My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SR0081321_SSNL
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
L
>
LOVELY
>
4700
>
2600 - Land Use Program
>
SR0081321_SSNL
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
3/24/2022 1:53:43 PM
Creation date
12/17/2019 3:48:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0081321
PE
2602
FACILITY_NAME
GREWAL FARMS
STREET_NUMBER
4700
Direction
W
STREET_NAME
LOVELY
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25010013
ENTERED_DATE
10/25/2019 12:00:00 AM
SITE_LOCATION
4700 W LOVELY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
TSok
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
55
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
rNLS§2.3, SSS§ 4.3, 4.4, 4.5, 4.6. There are no domestic or irrigation wells on the subject <br /> Parcel. Irrigation water is supplied by an irrigation district. <br /> Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading to the underlying groundwater is contingent upon the environmental <br /> factors required for nitrification to occur. These conditions include soil pore-space oxygen <br /> content, soil temperature, pH, electrical conductivity, organic matter, cation exchange capacity, <br /> and alkalinity. Alkalinity in wastewater effluent is derived from future on-site well water, in <br /> addition to the introduction of wastes. Nitrification consumes approximately 7.1 mg of alkalinity <br /> for every mg of ammonia-nitrogen(NH4-N) oxidized. Nitrification of the average Total Nitrogen <br /> (TN)concentration of 62 mg/L, as determined on Page 5, would require: 62 mg/L NH4-N x 7.1 <br /> mg CaCO3 =440 mg/L alkalinity. The alkalinity concentration in the underlying groundwater is <br /> unknown, but assuredly below 440 ppm. Therefore,there is an insufficient alkalinity in the <br /> domestic water for complete nitrification to readily proceed without the introduction of wastes <br /> along with the alkalinity in the soil environment. <br /> E. SURFACE WATER INFORMATION <br /> Storm water management will be on-site, flowing into the almond orchard surrounding the Ag <br /> Building project. Percolating rainwater may provide an indeterminable water table dilution effect <br /> to percolating wastewater effluent. <br /> Climatic Data: Rainfall <br /> NLS§3.2. The filter bed for the project has not been designed to take advantage of <br /> evapotranspiration. Consequently, evapotranspiration(Eto) data from the California Irrigation <br /> Management Information System (CIMIS) is not applicable information. Only when plant life, <br /> specifically a grass, is allowed to grow over the filter bed area and is periodically mowed to <br /> alleviate nitrate loading, can CIMIS data be used. Consequently, the only applicable data that <br /> pertains to this project in the nitrate loading equation and calculations below, is rainfall for this <br /> specific Tracy area. <br /> III. NITRATE LOADING STUDY FINDINGS <br /> A. WASTEWATER FLOW VOLUME PROJECTIONS AND CHARACTERISTICS <br /> Wastewater Flow Volume Projections <br /> Typically, loading projections for commercial facilities are based on the maximum anticipated <br /> wastewater flows generated by occupied people that occur daily, weekly, monthly, or for singular <br /> events. <br /> Page -4- <br /> Chesney Consulting <br />
The URL can be used to link to this page
Your browser does not support the video tag.