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CORRESPONDENCE_2003-2005
Environmental Health - Public
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CORRESPONDENCE_2003-2005
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Last modified
4/17/2023 4:15:06 PM
Creation date
7/3/2020 10:49:30 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2003-2005
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\cfield
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\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2003-2005.tif
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EHD - Public
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expected to occur. Also shown are how increases in EXAMPLES OF ENVIRONMENTAL <br /> these environmental characteristics effect the magni- FATE CHARACTERISTICS WHICH <br /> tude of the anticipated attenuation and,therefore,the INFLUENCE ATTENUATION FACTORS <br /> selection of environmental attenuation factors. As the following characteristics increase... EFFECT ON <br /> ATTENUATION FACTOR <br /> If ground water is threatened by waste constitu- FOR THE PROTECTION OF GROUND WATER— INCREASE DECREASE <br /> ents,increases in the depth to ground water(thickness Depth to Highest Ground Water(incl.capillary fringe) <br /> • Net Recharge (i.e.,[rainfall]—[evaporation]) <br /> of the vadose zone),in the clay content,organic matter Characteristics of the Vadose Zone: <br /> a capacity or H of vadose zone Permeability and Porosity <br /> content,ion exchan <br /> g p •� p Clay Content <br /> materials,and in the ionic strep th,viscosity,de add- Organic Matter Content <br /> g � � Ion Exchange Capacity and pH <br /> bility or octanol/water partition coefficient(the affinity Pollutant Characteristics: _ <br /> Polarity <br /> of the chemical for octanol or soil organic matter versus Ionic Strength(more positive) <br /> Volatility(potential for vapor transport) <br /> its affinity for water)of the waste constituent will cause Viscosity <br /> Degradability or Biologic Activity <br /> the attenuation factor to be larger(greater attenuation Octanol/Water Partition Coefficient(Kow) 77,1777777 <br /> • Other Constituents that Could Increase Mobility <br /> expected). Increases in the net recharge rate(a driving Topography(steepness of terrain) <br /> • <br /> force for movement of waste constituents),in the per- Total Pollutant Load(mass loading)Uncertainty of the Data and Assumptions <br /> meability or porosity of vadose zone materials,in the <br /> polarity or volatility of the waste constituent,in the FOR THE PROTECTION OF SURFACE WATERS— <br /> concentrations of solvents or other chemicals that can • Distance from Drainage Courses - <br /> • Topography(steepness of terrain) <br /> increase the permeability of soils or act as carriers for • Pollutant Characteristics: <br /> Volatility(loss to atmosphere) <br /> the constituent,or in the mass loading of waste con- Reactivity or Degradability <br /> stituents will cause the attenuation factor to be smaller Polarity <br /> Octanol/Water Partition Coefficient(Kow) <br /> (less attenuation ex ected as the constituent mi rates Other Constituents That Could Increase Mobility <br /> P g Initial Dilution Upon Reaching Surface Waters <br /> to ground water). (min.surface water flow vs.max.pollutant flow) <br /> • Interconnection of Ground and Surface Waters <br /> If surface waters are threatened by constituents in a Total Pollutant Load(mass loading) <br /> • Uncertainty of the Data and Assumptions <br /> waste,increases in the distance of travel from the site <br /> of waste discharge to surface water,in the volatility, Figure 6 <br /> reactivity,degradability or octanol/water partition <br /> coefficient of the waste constituent,and in the amount tal attenuation should also be reflected in the amount <br /> of initial dilution that the waste or leachate would re- of vadose zone and ground water monitoring that is <br /> ceive upon entering surface waters will cause the at- required for a waste management unit. Greater uncer- <br /> tenuation factor to be larger. Increases in the steepness tainty necessitates a greater monitoring effort to assure <br /> of the terrain,in the polarity of the constituent,in the that the attenuation factor setting process was suffi- <br /> amount of interconnection between ground and sur- ciently protective of water quality. <br /> face waters,in the concentrations of solvents or other Site-and constituent-specific information regard- <br /> chemicals that can act as carriers for the constituent, ing key environmental fate characteristics under rea- <br /> and in the total constituent loading will lower the at- sonable worst-case conditions may be used to estimate <br /> tenuation factor. attenuation factors for specific waste constituents at a <br /> Undoubtedly the most important characteristic that site. Publications such as The California Site Mitigation <br /> must be evaluated in the derivation of environmental Decision Tree Manual from DISC,The Soil Chemistry of <br /> attenuation factors is the relative uncertainty of the Hazardous Materials by James Dragun,the USEPA pub- <br /> data and assumptions used to quantify environmental lications Superfund Exposure Assessment Manual,Water <br /> fate processes. The more uncertainty involved in the Related Environmental Fate of the 129 Priority Pollutants <br /> estimation of environmental attenuation factors,the and DRASTIC:A Standardized System for Evaluating <br /> more the assumptions being used in their derivation Ground Water Pollution Potential Using Hydrogeologic <br /> should lean toward underestimating the amount of Settings, and the Handbook of Environmental Data on <br /> attenuation expected to occur. In this way,a greater Organic Chemicals by Karel Verschueren contain infor-° <br /> assurance of water quality protection is provided. The mation and/or procedures that can be used to assess <br /> degree of uncertainty in the estimation of environmen- the fate of chemicals in the environment and to esti- <br /> Central Valley Regional Water Quality Control Board Page 5 <br />
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