Protocol for the Derivation of Environmental and Human ... - CCME

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References Aldenberg, T., and W. Slob, (1991) Confidence Limits for Hazardous Concentrations Based on Logistically Distributed NOEC Data, RIVM, Bilthoven, The Netherlands, Report 719102002. Alder, V.J., L.J. Evans and G.A. Spiers, (1994) "Evaluation and Distribution of Master Variables Affecting Solubility of Contaminants in Canadian Soils", prepared for Environment Canada, Eco-Health Branch, Ottawa, Ontario, (unpublished). Angus Environmental Limited, May (1991) "Review and Evaluation of Receptor Characteritics for Multi-media Assessments, "Report prepared for Health and Welfare Canada, Monitoring and Criteria Division. Armstrong, V.C. and R.C. Newhook, (1992) "Assessing the Health Risks of Priority Substances Under the Canadian Environmental Protection Act", Regulatory Toxicology and Pharmacology 15: 111-121. ASTM (American Society for Testing of Materials) (1990a) "Standard Guide for Conducting Seed Germination and Root Elongation Soil Elutriate Chronic Toxicity Bioassay", Draft, Annual Book of ASTM Standards Committee E-47 on Biological Effects and Environmental Fate (E47.11.01 Plant Toxicology) p. 20. ASTM (American Society for Testing of Materials) (1990b) "Standard Guide for Conducting Seedling Emergence Toxicity Tests in Soils and Sediments from Hazardous Waste Sites", Draft, Annual Book of ASTM Standards. Committee E-47 on Biological Effects and Environmental Fate (E47.11.01 Plant Toxicology) p. 18. ASTM (American Society for Testing of Materials) (1991) Protocol for Toxicity Assessment with Tradescantia. Draft Report. Committee E-47 on Biological Effects and Environmental Fate (E47.11.01 Plant Toxicology) p. 29. Barkach, J. H., J. Dragun, and S. A. Mason, (1990) "Soil and Ground Water Clean-up Standards as Approached by the Michigan Department of Natural Resources", Environ. Professional. 12: 319-333. Beresford, N.A., and B.J. Howard, (1990) "The Importance of Soil Adhered to Vegetation as a Source of Radionuclides Ingested by Grazing Animals (sheep)", Sci. Tot. Environ. 107: 237- 254. Beyer, W. N., E. Conner, and S. Gerould, (1992) "Survey of Soil Ingestion Rates by Wildlife", J. of Wildl. Man. 108
References Bonnell, M., (1992) "Predicting the Relationship and Uncertainty Between No Observed Effect Concentration (NOEC) Data and Short-term Toxicity (E/LC50) for -Soil 109
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A Protocol for the Derivation of En
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Readers' Comments The Canadian Coun
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Overview In response to growing pub
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mechanisms for migration of soil co
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procédures d'élaboration des reco
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• être absorbés par les plantes
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PART B Section 1 Derivation of Envi
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Section 2 Investigation of Contamin
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PART D Section 1 Derivation of the
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List of Figures 1 National Framewor
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Acknowledgements The CCME Subcommit
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Document Organization This document
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Bioaccumulation: The process by whi
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Denitrification: The gaseous loss o
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GGG Guidelines: Generic numerical l
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Mutagenicity: The ability of a chem
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xxxiv human exposure. Risk estimati
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Soil: Normally defined as the uncon
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VVV Volatilization: The chemical pr
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Section 1 The National Contaminated
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Part A, Section 1 6
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Part A, Section 1 1.2.2.2 Remediati
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Part A, Section 1 of, and establish
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Part A, Section 2 Section 2 Nationa
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Part A, Section 2 2.2 Limitations o
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Part A, Section 2 17
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Part A, Section 2 Industrial: where
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• the sensitivity of the test con
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Part A, Section 3 23
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Section 2 Level of Ecological Prote
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Part B, Section 2 2.3 Endpoint Defi
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Part B, Section 2 There is consiste
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Part B, Section 4 Section 4 Potenti
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Part B, Section 4 Figure 4 Simplifi
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Figure 5 Key Receptors and Exposure
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Part B, Section 5 grazing herbivore
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Part B, Section 5 5.2.2 Maintenance
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Part B, Section 5 5.4 Industrial La
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Section 6 Uncertainty in Guidelines
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Section 7 Guidelines Derivation Pro
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Part B, Section 7 (SQG SG = soil qu
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Part B, Section 7 a soil quality gu
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Where: NPER = no to Potential Effec
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Part B, Section 7 7.5.2.1 Using Mic
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Part B, Section 7 data, the Median
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Part B, Section 7 EC 50 LC 50 UF =
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Where: ERL = Effects Range Low, ECL
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Part B, Section 7 Where: EC 50 = Me
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Part B, Section 7 Where the ECL lie
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Part B, Section 7 4. Fewer than thr
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Part B, Section 7 An uncertainty fa
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Part B, Section 7 Therefore, BCF =
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Part B, Section 7 ingestion (SQG I
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Section 8 Derivation of the Final E
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Part C, Section 1 65
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Part C, Section 1 various sites acr
Page 123 and 124: Part C, Section 1 Geographical unce
Page 125 and 126: preferred for the assessment, but s
Page 127 and 128: Part C, Section 2 73
Page 129 and 130: Part C, Section 2 Environmental con
Page 131 and 132: Part C, Section 2 extent, the steep
Page 133 and 134: Section 3 Exposure to Contaminants
Page 135 and 136: Part C, Section 3 81
Page 137 and 138: Part C, Section 4 Section 4 Exposur
Page 139 and 140: Part C, Section 4 within limits, th
Page 141 and 142: Part C, Section 4 Figure 19 Concept
Page 143 and 144: Part C, Section 4 4.2 Absorption of
Page 145 and 146: Part C, Section 4 In the case of no
Page 148 and 149: Residential/Parkland Land Use Sensi
Page 150 and 151: Part C, Section 4 Commercial Land U
Page 152: Part C, Section 4 Industrial Land U
Page 155 and 156: Part C, Section 5 these data are av
Page 157 and 158: Part C, Section 5 GEOCHEM (Mattigod
Page 159 and 160: Part C, Section 5 • K oc (sorptio
Page 161 and 162: Part C, Section 5 5.3.3 Evaluation
Page 163 and 164: Part C, Section 5 parameters, and s
Page 165 and 166: Section 6 Derivation of the Final H
Page 167 and 168: Part D, Section 1 101
Page 169 and 170: does not apply to the commercial or
Page 171: Part D, Section 1 105
Page 176 and 177: References -dwelling Organisms", Ab
Page 178 and 179: References 112
Page 180 and 181: References Hill, E.F., and D.J. Hof
Page 182 and 183: References Paustenbach, D.J., (1989
Page 184 and 185: References Summers, J.K., H.T. Wils
Page 186 and 187: Appendix A Appendix A Nutrient and
Page 188 and 189: Appendix A Figure A.1 Simplified Te
Page 190 and 191: Appendix A 4.1 Agricultural and Res
Page 192 and 193: Appendix A References Bååth, E.,
Page 194 and 195: The Subcommittee considers that exp
Page 196 and 197: Appendix B P l P r BW = percent pro
Page 198 and 199: Appendix B Substituting equation 5
Page 200 and 201: Appendix B Where no MRL exists, the
Page 202 and 203: Appendix B Then, the remainder (T R
Page 204 and 205: Appendix B For carcinogens, total i
Page 206 and 207: Appendix C Rearranging [2] and subs
Page 208 and 209: Appendix C References Chiou, C.T.,
Page 210 and 211: Appendix D uncontaminated organic m
Page 212 and 213: Appendix D R = recharge, m/yr A = a
Page 214 and 215: Appendix D 2.3.3 Hydraulic Gradient
Page 216 and 217: Appendix D 2.3.5 Site Length The le
Page 218 and 219: Appendix D Table D.2 Lower Quantile
Page 220 and 221: Figure D.2 Conceptual Model of Dilu
Page 222: Appendix D Figure D.3 Recharge Esti
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Appendix D 159
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Smith, A.E., P.B. Ryan, and J.S. Ev
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Appendix E C K L V is the climate f
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Appendix E contaminant concentratio
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Appendix F Appendix F Multi-media E
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Appendix F example, fish BCFs are t
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Appendix G 2.2 Contaminant Vapour T
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Appendix G Table G.1 Equations Used
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Appendix G at the outset that, rath
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Appendix G 4.4 Application of the R
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Average outdoor summer temperature
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Appendix G References Alberta Envir
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