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CORRESPONDENCE_1994-1998
EnvironmentalHealth
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4400 - Solid Waste Program
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PR0440007
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CORRESPONDENCE_1994-1998
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Last modified
6/7/2021 9:24:25 AM
Creation date
7/3/2020 11:08:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
1994-1998
RECORD_ID
PR0440007
PE
4434
FACILITY_ID
FA0000595
FACILITY_NAME
HARNEY LANE LANDFILL
STREET_NUMBER
14750
Direction
E
STREET_NAME
HARNEY
STREET_TYPE
LN
City
LODI
Zip
95240
APN
06503006
CURRENT_STATUS
01
SITE_LOCATION
14750 E HARNEY LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\cfield
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FilePath
\MIGRATIONS\SW\SW_4434_PR0440007_14750 E HARNEY_1990-1994.tif
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EHD - Public
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The Harney Lane Sanitary Landfill is located to the north of ephemeral South Paddy <br /> Creek. Article 5 requires background surface water monitoring points which represent <br /> surface water quality that has not been affected by landfill activities. Background <br /> monitoring point S-1 is sampled in South Paddy Creek above the detention basin inlet, <br /> and downstream monitoring point S-2 is sampled at the point of discharge into South <br /> Paddy Creek from the stormwater detention basin. <br /> There are no unsaturated zone monitoring facilities at the Harney Lane Sanitary Landfill. <br /> Although Article 5 requires monitoring of the unsaturated zone at waste management <br /> units, the lack of information regarding the landfill base configuration makes unsaturated <br /> zone monitoring unfeasible. <br /> 3.1.2 Revisions to the Monitoring ram <br /> The first phase of the evaluation program will be to continue with the current monitoring <br /> program sampling frequency and conduct statistical analysis for MW-2 data. As required <br /> by WDR Order No. 93-093, quarterly monitoring of all the monitoring wells for VOCs <br /> will be continued. The WQPS report specifies that the tolerance interval method be used <br /> where statistical comparison is applicable. Because VOCs are not naturally occurring, the <br /> concentration limit for most VOCs is its detection limit. Therefore, once VOCs are <br /> detected, the trend analysis method is more appropriate. <br /> The Kendall-tau test for trend is proposed for the site monitoring program to evaluate the <br /> correlations between time and monitoring parameter concentrations.A detailed description <br /> of the trend analysis method is contained in Appendix C. Consistent with the use of trend <br /> analysis, the concentration limits for the organic monitoring parameters in well MW-2 be <br /> "no statistically significant upward trend." <br /> 3.2 Assessment of Nature and Extent of Release <br /> Section 2550.9(x) of Article 5 requires the County to assess the nature and extent of the <br /> release from the waste management unit. Section 2550.9(b) requires that the discharger <br /> collect and analyze all data necessary to assess the nature and extent of the release to <br /> determine the spacial distribution and concentration of the constituents of concern <br /> throughout the zone affected by the release. This section also requires that the discharger <br /> complete this assessment within 90 days of establishing an evaluation monitoring <br /> program. <br /> An assessment of the nature and extent of the observed release will be conducted in a <br /> phased approach. The first phase will entail a review of the historical groundwater data <br /> for the site and from other sites in the Central Valley that have VOC releases. Since the <br /> RWQCB has already indicated a concern that MW-4 might be impacted from off-site <br /> sources, EMCON proposes that a review of analytical results from the adjacent waste <br /> SAC/pj0 093M390011.8a1-94/lfc:9 Rev.0. 10/17/94 <br /> 0939-001.18 6 <br />
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