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SU0007861
Environmental Health - Public
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SU0007861
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Entry Properties
Last modified
1/6/2020 11:37:03 AM
Creation date
9/4/2019 10:03:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007861
PE
2675
FACILITY_NAME
PA-0800105
STREET_NUMBER
9999
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
APN
20106003
ENTERED_DATE
8/11/2009 12:00:00 AM
SITE_LOCATION
9999 S AUSTIN RD
RECEIVED_DATE
7/24/2009 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
Scanner
SJGOV\sballwahn
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FilePath
\MIGRATIONS\A\AUSTIN\9999\EIR PA-0800105\NOP.PDF
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EHD - Public
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Draft Environmental Impact Report Page IV.D-27 <br /> Forward Landfill Expansion <br /> Table IV.D-4 shows the total GHG emissions from the landfill for the current actual and <br /> future potential scenarios. As discussed previously, the methane emission is <br /> anthropogenic and is always considered a GHG emission from the landfill. The CO2 <br /> emission is biogenic,but is also considered as an emission from the landfill,but should <br /> not be attributed to the landfill since carbon dioxide from refuse would normally occur in <br /> the natural carbon cycle. The energy displacement credit is a credit for the landfill.The <br /> carbon sequestration is also a credit for the landfill. The total GHG emissions from <br /> Forward Landfill are the sum of the methane and CO2 emissions minus the power <br /> displacement and carbon sequestration credits. Negative totals indicate that more GHG <br /> is displaced and carbon is stored in the landfill than is GHG is emitted. Both the CARB <br /> default values and the Solid Waste Industry for Climate Solutions (SWICS) site specific <br /> values are shown. <br /> It should be noted that the amount of carbon sequestered is greater than the GHG <br /> emissions from the landfill for all scenarios. When carbon storage is included in the GHG <br /> total for the project, the Project lowers the GHG emissions of Forward Landfill because <br /> more carbon is sequestered in the landfill where it will not be emitted as either methane <br /> or CO2. <br /> Table IV.D-4 <br /> GHG Emissions (metric tons a uivalent CO2 er ear) <br /> SIN <br /> ®m m <br /> Future Project-Current Actual (Flare) -33,570 -23,676 <br /> Future Project-Current Actual (LFG Engine) -36,011 -26,361 <br /> Future Project-Current Permitted(Flare) -19,659 -15,609 <br /> Future Project-Current Permitted (LFG Engine) -22,099 -18,295 <br /> SOURCE: SCS Engineers,2009 <br /> With regard to Items B the project results in a decrease in GHG emissions as a result of <br /> increased power displacement and increased carbon storage. <br /> With regard to Item C,the project is located inclose proximity to the City of Stockton, <br /> which would minimize "hauling GHG emissions" in comparison to a landfill located in a . <br /> remote area (where all hauling trips would generate higher GHG emissions). <br /> The review of Items A, B, and C indicate that the project would not conflict with the State <br /> goals established in AB 32 and, therefore, the project's emissions of GHGs would <br /> constitute a less than significant impact. <br /> Mitigation Measure IV.D.6: None required. <br /> � q <br /> Impact IV.D.7.The project would contribute to a cumulative air quality impact in <br /> the project area. <br /> According to the SJVAPCD GAMAQI, cumulative impacts should be assessed for ozone, <br /> PMI(), CO and TAC. <br /> Ozone impacts are the result of the cumulative emissions from numerous sources in the <br /> region and transport from outside the region. Ozone impacts are assessed based on the <br />
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