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SR0083411_SSNL
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SR0083411_SSNL
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Last modified
4/8/2021 4:54:02 PM
Creation date
4/8/2021 4:49:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0083411
PE
2602
FACILITY_NAME
19960 S SAN JOSE RD
STREET_NUMBER
19960
Direction
S
STREET_NAME
SAN JOSE
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
20929032
ENTERED_DATE
3/16/2021 12:00:00 AM
SITE_LOCATION
19960 S SAN JOSE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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III. NITRATE LOADING STUDY FINDINGS <br />WASTEWATER CHARACTERISTICS AND FLOW PROJECTIONS <br />WASTEWATER CHARACTERISTICS <br />The wastewater characteristics are anticipated to be those normally found in typical domestic or <br />household systems. The scientific literature (Ref. 10) cites domestic wastewater nitrogen concentrations <br />of 35 mg/L N. This concentration will be used in the calculations below. <br />WASTEWATER FLOW VOLUME PROJECTIONS <br />To determine nitrate-nitrogen loading from any project, wastewater flow volumes must be determined as <br />accurately as possible. Domestic flow volume projections are typically approximated from the USEPA <br />Onsite Wastewater Treatment Systems Manual, Pg. 3-4. However, for nitrate loading calculations, the <br />EHD now requires wastewater flow volume projections from single family residential structures to be <br />calculated as follows: 100 gallons per day (gpd) for the first bedroom and 50 gpd for all subsequent <br />bedrooms within the structure. <br />The flow volumes are calculated below using a maximum number of bedrooms for both the primary and <br />accessory unit dwellings. Therefore, the flow volumes for this project are: <br />5 Bedroom Primary Structure: 100 + 50 + 50 + 50 + 50 = 300 gpd. <br />5 Bedroom Accessory Unit Dwelling Structure: 100 + 50 + 50 + 50 +50 = 300 gpd. <br />Total Wastewater Flow Volume from the subject property: 300 + 300 = 600 gpd. <br />CALCULATED NITRATE-NITROGEN LOADING <br />NLS§ 3.3, 3.4, 3.5, 3.6. The calculated nitrate-nitrogen impact to the soil and potentially to the <br />groundwater is difficult to determine due to the large number of variables involved and unknown at this <br />time. These include: 1.) Variability in wastewater flows, nitrogen concentrations and dilution affects that <br />may occur, 2.) Impact from upgradient nitrate sources, 3.) Changes in groundwater directional flow and <br />elevation, 4.) Denitrification potential within the soil environment and within the confined and/or <br />unconfined aquifers, and 5.) Landscape/native grass uptake of nitrogen. <br />Various scientific methods exist to estimate nitrate-nitrogen loading. This Study uses the <br />Hantzsche/Finnemore Equation to predict the average resultant concentration of nitrate-nitrogen in <br />effluent recharge water from a conventional septic system. The effluent concentration must not exceed 10 <br />ppm nitrate-nitrogen (45 ppm as nitrate). <br />Wastewater researchers place the nitrogen reduction occurring in septic tanks at 10% to 20%. From the <br />September 2004 Symposium "University Curriculum Development for Decentralized Wastewater <br />Management - Onsite Nitrogen Removal," Dr. Stuart Oakley of California State University Chico states <br />that "approximately 20% of the total nitrogen generated is removed in the septic tank" (Ref. 8). As noted <br />below, this estimate of 20% is used for nitrogen reduction occurring in the septic tanks. <br />6 <br />Chesney Consulting
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