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SU0006677 SSNL
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SU0006677 SSNL
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Last modified
5/7/2020 11:32:39 AM
Creation date
9/6/2019 10:05:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006677
PE
2631
FACILITY_NAME
PA-0700315
STREET_NUMBER
12687
Direction
S
STREET_NAME
MANTHEY
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19123007
ENTERED_DATE
8/3/2007 12:00:00 AM
SITE_LOCATION
12687 S MANTHEY RD
RECEIVED_DATE
8/2/2007 12:00:00 AM
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\M\MANTHEY\12687\PA-0700315\SU0006677\NL STDY.PDF
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EHD - Public
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rr4. <br /> . Published Data in the San Joaquin County Sewage Standards and scientific literature. <br /> . Number of bathroom fixtures correlated with bathroom use per capita for a facility. <br /> . Number of parking spaces for a facility. <br /> Maximum number of people(e.g., employees, customers,etc.)for a facility. <br /> . Historical wastewater flow data from an existing facility. <br /> 1. The San Joaquin County Sewage Standards assigns l5lag lons per person for Industrial Buildings <br /> with no food cafeteria, or 30 ga11Qgs mer person for day wRrkcrs at offices. <br /> __. <br /> 2. The Sewage Standards assign 150 gallons per toilet fixture for employee/public use. <br /> Since it cannot be adequately determined how many people will use the Office Trailer restroom on a <br /> daily basis, the Sewage Standard of assigning 150 gallons per day is applicable. However, this <br /> Standard was based on old style toilets using 3 to 5 gallons per flush. Contemporary toilets use 1.5 <br /> gallons per flush. Wastewater flows projected from the Office Trailer is equivalent to 100 flushes <br /> per day(150 gals/day 1.5 gals/flush/day= 100 flushes)which incorporates an enormous safety <br /> factor. <br /> Wastewater Flow Characteristics <br /> It is assumed there will be no cooking, or food production in the Office Trailer. Therefore, there <br /> should be no concentrated organic loading. The characteristics of the wastewater flow will be <br /> predominately blackwater from toilets, with a comparatively small volume of graywater from sinks, <br /> or other sources of graywater. Additional wastewater constituents may consist of coffee,juices or <br /> other similar type liquids to the system. No industrial or commercial chemicals, solvents, etc. are to <br /> be introduced into the septic system. <br /> From the anticipated wastewater characteristics described above, the nitrogen emanating from the <br /> project may be at a higher concentration than what would normally be found in a typical domestic <br /> or household system. This can be attributed to the lack of a dilution effect that graywater from <br /> showers, laundry, and dishwashing would provide from a household. The scientific literature cites <br /> nitrogen concentrations in residential septic effluent typically ranging from 17 mg N/L for basins, <br /> sinks, etc. to 140 mg N/L for toilet wastes Therefore, considering a 70/30 percent usage for toilet <br /> water volume ind sinkOvate yr olume,respectively, a value of 103 mg N/L of septic effluent will be <br /> used to calculate nitrate-nitrogen loading for this project. A value of 66 mg N/L is typically used <br /> for residential calculations, as indicated in the scientific literature. <br /> B. CALCULATED NITRATE-NITROGEN LOADING <br /> The calculated nitrate-nitrogen impact to the soil and ultimately to the groundwater is difficult to <br /> determine due to the large number of variables involved, and variables unknown at this time. These <br /> include: 1.) Impact from upgradient nitrate sources, 2.) Variability in wastewater flows, nitrogen <br /> concentrations and dilution effects from effluent and stormwater recharge, 3.) Changes in <br /> groundwater directional flow and elevation, 4.) Denitrification potential within the soil environment <br /> and within the confined and unconfined aquifers and 5.)Potential landscape uptake of nitrogen. <br /> 7 <br /> Chesney Consulting <br />
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