My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0002230
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
T
>
TURNER
>
1973
>
2600 - Land Use Program
>
UP-98-03
>
SU0002230
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:29:07 AM
Creation date
9/9/2019 10:46:45 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0002230
PE
2626
FACILITY_NAME
UP-98-03
STREET_NUMBER
1973
Direction
W
STREET_NAME
TURNER
STREET_TYPE
RD
City
LODI
Zip
95240
ENTERED_DATE
10/26/2001 12:00:00 AM
SITE_LOCATION
1973 W TURNER RD
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\T\TURNER\1973\UP-98-03\SU0002230\APPL.PDF \MIGRATIONS\T\TURNER\1973\UP-98-03\SU0002230\CDD OK.PDF \MIGRATIONS\T\TURNER\1973\UP-98-03\SU0002230\EH COND.PDF \MIGRATIONS\T\TURNER\1973\UP-98-03\SU0002230\EH PERM.PDF
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
301
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
Wastewater Treatment System FALL CREEK <br /> Engineering Report ENGINEERING,INC. <br /> rate of 0.16 in/hr, each zone will receive approximately 0.13 in/day. On average during peak <br /> crush months each zone will get irrigated every other day. That means that the field will get an <br /> average of 0.5 inches of water per week (2 in/mo). <br /> The average daily process water application rate is about half of the evapotranspiration rate of <br /> grass in Lodi during the month of September (4.6 in/mo), as was shown in Table 4.1. This <br /> implies that additional water may need to be applied to keep the field green. It also implies that <br /> '�. additional process water may be added without hydraulically overloading the field. Similarly, <br /> ` the Winery may choose to apply additional water to the field during earlier spring and summer <br /> months when grassland evapotranspiration rates exceed process water generation rates. Water <br /> losses during the spring and summer month will primarily be through evapotranspiration with a <br /> minimal amount lost through infiltration. Infiltration may be higher in the winter when grass <br /> evapotranspiration rates are low and stormwater generation is high. <br /> 5.2. Surface Loading Rate <br /> 5.2.1. Organic Loading Rate <br /> The maximum land application rate for organic material applied to a slow-rate land infiltration <br /> system is generally required to be less than 100 lbs BOD/ac-day. Calculations were performed <br /> to determine if the disposal system at Jessie's Grove Winery would meet these requirements. An <br /> ` average daily flow rate (Q) of 1,660 was used and it was assumed as a worst-case scenario that <br /> the concentration of BOD in the effluent(C j was 400 mg/L (a 90% BOD reduction). The daily <br /> field application area(Aa) will be approximately 0.5 acres (2 sets/day each consisting of one <br /> 0.25-acre zone). The maximum daily surface-loading rate (LS) was therefore calculated as <br /> follows: <br /> — 1,660gaf * 400mg * 3.785L * 1b <br /> CC — d L gal 4.536*10'mg = 1 llbs/ac/day. <br /> Aa 0.5acres <br /> Each field will have approximately one day of rest between each day of water application, the <br /> average daily surface-loading rate is approximately 5.5 lbs/ac/day. This is well below the target <br /> generally set of 100 lbs BOD/ac-day. <br /> — <br /> 5.2.2. Nitrogen Loading Rate <br /> Nitrogen Loading Rate was calculated in a similar manner to BOD. The maximum land <br /> application rate for nitrogen is generally 150 lbs/ac-yr. To determine whether the disposal <br /> low system at Jessie's Grove would meet these requirements, several assumptions were made <br /> regarding the concentration of nitrogen in the process wastewater. To date there has been no <br /> nitrogen testing of the Winery's process wastewater quality, however in general Winery process <br /> wastewater is assumed to be low in total nitrogen with a typical concentration range between 5 <br /> and 50 mg/L, as was shown in Table 2.1. It was assumed that the average total nitrogen <br /> %W concentration is 25 mg/L. Further, it was assumed that on average the wetland reduces the <br /> concentration of nitrogen in the wetland by 50%. Therefore the average concentration of <br /> JESSIE'S GROVE WINERY MAY 2002 <br /> 21 <br />
The URL can be used to link to this page
Your browser does not support the video tag.