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SU0002529_SSNL
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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99 (STATE ROUTE 99)
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2600 - Land Use Program
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SA-01-20
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SU0002529_SSNL
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Last modified
11/19/2024 1:52:11 PM
Creation date
9/8/2019 12:53:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002529
PE
2633
FACILITY_NAME
SA-01-20
STREET_NUMBER
15051
Direction
S
STREET_NAME
STATE ROUTE 99
ENTERED_DATE
10/29/2001 12:00:00 AM
SITE_LOCATION
15051 S HWY 99
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\N\HWY 99\15051\SA-01-20\SU0002529\SS STDY.PDF
Tags
EHD - Public
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08/16/01 THU 16:55 F.a1 [a 005 <br /> k'9 KLEINFELt7ER <br /> High Estimate <br /> N, = 0.3(1.75)(45)(1 —0.1)+1.0(3) = 21.3 +3.0 = 6.9 m-/I as N <br /> 03(l.75)+3 0.52 + 3 <br /> Average N,= 6.21 rag/1 as N <br /> One of the factors that is required by the SICPPIS is to det.ennine the existing value of nitrate in <br /> the groundwater below the site. A groundwater sample was obtained for the existing on-site well <br /> using "clean" methods. At least 5 gallons of water was first bailed from the well prior to <br /> obtaining our earnple. The wator sairple was submitted to Cec►Analytical Lahorataries, hir,. <br /> using chain-of-custody procedures to evaluate nitrate as N in accordance with EPA Test Method <br /> 300. Results of the test showed a non-detectable nitrate as N concentration. A copy of our test <br /> rc,sttlts and chain of custt,dy a1c wtt4,Amd. VvIliru this valor-, is cumbivCd With Our loin and high <br /> nitrate-nitrogen (N) in groundwater calculated above, the total nitrate-nitrogen is well below the <br /> state drinking water MCL standard. eALQrCrdjngly. we conclude. that placement of the new s.-ptic <br /> system on the site should not cause a rise of nitrate levels above State standards. <br /> DRAINAGE BASIN <br /> There are many factors that influence storm water disposal Clear water was used in our tests, <br /> whereas oil residue, silt, organic matter and other deleterious material will likely oe included in <br /> the actual storm water. Varations in soil conditions within the basin will also likely affect <br /> percolation characteristics. For use in design, a factor of safety on the order of 1.5 to 2 should be <br /> applied to ll?rt puQ914:iun rafe5 d51imal-d, <br /> The above percolation values apply to drainage trenches or drywells installed in the basins and <br /> possibly to the sides of the basins. Depending on the depth of the basins, the design percolation <br /> rates for the basin sides should be farther mviewed. Over time, very little percolation should be <br /> assumed through the basin bottoms due to silting and organic build-up unless a vigorous program <br /> is followed to maintain the basins by frequent cleaning and discing to reduce silt build-up. <br /> Subsurface drain trenches andlor drywells should be equipped with filtered intakes. Our <br /> representative should be allowed to observe the soils exposed daring construction of the basins <br /> and subsurface trenches or drywells in order to confirm that the design rates used are appropriatc <br /> for the actual soils encountered. <br /> 20-4630-01.G01/2011 R9E6 Page 4 of 5 <br /> Copyright 2001 Kleinfelder,Inc. August 16,2001 <br />
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