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SU0010975_SSNL
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SU0010975_SSNL
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Last modified
10/28/2020 5:09:51 PM
Creation date
9/6/2019 10:11:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0010975
PE
2656
FACILITY_NAME
UP-96-0002
STREET_NUMBER
13400
Direction
W
STREET_NAME
MIDDLE
STREET_TYPE
RD
City
TRACY
Zip
95304-
APN
21204002
ENTERED_DATE
7/15/2016 12:00:00 AM
SITE_LOCATION
13400 W MIDDLE RD
RECEIVED_DATE
7/15/2016 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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\MIGRATIONS\M\MIDDLE\13400\UP-960002\SU0010975\SS NL STDY.PDF
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EHD - Public
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F7decreasing <br /> mound may form under the disposal field creating saturated flow conditions and <br /> istance the effluent must travel under unsaturated flow for effluent treatment to <br /> tion developed by Finnemore and Hantzsche (1983) is used below to predict themum rise of the mound: <br /> h=H+Z,n=2 <br /> where: h=distance from boundary to mid-point of the long-term mound, in ft <br /> H=height of stable groundwater table above impermeable boundary, in ft <br /> Zm= long-term maximum rise of the mound, in ft <br /> Substituting known and estimated values for the variables, we find the following: <br /> H=The height of stable groundwater above an impermeable boundary is estimated to be 5 ft based upon <br /> the measured standing water in the boring. Therefore, it will be assumed that a boundary exists at H= <br /> 7 - 5 (Highest measured water table depth)=2 ft. Long-term maximum rise of mound is estimated at 0.5 ft. <br /> Therefore, h=2+(0.5 2)=2.25 ft <br /> Zm 1 CI (4 In 11Ctt'o.5n ' t i-a5. <br /> where: Q=average daily flow in ft'/day <br /> A=area of disposal field in ft' <br /> C=mounding equation constant <br /> L=length of disposal field in ft <br /> K=horizontal permeability of soil in ft/day <br /> n=mounding equation exponent <br /> Sy=specific yield of receiving soil in percent <br /> t =time since the beginning of wastewater application in days <br /> Substituting known constants for the variables,we find the following: <br /> Q =425 gpd(One-quarter of Sunday ADF found on Pg 9 averaged over a typical week)_7.48 gals/ft=57 ft'/day <br /> A =6,500 ft(From mound system sizing calcs, Pg 15) <br /> C=Length to width ratio constant = 2.6,therefore,C= 1.135 <br /> L= 130ft <br /> K=Using average vertical permeability as most conservative= min/in: 1440 min/day= 15 min/in=8 ft/day <br /> h=2.25 (See above) <br /> n=Length to width ratio exponent =3,therefore,n= 1.76 <br /> Sy=7% <br /> t =3,650 days(10 yrs) <br /> Zm =0.00995 x 458 x 0.0786 x 2.12=0.76 ft <br /> From the calculations presented above,the maximum mound height that may occur under the future <br /> mound system is 0.76 feet. There remains a sufficient distance for effluent treatment to occur,which is <br /> generally regarded to be five feet, between the soil/effluent interface within the mound and the top of the <br /> theoretical mound above the highest elevation of the water table, as demonstrated: <br /> 5 ft=current distance between existing grade and water table minus 0.76 ft potential rise in water table= <br /> 4.24 ft. 4.24 ft+(0.33 ft of mound peat material + 1.0 ft of sand/drain rock)= 5.6 ft distance the mound <br /> system will provide between the sand-drain rock/effluent interface and the potential water table rise. <br /> I <br /> 6 <br /> Chesney Consulting <br />
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