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ARCHIVED REPORTS_2005_4
Environmental Health - Public
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ARCHIVED REPORTS_2005_4
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Last modified
4/12/2022 3:00:48 PM
Creation date
7/3/2020 10:50:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2005_4 N&O 03-01+
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
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440005_9999 AUSTIN_2005_4.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:Per _ <br /> content ion exchange capacity or pH of vadose zone Clay Content and Porosity _ <br /> , Clay Content <br /> materials,and in the ionic strength,viscosity,de�ada- Organic Matter Content <br /> g 'J Ion Exchange Capacity and pH <br /> bility or octanol/water partition coefficient(the affinity PollutaPola taracteristics: <br /> y <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) <br /> • Other Constituents that Could Increase Mobility <br /> expected). Increases in the net recharge rate(a driving Topography(steepness of terrain) <br /> force for movement of waste constituents),in the per- Total Pollutant Load(mass loading) <br /> ) P 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 O laity <br /> Octanol/Water Partition Coefficient(Kow) <br /> (less attenuation ex ected as the constituent mi rates Other Constituents That Could Increase Mobility <br /> I' g Initial Dilution Upon Reaching Surface Waters <br /> t0 round water). (min,surface water flow vs.max.pollutant flow) <br /> g 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 DTSC,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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