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ARCHIVED REPORTS_DRAFT ENVIRONMENTAL IMPACT REPORT
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ARCHIVED REPORTS_DRAFT ENVIRONMENTAL IMPACT REPORT
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Last modified
7/23/2020 5:02:58 PM
Creation date
7/23/2020 4:33:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
DRAFT ENVIRONMENTAL IMPACT REPORT
RECORD_ID
PR0506303
PE
2965
FACILITY_ID
FA0001086
FACILITY_NAME
MANTECA PUBLIC WORKS
STREET_NUMBER
2450
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
24130050
CURRENT_STATUS
01
SITE_LOCATION
2450 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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Arsenic <br /> Arsenic levels exceed the MCL of 10 micrograms per liter(gg/1)at 12 of the 16 city wells,which have <br /> concentrations of 12 to 19µg/11.Arsenic treatment has been initiated at each well to lower levels to below the <br /> MCL, and will be installed in any new wells constructed that exceed the MCL. <br /> Manganese <br /> There is no primary MCL for Manganese. The city has one well that exceeds the secondary MCL of 50 gg/l. This <br /> well has been installed with a filter to bring it into compliance. The secondary MCL addresses the aesthetic <br /> characteristics of water(e.g. taste and odor). <br /> Organic Chemicals <br /> Ethylene dibromide(EDB), dibromochloropropane(DBCP) and perchloroethylene (PCE)have been detected at <br /> low levels in seven of the city's wells. EDB and DBCP, agricultural chemicals that have been used in the <br /> surrounding area, are below the MCL in all but one well,which has been fitted with an activated carbon filter to <br /> remove the EDB and DBCP. PCE has been detected at one well at levels below the MCL. Concentrations of EDB <br /> and DBCP are expected to decline over time, as they have not been used for 20 years. PCE is also expected to <br /> decline as use of this chemical is more closely regulated. <br /> Factors Affecting Groundwater Quality <br /> In general,groundwater quality can be affected by unlined WWTP solids storage basins, land disposal sites, on- <br /> site wastewater treatment systems(OWTS) such as septage pits, and agriculture,including irrigation, fish,and <br /> dairy farming. It is reasonable to suspect that leachate from these sources may contain elevated levels of inorganic <br /> ions and salts,nitrogen in the form of nitrate or ammonia, and potentially other contaminants such as trace metals <br /> or organic compounds. Soil particles provide an effective barrier to the transmission of many chemical parameters <br /> through physical filtration, chemical complexation, or biological decay processes. However,the specific <br /> constituents that may be discharged to groundwater, concentrations of constituents in leachate, and fate in the <br /> underlying aquifers can cause potential risks to groundwater. <br /> Surface Water Quality <br /> San Joaquin River Water Quality <br /> The water quality of the lower San Joaquin River drainage and the Sacramento—San Joaquin Delta has been <br /> heavily affected by human activities.Land use in the Sacramento—San Joaquin Delta is dominated by agriculture <br /> (about 538,000 acres),while urban and commercial property account for about 64,000 acres of developed land <br /> (DWR 2005). The use of pesticides and fertilizers has altered water quality,with pesticides sometimes reaching <br /> levels acutely toxic to sensitive invertebrates. Agriculture and urban/stormwater runoff are the predominant <br /> sources of contaminants in the San Joaquin Basin, as shown on Table 4.9-4. Agricultural return flows sometimes <br /> contain high concentrations of dissolved solids (i.e. salinity)and trace elements that can degrade water quality. <br /> Watersheds that feed the river and Delta contribute pollutants and stressors that produce or exacerbate water <br /> quality problems. Construction of the Stockton Deep Water Channel and channeling of the San Joaquin River <br /> system have created an area of reduced dissolved oxygen near Stockton. Contaminants on the 303(d)impaired <br /> waters list for the lower San Joaquin River drainage and the Sacramento—San Joaquin Delta are shown in Table <br /> 4.9-6. <br /> Data from the Delta monitoring locations of long-term comprehensive surface water quality evaluation programs <br /> shown on Table 4.9-11 were compiled for three different water years for eighteen parameters(see constituents in <br /> DER EDAW <br /> City of Manteca 4.9-7 Hydrology and Water Quality <br />
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