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COMPLIANCE INFO_1991-2006
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COMPLIANCE INFO_1991-2006
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Last modified
6/29/2021 10:26:30 AM
Creation date
7/3/2020 11:19:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
1991-2006
RECORD_ID
PR0440074
PE
4461
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
02
SITE_LOCATION
2450 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sfrench
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4461_PR0440074_2450 W YOSEMITE_.tif
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EHD - Public
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Technical Memorandum 4- March 31, 1992 <br /> If 55 lbs/acre (1990 data) is supplied from the sludge, the remaining crop nitrogen uptake <br /> capacity is 545 lbs/acres. The effluent nitrogen application rate of 814 lbs/acre exceeds the <br /> available crop nitrogen requirement of 545 lbs/acre. Therefore,effluent application on the site <br /> needs to be reduced to meet agronomic nitrogen demands. <br /> Heavy Metals Loading <br /> The concentration of heavy metals (from Table 2) in sludge is used to calculate the amount <br /> of sludge that can be land applied. The cumulative pollutant loading rates used in this <br /> analysis are as stated in the Environmental Protection Agency's (EPA)proposed 40 CFR,Part <br /> 503 draft sludge regulations. The final regulations are expected to be issued in July 1992. <br /> EPA's proposed Cumulative Pollutant Loading Rates (CPLR) is presented in Table 7. <br /> For the purpose of this analysis, the calculations are based on 1984 as the start of operations <br /> to determine the cumulative pollutant loads that have been applied to the 303 acre site. The <br /> remaining capacity of Manteca's agricultural land is calculated based on the total metals <br /> applied from the sludge and effluent since 1984. Between 1984 and 1988, sludge was applied <br /> as a liquid over the entire 303 acre site. In 1989 and 1990, dried digested sludge was applied <br /> on 98 acres and 68 acres, respectively. For the years 1989 and 1990, effluent equivalent to <br /> 2.26 mgd and 3.24 mgd, respectively, were applied over the entire 303 acres. <br /> A comparison of the actual total metals (effluent and sludge) applied since 1984 and EPA's <br /> cumulative pollutant loading rates is presented in Table 8. Results from Table 8 indicate that <br /> copper is the contolling parameter that determines the remaining capacity of the agricultural <br /> land. At this time, 78 percent of the total capacity of the 303 acre site is available for sludge <br /> and effluent application, assuming that only 210 acres of the site is available for sludge <br /> application. <br /> Based on the results of this analysis, it appears that the past seven years' sludge and effluent <br /> application has exhausted 22 percent of the site's useful capacity. <br /> PROJECTED SLUDGE AND EFFLUENT APPLICATION RATES <br /> Based upon the historical sludge and effluent application data, the future sludge and effluent <br /> application rates on the 303 acre site is controlled by the rate of effluent nitrogen applied. <br /> A ten-year planning period(1991-2000) is used to determine the projected sludge and effluent <br /> loads. In the year 2000, it is assumed that the flows would be 6.95 mgd. Table 9 presents <br /> a projection of the sludge and effluent loads that can be land applied in the future. <br /> The results in Table 9 indicate that effluent at an annual equivalent of 2.24 mgd can be land <br /> applied in 1991. In the year 2000, the effluent application would be reduced to an annual <br /> equivalent of 2.15 mgd. It is assumed that sludge is applied on 210 acres of City owned <br /> land. Effluent is applied on both the 210 acre City-owned land and the 93-acres of leased <br /> land. At these effluent application rates, it is expected that a nitrogen balance with the crop <br /> nitrogen uptake requirements would be achieved. <br />
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