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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
Scanner
LSauers
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EHD - Public
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i <br /> RISKPRO'S SESOIL for Windows User's Guide <br /> The biodegradation process is usually a significant loss mechanism to soil systems since soil <br /> Ienvironments have a diverse microbial population and a large variety of food sources and <br /> habitats (Hamaker,1972). Many environmental factors affect the rate of biodegradation in soil, <br /> including pH, moisture content of the soil, temperature, redox potential, availability of nutrients, <br /> oxygen content of the soil air, concentration of the chemical, presence of appropriate <br /> microorganisms, and presence of other compounds that may be preferred substrates. However, <br /> ISESOIL does not consider these factors <br /> Biodegradation in SESOIL is handled as primary degradation, which is defined as any structural <br /> transformation in the parent compound which results in a change in the chemical's identity It <br /> is estimated using the chemical's rate of decay in both the dissolved and adsorbed phases <br /> according to the first-order rate equation. <br /> Pd =(C•O •kdi +S• pb•k -A•d *At (1 <br /> where: <br /> Pd = decayed pollutant mass during time step t (µg) <br /> kd, = biodegradation rate of the compound in the liquid phase (day) <br /> kd, = biodegradation rate of the compound in the solid phase (day) <br /> A = area of pollutant application (CMI) <br /> d, = depth of the soil sublayer (cm) <br /> I At = time step (day) <br /> c, 8, s, and Pb are as defined for Eqs (S) and (9) <br /> INote that c, B, and s are functions of time in the SESOIL model <br /> The use of a first-order rate equation is typical for fate and transport models and generally is <br /> an adequate representation of biodegradation for many chemicals However, due to the many <br /> factors affecting biodegradation, in some cases a first-order rate may not be applicable to the site <br /> field conditions and a zero-order or a second-, or higher-order rate might be more appropnate <br /> The biodegradation algorithm in SESOIL that is described by Eq (15) cannot handle these cases. <br /> The user is cautioned regarding the use of literature values for the biodegradation rates since <br /> I these values are quite variable and in many cases are not applicable to site field conditions. In <br /> most cases, biodegradation rates are very site-specific and uncertainty in these rates must be <br /> recognized. The user-supplied first-order decay rate constants (for moisture and solids) should <br /> Ibe values measured for the pollutant in a soil culture test under conditions similar to the site <br /> being modeled. <br /> Page 27 <br />
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