination. <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 could impact the project site <br /> includes: <br /> Information conveyed by the February 9, 2006 Envisions Program Documents illustrates no <br /> listings on, or in proximity to the subject property. The two closest Leaking Underground <br /> Fuel Tanks (LUFTs) are approximately 1.5 miles to the north of the property based upon <br /> the Geotracker data. The distances involved make it virtually impossible for these sites to <br /> impact the subject property, and two of the cases have been closed. <br /> Agricultural spray drift (non-target) from the on-site and nearest agricultural production <br /> land affecting the property could be a possibility, since agricultural production occurs <br /> primarily to the west and east of the property. Agricultural pesticide aerial applications by <br /> helicopter to the property cropland consist of Pyrethroids which are environmentally soft, <br /> and ground applications of herbicides such as Round-up. According to the Western <br /> Fertilizer Handbook, the currently planted crop of oats require 115 pounds of nitrogen per <br /> growing season. A second crop of tomatoes requires 180 units, for a total of 295 pounds of <br /> nitrogen needed. One hundred units (pounds per acre) of urea are applied to the oats. <br /> Some nitrogen make-up is from horse manure at 102 pounds of nitrogen for each horse. <br /> This totals 2,550 pounds of nitrogen per year for 25 horses, or 2,550 pounds -41 acres = <br /> 62 units. Therefore, without additional nitrogen, there is a nitrogen deficiency within the <br /> cropland soils. <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. As referenced <br /> below, although DDT was banned in 1972, its presence in San Joaquin Valley soils is <br /> indicative of its long half-life of 15.6 years. Consequently, there may be extremely small <br /> concentrations of DDT and its degradates in the subject property soils. <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. <br /> Page-5- <br /> Chesney Consulting <br />
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