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ARCHIVED REPORTS_XR0009414
Environmental Health - Public
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EHD Program Facility Records by Street Name
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T
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12 (STATE ROUTE 12)
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3049
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3500 - Local Oversight Program
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PR0545717
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ARCHIVED REPORTS_XR0009414
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Last modified
11/19/2024 3:45:51 PM
Creation date
6/3/2020 11:16:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009414
RECORD_ID
PR0545717
PE
3528
FACILITY_ID
FA0003912
FACILITY_NAME
MARTINIS BAIT & TACKLE
STREET_NUMBER
3049
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240
APN
02514016
CURRENT_STATUS
02
SITE_LOCATION
3049 W HWY 12
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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'RISKPRO'S SESOIL for Windows User's Guide <br /> s <br /> MCEC=a • CEC • MWTJVAL (14) ' <br /> s <br /> where. ' <br /> MCEC = maximum pollutant cation exchanged by the soil (µg/g soil) <br /> a , = 10.0 (units coefficient) ' <br /> CEC = cation exchange capacity of the soil (meq/100 g of dry wt. soil) <br /> _ MWT = molecular weight of the-pollutant cation (g/mol) - <br /> VAL = valence of the cation 0 <br /> With--clays,the-exchanged-ion-is-oftemcalcium;and-clay-soils-tend-to-have-the--highest-cation— <br /> exchange capacity Note,that the CEC value of a soil increases with increase in pH, but pH is <br /> not included in the CEC algorithm in SESOIL. The CEC value must be adjusted manually to <br /> include effects due to pH <br /> In SESOIL; cation exchange computed by Eq (14) is assumed to occur instantaneously, and <br /> irreversibly. Once maximum adsorption via exchange has been reached, no additional adsorption <br /> will be calculated The process is also assumed to take precedence over all other soil processes ' <br /> in competition for the pollutant cation <br /> The use of the cation exchange subroutine is optional If it is used, Eq (8) should not be us4M <br /> (i.e., model inputs for Y...d and I{a should be 0 0) unless the user has selected the model inputs <br /> in such a way as to avoid double accounting. It is up to the user to be sure that cation <br /> exchange is the predominant adsorption mechanism at the modeled site. This determination i <br /> includes-considerations of leachate characteristics such-as pH,ionic strength--and the presence - <br /> and_concentration of_other cations __The other cations, often found in landfill,leachate and_ <br /> aqueous industrial wastes, may have higher affinity for exchange with soil cations, and may, <br /> effectively block exchange between the pollutant and the soil cations--,In addition, the speciation <br /> of the pollutant should be considered (Bonazountas and Wagner, 1984). <br /> 3.5.5 Degradation: Biodegradation and Hydrolysis <br /> The pollutant cycle of SESOIL contains two transformation routines, that can be used to estimate ' <br /> pollutant degradation in the soil _ Biodegradation is the biologic breakdown of organic <br /> chemicals, most often by microorganisms Hydrolysis is a chemical reaction of the pollutant <br /> with water Both processes result in the loss of the original pollutant and the creation of new <br /> chemicals The SESOIL model accounts for the mass of original pollutant lost via degradation <br /> but does not keep track of any degradation products The user is responsible for knowing what ' <br /> the degradation products will be and their potential significance <br /> 1 <br /> Page 26 ' <br /> I ' <br />
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