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SU0004494 SSNL
Environmental Health - Public
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SU0004494 SSNL
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Last modified
12/5/2019 4:33:16 PM
Creation date
9/6/2019 10:01:59 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0004494
PE
2622
FACILITY_NAME
PA-0400266
STREET_NUMBER
1481
Direction
W
STREET_NAME
MANILA
STREET_TYPE
RD
City
LATHROP
APN
19127001
ENTERED_DATE
5/27/2004 12:00:00 AM
SITE_LOCATION
1481 W MANILA RD
RECEIVED_DATE
5/25/2004 12:00:00 AM
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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\MIGRATIONS\M\MANILA\1481\PA-0400266\SU0004494\SS STDY.PDF
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EHD - Public
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r Richland Communities Inc. 5943.5.001.03 <br /> 1481 West Manila Road,PA-04-266 (MS) September 9,2004 <br /> SEPTIC FIELD SOIL SUTTABILTTY STUDY Page 3 <br /> located to the northwest of the residence at 1481 Manila Drive (Figure 2). The water sample was <br /> collected directly from af ua cet outside of the shed From the well head, water passed <br /> through a pressure tank before being pumped through the faucet located outside the shed. The <br /> water sample was collected in pre-cleaned laboratory containers supplied by the testing <br /> laboratory. No purging of the water system was performed. Following sample recovery, the <br /> r sample containers were labeled and placed in an ice cooled chest for transport under documented <br /> chain of custody to Sequoia Analytical inacramento, California for analysis of <br /> 1,2-Dibromo-3-chloropropane (DBCP) and Nitrate as N 3. The result of the laboratory analyses <br /> did not reveal detectable concentraa iMM 5T BCP and Nitrate as NO3 above the laboratory <br /> detection limits of 0.01 ug/L and 1 mg/L, respectively. The laboratory detection limits are <br /> below the EPA Region 9 Preliminary Remedial Goals for tap water. The Sequoia Analytical <br /> laboratory results are attached as Appendix C. <br /> Percolation Test Preparation <br /> Two 12-inch-diameter percolation test holes (one per parcel) were drilled to a depth of 36 inches <br /> below the existing ground surface at the locations shown on Figure 2. Following drilling, the <br /> sides of the holes were scraped to remove smear from the drilling process and loose material was <br /> removed from the bottom of each hole. Preparation of the percolation test hole began by placing <br /> two inches of pea-sized gravel in the bottom of each hole. A four-inch-diameter perforated drain <br /> pipe was then placed in the hole and was surrounded by approximately two feet of 3/4-inch <br /> diameter drain rock. Water was added to the hole up to the ground surface (36 inches) and <br /> _ allowed to pre-soak overnight. Per Mr. Justin Hess (San Joaquin County Environmental Health <br /> Specialist), due to shallow groundwater at the site, no deep percolation tests were required. <br /> ` Percolation Testing <br /> The percolation tests were performed at the property on August 25 2004. Upon completion of <br /> the overnight presoak, The holes were refilled <br /> with water to a level approximately 6 inches above the gravel base at the bottom of the pipe. The <br /> water level was measured every 10 minutes for a 30-minute period. After the 30-minute period <br /> the water level was reset to approximately 6 inches above the gravel base. Since six inches of <br /> water did not all percolate in the first 30 minutes in either location, the measurement interval was <br /> increased to 30 minutes and the process was repeated for four hours. The last stabilized <br /> .. measurement was performed under the observation of Mr. Ray Borges, a San Joaquin County <br /> Environmental Health Specialist and was used to determine the peicoRion rate of 7.6 minutes <br /> per inch (mpi) for Test Hole #1 located on Parcel 1 and 12.5 mpi for Tes :a located on <br /> Parcel 2. The completed San Joaquin County percolation test rate Form lc (EHD 42-02-003 <br /> revised 5/7/02) is attached as Appendix D. <br /> r <br /> r <br />
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