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Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
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Index

A

Absorption, 110, 111

Acid-base reactions, 106-107, 131, 133-134, 152, 164, 177, 180, 182, 184-185, 194

Adenosine triphosphate, 83-84, 85

Adsorption, 81, 110

Advection, 78-80, 114, 135, 177, 180-184 (passim)

Agency for Toxic Substances and Disease Registry (ATSDR), 42, 53, 55-56, 57

Agent Orange, 43, 100

Air Force (U.S.), 29

case studies, 117-120, 122-127, 153

definition of natural attenuation, 23

protocols, 213, 220, 223, 226-227, 229, 232, 234-235, 238, 239, 240, 241, 244, 245

American Indians, see Native Americans

American Petroleum Institute, 33, 215, 230-231, 234-235

American Society for Testing and Materials, 33, 215, 229-230, 232, 234-235, 237-238, 240, 241

definition of natural attenuation, 23

Anaerobic processes, 74, 75, 84, 120, 127-128, 152, 165, 194, 228, 231

case studies, 115, 117, 120, 127

halogenated aliphatic compounds, 93-98

hydrocarbons, 86, 87-90, 91, 93, 115, 117

inorganic compounds, 101, 103, 104, 105

Aqueous complexation, 23, 109-110, 135

Army Science Board, definition of natural attenuation, 23

Arsenic, 9, 69, 89, 103, 139

ATP, see Adenosine triphosphate

ATSDR, see Agency for Toxic Substances and Disease Registry

B

Benzene, toluene, ethylbenzene, and xylene (BTEX), 5-6, 7, 13, 19, 21, 34, 68, 86, 87, 91-92, 138, 140

case studies, 115-117, 118, 126, 154

monitoring, 205, 208-209

protocols, 13, 221, 227-228

site modeling, 175, 181, 182-183, 184-185

Bhopal disaster (India), 43

Biodegradation, general, 22, 23, 31-32, 33, 65, 82-106, 127, 135, 138-139, 170, 171, 206-207

byproducts of chlorinated solvent biodegradation, 7, 39, 40, 127, 140, 167, 191, 228

vinyl chloride, 6, 32, 39, 85-86, 120, 167, 191-192

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

case studies, 115, 118, 120, 124, 127, 130-131, 153

chlorinated solvents, general, 10, 12, 73, 93-99

hydrocarbons, general, 31-32, 73, 86-93, 115, 118, 130-131, 138, 152, 153, 164-165, 184-185, 194, 196-197, 207

inorganic contaminants, 88-90, 101-106, 131, 139

mass budgeting, 175-177

protocols, 223-224, 228, 229

public opinion of, 40, 41

redox reactions, 82, 83, 107-108

site modeling, 10, 11, 12, 151, 152, 153, 164-165, 170, 171, 175-177, 181, 184-185, 191, 194, 196-197, 198

source removal, effects on, 73, 74, 75, 141

volatilization and, 84, 86, 102

see also Anaerobic processes

Brownfield programs, 27

Byproducts of natural attenuation, 7, 39, 40, 127, 140, 167, 192, 228

vinyl chloride, 6, 32, 39, 85-86, 120, 167, 191-192

C

California, leaking underground storage tanks, 30

Capping, 74

Case studies, 49, 71, 115-135, 136, 151, 152, 194, 200, 202, 229

Air Force sites, 117-120, 122-127, 153

anaerobic processes, 115, 117, 120, 127

BTEX, 115-117, 118, 126, 153

biodegradation, 115, 118, 120, 124, 127, 130-131, 152, 153

chlorinated solvents, 119-126

Coast Guard site, 115-117

Department of Energy (Hanford), 134-135, 136

documentation requirements, 115, 117

footprints, 117, 124, 151, 153

metal pollutants, 131-133, 153

plume factors, 115-117, 118-119, 120, 122-123, 129, 130, 131, 133-135, 136

pump-and-treat approach, 115

redox reactions, 120, 127, 133-134

sampling techniques, 119, 120, 122, 129, 134

Chemical oxygen demand, 119, 120, 129, 151

Chevron Corp., 33, 215, 229, 234-235

Children, 42, 58

Chlorinated solvents, 6, 68, 71, 107, 162

biodegradation, general, 10, 12, 73, 93-99

byproducts of biodegradation, 7, 39, 40, 127, 140, 167, 191, 228

vinyl chloride, 6, 32, 39, 85-86, 120, 167, 191-192

case studies, 119-126

DCA, 68, 124

DCE, 112, 120, 124, 126, 191

dechlorination, 75, 93, 95, 97, 99, 107-108, 114, 120, 127, 128, 151, 152, 166-167, 168, 223, 227, 192-193

engineering remediation, 73, 74

footprints, 12, 124, 166-171, 207-208

halogenated alphatics, general, 68

PCE, 68, 93, 95, 96-97, 114, 119-120, 227

protocols, 13, 16, 23, 214, 215, 219, 220, 222-244 (passim), 249, 251

source removal, 73, 74-76

state regulations, 16, 228-229, 232

TCA, 112, 123-127, 138, 152, 167, 245

TCE, 6, 32, 39, 42, 45, 48, 93, 94, 95, 97, 114, 120-127, 138, 151, 152, 153, 166-167, 170-171, 191-192, 227, 245

Chromium, 9, 69, 89, 102-103, 109

Citizen advisory committees, 56, 57

Citizen’s Environmental Coalition, 33

Classification exception areas, 229, 233, 236

Coast Guard, case study, 115-117

Co-contaminants, 10

Cometabolism, 84, 171

Community advisory groups, 53-54, 56, 57

Community participation, 3-5, 14, 16-17, 37, 38, 48-61, 234-235

citizen advisory committees, 56, 57

community advisory groups, 53-54

cost of cleanups, 3, 24, 38, 39, 41, 53, 61

Department of Defense efforts, 4, 57-58, 60

documentation, 2-3, 5, 38-41, 58, 61

economic factors, other than costs of cleanups, 41, 45-46, 50, 233, 236

education of public, 49, 53, 55, 60-61, 232, 236, 247-248, 253

EPA efforts, 5, 50, 51, 56-57, 61, 233-235

funding for, 39, 57

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

health effects, 37, 41, 42-45, 47, 48, 58

historical perspectives, 43, 50, 54, 59

institutional controls, 5, 39, 40, 50

language factors, 5, 55

leaking underground storage tanks, 53-54

metal pollutants, 40

mixtures of contaminants, 39, 45

monitoring of sites, 39, 40-41, 48, 52, 58

protocols, 14, 16-17, 55-56, 216, 217, 229, 232, 233, 234, 236-238, 247-248, 251, 252, 253

psychological factors, 41, 46-48, 58

regulatory issues, 3-5, 47-48, 53, 55, 59-61, 236

Resource Conservation and Recovery Act, 50

state-level actions, 50

Superfund sites, 33-34, 42, 43, 50, 51-52, 60

timing and other time factors, 5, 39, 40, 41, 45, 49, 50, 52, 58, 236

see also Public opinion;

Social factors

Comprehensive Environmental Response, Compensation, and Liability Act, see Superfund

Contingency planning, 16, 21-22, 217, 218, 234, 237-238, 251, 252

funding, 39

Cost factors, 22, 24

community concerns/participation, 3, 24, 38, 39, 41, 53, 61

engineering bioremediation, 20, 24, 39, 41

protocol, training regarding, 18, 254

site modeling, 154, 161-162

see also Funding

Cultural factors, 5, 55

language factors, 5, 55

Native Americans, 46

D

Dechlorination, 75, 93, 95, 97, 99, 107-108, 114, 120, 127, 128, 151, 152, 166-167, 168, 223, 227, 192-193

Dense nonaqueous-phase liquids, 69, 71, 72

TCE, 6, 32, 39, 42, 45, 48, 93, 94, 95, 97, 114, 120-127, 138, 151, 152, 153, 166-167, 170-171, 191-192, 227, 245

Department of Defense, community concerns/participation, 4, 57-58, 60

Department of Energy, 105

Hanford site, 134-135, 136

model evaluation, 202-203

protocols, 13, 214, 224-226, 232-233, 234-235, 242, 244, 251, 253

uranium mill tailings sites, 32

Desorption, 23

Dichloroethane (DCA), 68, 124

Dichloroethene (DCE), 112, 120, 124, 126, 191

Dilution, 2, 22, 23, 34, 40, 221

community concerns, 38, 58

Diseases and disorders, see Health effects

Dispersion, 22, 23, 40, 80-81, 78, 79, 114, 135, 180, 221

community concerns, 38

Dissolution reactions, see Precipitation and dissolution reactions

DNA, 82-83

DNAPLs, see Dense nonaqueous-phase liquids

Documentation, 1, 7, 10-12, 150, 207

case studies, 115, 117

community participation, 2-3, 5, 38-41, 58, 61

see also Models and modeling;

Monitoring requirements;

Protocols;

Sampling

Draft Guidelines: Natural Attenuation of Chlorinated Solvents in Groundwater, 228

Draft Region 4 Suggested Practices for Evaluation of a Site for Natural Attenuation (Biological Degradation) of Chlorinated Solvents, 223

E

Economic factors

community concerns/participation, 41, 45-46, 50, 233, 236

see also Cost factors;

Funding

Education and training

professional, 55

protocols, 14-15, 17, 18, 226, 242, 245-248, 254

public, 49, 53, 55, 60-61, 232, 236, 247-248, 253

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

Epidemiologic studies, 44, 45

Engineered bioremediaton, 20, 60, 74-76

capping, 74

chlorinated solvents, 73, 74

costs of, 20, 24, 39, 41

excavation, 20, 74

limitations of, 29, 25-26, 74-76

protocols, 240, 252

pump-and-treat approach, 20, 24, 24, 74, 115

see also Source zones and source removal

Environmental Protection Agency, 5

community participation, 5, 50, 51, 56-57, 61, 233-235

definition of natural attenuation, 23

Office of Solid Waste and Emergency Response, 56-57

protocols, 15-18, 33, 214, 221-224, 226, 227, 230, 231, 232, 233, 236-244 (passim), 246, 248, 250-254 (passim)

RCRA Corrective Action Program, 29

Toxic Substances Control Act Chemical Inventory, 25

see also Superfund

Evaporation, see Volatilization

Evidence, see Documentation;

Monitoring requirements;

Sampling

Ethylbenzene, see Benzene, toluene, ethylbenzene, and xylene (BTEX)

Europe, 42

Excavation, 20, 74

F

Federal government, 221-228, 247, 254

Agency for Toxic Substances and Disease Registry (ATSDR), 42, 53, 55-56, 57

Army Science Board, 23

Coast Guard, 115-117

Occupational Safety and Health Administration, 247

Geological Survey, 227

see also Air Force (U.S.);

Navy (U.S.);

Department of Defense;

Department of Energy;

Environmental Protection Agency;

Footprints, 10-12, 19, 114, 117, 124, 151-154, 188, 191, 205, 206-207

case studies, 117, 124, 151, 153

chlorinated solvents, 12, 124, 166-171, 207

hydrocarbons, 163-165, 207

mass budgeting, 159-160, 172, 173, 175-177, 180-185, 186, 187-188, 194, 199, 201-203, 206, 230

models, 154, 163-171

monitoring requirements, 151-154, 163-171

petroleum hydrocarbons, 163-165, 167, 167-171 (passim)

reaction, 163-171

sampling approaches, 151, 152

see also Plume factors

Funding

community participation, 39, 57

contingency plans, 39

see also Cost factors

G

Geological Survey (U.S.), 227

Guide for Remediation of Ground Water by Natural Attenuation at Petroleum Release Sites, 229-230

H

Halogenated aliphatic compounds, 8, 68, 87, 93-98, 138

Halogenated aromatic compounds, 8, 68, 87, 98-100, 138

polychlorinated biphenyls (PCBs), 43, 68, 88, 99-100, 127-128, 138, 153, 233, 251

Hanford site (Washington), 134-135, 136

Health effects, 2, 3, 5, 6, 7, 9, 10, 19, 128

carcinogens, 32, 42, 45;

see also specific carcinogens

children, 42, 58

community concerns/participation, 37, 41, 42-45, 47, 48, 58

DNA, 82-83

epidemiologic studies, 44, 45

protocols and, 13, 15, 235-236;

see also Institutional controls

Heavy metals, see Metal pollutants

Historical perspectives, 20, 25, 26

case studies, 49, 71, 115-135, 151, 152, 153, 194, 200, 202, 229

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

community concerns/participation, 43, 50, 54, 59

intrinsic bioremediation/natural attenuation, general, 20, 21-22, 25, 26, 26-31, 32-33

protocols, 222

HMX, see Octahydro-1,3,5,7tetranitro-1,3,5,7-tetrazocene

Houston, Texas, 24

Hudson River, case study, 127-128, 153

Hydrocarbons, 8, 29, 66, 68, 138

anaerobic processes, 86, 87-90, 91, 93, 115, 117

biodegradation, general, 31-32, 73, 86-93, 115, 117, 115, 118, 130-131, 138, 152, 153, 164-165, 184-185, 194, 196-197, 207-208

footprints, 163-166, 207-208

oxygenated hydrocarbons, 8, 68, 87, 92-93, 138

MTBE, 29, 68, 92-93, 117-119, 138, 153

polycyclic aromatic hydrocarbons (PAHs), 71-72, 92, 128-131, 138, 153, 233, 251

protocols, 13, 215, 219, 221, 227-228, 230-231

source removal, 73

see also Petroleum hydrocarbons

Hydrogeologic processes, 12, 14, 24, 65, 66-69, 73, 76-78, 128, 137

protocols, 14, 218-219, 222, 235, 239, 251

site modeling, 155-157, 163-165, 168, 173, 174, 184, 185-200, 205-207

see also Plume factors;

Transport processes

Hydrolysis, 106, 112

I

Immobilization processes, 1, 4, 7-10 (passim), 18-19, 34, 65-66, 88, 89, 90, 134-135, 137, 225-226

capping, 74

In Situ Bioremediation: When Does It Work?, 21

Interstate Technology Regulatory Cooperation Work Group, 246, 247, 249

Institutional controls

community opinion/participation, 5, 39, 40, 50

protocols, 14, 216-217, 224, 229, 234, 236-237, 251

Intrinsic bioremediation, see Natural attenuation/intrinsic bioremediation, general

L

Landfills, 20, 21, 42-43, 44, 48, 66, 68, 69, 201, 227

property values in vicinity of, 45-46

Language factors, community participation, 5, 55

Lawrence Livermore National Laboratory, 26, 29

Leaking underground storage tanks, 18, 26, 27-30, 69

community involvement, 53-54

monitoring of specific sites, 151

protocols, 18, 221, 250

Legislation, 1

Comprehensive Environmental Response, Compensation, and Liability Act, see Superfund

Resource Conservation and Recovery Act, 18, 26, 27, 29, 50, 221, 249, 250, 253

Toxic Substances Control Act, 25

Uranium Mill Tailings Remediation Control Act, 27, 32

see also Regulatory issues;

Superfund

Light nonaqueous-phase liquids (LNAPLs), general, 69, 71, 72

Love Canal, 20, 27, 42, 236

M

Massachusetts Department of Public Health, 42, 45

Mass balance/budgeting, 159-160, 172, 173, 175-177, 180-185, 186, 187-188, 194, 199, 201-202, 206, 230

Mass media, 42, 43, 55

Mercury, 9, 69, 89, 103

Metal pollutants, 6-10 (passim), 32, 66, 69, 81, 88-89, 102-103, 107-111, 114, 139, 140, 171

case studies, 131-133, 153

chromium, 9, 69, 89, 102-103, 109

community concerns, 40

mercury, 9, 69, 89, 103

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

Methods for Measuring Indicators of Intrinsic Bioremediation, 230-231

Methyl tert-butyl ether (MTBE), 29, 68, 92-93, 117-119, 138, 153

Michigan, Superfund sites, 43, 44

Microorganisms, see Biodegradation

Mine tailings, 32, 69

Minnesota, 215, 227, 228, 232, 234-234, 243, 244

Minorities, Native Americans, 46

Mixtures of contaminants, 6, 10, 66, 127, 137, 171, 174, 206, 219, 223, 224, 226, 243, 248

community concerns, 39, 45

Models and modeling

constructed models, 159-160

Department of Energy evaluation efforts, 202-203

footprints, 154, 163-171

laboratory studies, 192, 193

realizations, 157-159, 160

quality control for, 195, 198-203

site, 10, 11, 12, 151, 152, 154-171, 172, 173, 175-177, 180, 184-200, 205, 206, 223

biodegradation, general, 10, 11, 12, 151, 152, 153, 164-165, 170, 171, 176-177, 180, 184-185, 191, 194, 196-197, 198

BTEX, 176, 181, 182, 183

costs, 154, 161-162

hydrogeologic processes, 155-157, 163-165, 168, 173, 174, 184, 185-200, 205-206

NAPLs, 156, 157, 161-162, 165, 175, 180-181, 184-185, 187, 201

plume factors, 162-163, 168-170, 181, 202, 207

regulatory issues, 165, 208

statistical analyses, 162, 172, 173, 174-176, 178-179, 187-188, 195, 202, 204

solute transport, 154-171, 172, 173, 185-200, 208

sorption, 112

vadose zone, 77

Monitoring requirements, x, 5, 11, 12, 116, 140, 150, 203-204, 209-210

BTEX, 204, 208-209

community concerns/participation, 39, 40-41, 48, 52, 58

footprints, 151-154, 163-171

leaking underground storage tanks, 151

protocols, 14, 16, 204, 210, 221-222, 234, 236-237

redox reactions, 82, 83, 107-108

see also Models and modeling;

Sampling;

Sustainability

MTBE, see Methyl tert-butyl ether

N

National Contingency Plan (1990), 21-22

National Environmental Justice Advisory Council, 55

National Ground Water Association, 246

National Stakeholders’ Forum on Monitored Natural Attenuation, 41

Native Americans, 46

Natural attenuation/intrinsic bioremediation, general, 21

defined, 1, 21, 22, 23, 34, 39-40

efficacy of, specific pollutants/ processes, 8-9

extent of, 1, 26-32

historical perspectives, 20, 21-22, 25, 26, 26-31, 32-33

Natural Attenuation of Chlorinated Solvents in Groundwater: Principles and Practices, 231

Navy (U.S.)

protocols, 214, 220, 227-228, 232, 234-235, 238, 240, 244

source removal, 72-73

New Jersey, 43, 215, 228-229, 233, 234-235, 236

Niagara Falls, New York, see Love Canal

Nitroaromatic compounds, 8, 68, 88, 101, 138

Nonaqueous-phase liquids (NAPLs), 69, 71, 73, 78, 113

protocols, 229, 237, 239

site modeling, 156, 157, 161-162, 165, 175-176, 177, 180, 181, 184-185, 187, 203

see also Dense nonaqueous-phase liquids;

Light nonaqueous-phase liquids;

specific NALPs

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

O

Occupational Safety and Health Administration, 247

Octahydro-1,3,5,7tetranitro-1,3,5,7-tetrazocene (HMX), 101

Office of Solid Waste and Emergency Response (EPA), 56-57

Oxyanions, 9, 69, 89, 104-105, 139

Oxygenated hydrocarbons, 8, 68, 87, 92-93, 138

MTBE, 29, 68, 92-93, 117-119, 138, 153

P

P1, see Inorganic phosphorus

Parsons Engineering Science, Inc., 226, 227

PCE, see Tetrachloroethylene

Peer review, 13, 14, 15, 17, 18, 217, 220, 232, 235, 241, 253

Petroleum hydrocarbons, 31-32, 86, 87, 91-92, 153, 194, 196-197, 207

American Petroleum Institute, 33, 215, 230-231, 234-235

engineering remediation, effects of, 73, 74-76, 86, 87

footprints, 163-165, 166, 168-171 (passim)

protocols, 16, 23, 31-32, 215, 221, 227, 229-231, 232, 238, 234-235

polycyclic aromatic hydrocarbons (PAHs), 71-72, 92, 128-131, 138, 153, 233, 251

see also Benzene, toluene, ethylbenzene, and xylene;

Leaking underground storage tanks

Phase transfers, 78, 81-82, 114, 181, 187-188

see also Soprtion;

Volatilization

pH levels, see Acid-base reactions

Pitman, New Jersey, 43

Plume factors, 12, 26, 29, 32, 66-67, 70, 71, 72, 97, 163-164

case studies, 115-117, 118-119, 120, 122-123, 129, 130, 131, 133-135, 136

protocols, 221, 226, 227, 228, 236

public opinion, 38

site models, general, 162-163, 168-170, 181, 202, 207

see also Footprints;

Transport processes

Political factors, 22, 24

Polychlorinated biphenyls (PCBs), 43, 68, 88, 99-100, 127-128, 138, 153, 233, 251

Polycyclic aromatic hydrocarbons (PAHs), 71-72, 92, 128-131, 138, 153, 233, 251

Precipitation and dissolution reactions, 103, 105, 106, 107-109, 114, 133, 135

Property values, see Economic factors

Protocol for Monitoring Bioremediation in Groundwater, 229

Protocol for Monitoring Natural Attenuation of Chlorinated Solvents in Groundwater, 229

Protocols, 2, 13-19, 32-33, 204, 213-254, 258

Air Force, 213, 220, 223, 226-227, 229, 232, 234-235, 238, 239, 240, 241, 244, 245

American Petroleum Institute, 33, 215, 230-231, 234-235

American Society for Testing and Materials, 33, 215, 229-230, 232, 234-235, 237-238, 240, 241

biodegradation, general, 223-224, 228, 229

BTEX, 13, 221, 227-228

chlorinated solvents, general, 13, 16, 23, 214, 215, 219, 220, 222-244 (passim), 249, 251

community involvement, 14, 16-17, 55-56, 216, 217, 229, 232, 233, 234, 236-238, 247-248, 251, 252, 253

contingency plans, 16, 217, 218, 222, 234, 237-238, 251, 252

cost of training, 18, 254

criteria for appropriate, 216-220, 252

defined, 213

Department of Energy, 13, 214, 224-226, 232-233, 234-235, 242, 244, 251, 253

education and training, 14-15, 17, 18, 226, 242, 245-248, 254

engineered bioremediation, 240, 252

EPA, 15-18, 33, 214, 221-224, 226, 227, 230, 231, 232, 233, 236-244 (passim), 246, 248, 250-254 (passim)

health effects, 13, 15, 235-236;

see also Institutional controls

historical perspective, 222

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

hydrocarbons, general, 13, 215, 219, 221, 227-228, 230-231

hydrogeologic processes, 14, 218-219, 222, 235, 239, 251

institutional controls, 14, 216-217, 224, 229, 234, 236-237, 251

leaking underground storage tanks, 18, 221, 250

monitoring requirements, 14, 16, 205, 210, 221-222, 234, 236-237

NAPLs, general, 229, 237, 239

Navy, 214, 220, 227-228, 232, 234-235, 238, 240, 244

overview of, 220-242

peer review, 13, 14, 15, 17, 18, 217, 220, 232, 235, 241, 253

petroleum hydrocarbons, 16, 23, 31-32, 215, 221, 227, 229-231, 232, 238, 234-235

plume factors, 221, 226, 227, 228, 236

regulatory issues, 15, 16-17, 213, 229, 233, 234-235, 236, 239, 247, 248-251, 254

RCRA, 221, 249, 250, 253

scoring systems, 15, 223, 242, 243-245, 253

social factors, 14, 16-17, 234-235

solute transport models, 195, 198-200

source removal, 235

state efforts, 29, 31, 33, 213, 215, 227, 228-229, 232, 233, 234-235, 236, 243, 244, 247, 248-250, 252-253, 254

Superfund, 221-222, 244, 249, 253

sustainability issues, 2, 13, 14, 17, 18, 217, 219, 224, 226, 237, 239-240, 251-252, 253

Psychological factors, 41, 46-48, 58

Public education, 49, 55, 60-61, 232, 236, 247-248, 253

Public opinion, x, 3-4, 24, 33-34, 37-48, 52-53, 54, 58-59

biodegradation, general, 40, 41

citizen advisory committees, 56, 57

dilution/dispersion approaches, 38, 58

health effects, 37, 41, 42-45, 47, 48, 58

mass media, 42, 43, 55

plumes, 38

psychological factors, 41, 46-48, 58

volatilization approaches to remediation, 38

see also Community participation

Pump-and-treat approach, 20, 24, 24, 74

case study, 115

R

Radioactive decay, 22, 23, 112-113

Radionuclides, 9, 32, 66, 69, 81, 89-90, 105-106, 134-135, 136, 139, 152, 153, 179, 226

Redox reactions, 82, 83, 91, 93, 97, 99, 103, 104, 105-106, 107-108, 114

biodegradation, general, 82, 83, 107-108

case studies, 120, 127, 133-134

monitoring, 151, 152, 164, 166, 174, 191-192, 196

Regulatory issues, 1-2, 26, 29, 31, 34

chlorinated solvents, 16, 228-229, 232

classification exception areas, 229, 233

community concerns/participation, 3-5, 47-48, 53, 55, 59-61, 236

funding for engineering remediation, 39

Interstate Technology Regulatory Cooperation Work Group, 246, 247, 249

leaking underground storage tanks, 29

protocols, 15, 16-17, 213, 229, 233, 234-235, 236, 239, 247, 248-251, 254

site modeling requirements, 165, 208

source removal/containment, 71

see also Environmental Protection Agency;

Legislation

Remediation Technologies Development Forum (RTDF), 215, 231, 233, 234-235, 238, 241, 243, 244

Resource Conservation and Recovery Act (RCRA), 18, 29

community participation, 50

leaking underground storage tanks, 18, 26, 27

protocols, 221, 249, 250, 253

Restoration advisory boards, 4, 57-58, 60

Rivers, 127-128, 153

S

Sampling, 10, 11, 150, 174, 195, 230-231

case studies, 119, 120, 122, 129, 134

errors, 176, 181

footprints and, 151, 152

health effects, sample size, 45

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

plume delineation, 162-163

professional training in, 247

Scoring systems, 15, 223, 242, 243-245, 253

Selenium, 9, 69, 89, 104, 109, 139

Site Screening and Technical Guidance for Monitored Natural Attenuation at DOE Sites, 224-226

Social factors, 3-4

cultural factors, 5, 46, 55

language factors, 5, 55

political factors, 22, 24

protocols and, 14, 16-17, 234-235

psychological factors, 41, 46-48, 58

public education, 49, 55, 60-61, 232, 236, 247-248, 253

see also Community participation;

Public opinion

Solvents, 6, 66, 68, 239

cosolvents, 73, 76

see also Chlorinated solvents

Sorption, 22, 23, 81, 88, 100, 102, 106, 110-112, 131, 135, 221

adsorption, 81, 110

desorption, 23

site modeling, 192

Source zones and source removal, 10, 12, 14, 18, 23, 41, 58, 66, 68, 69-78, 140

biodegradation, effects of removal, 73, 74, 75, 141

chlorinated solvents, general, 73, 74-76

protocols, 235

regulatory issues, 71

site modeling, 160-162

South Glen Falls, New York, 128-131

Spatial factors, 156-157

site modeling, 156-157

see also Footprints;

Plume factors

Standard Guide for Remediation of Groundwater by Natural Attenuation at Petroleum Release Sites, 23

State-level actions, 16, 29, 31

chlorinated solvents, 16, 228-229, 232

community participation, 50

leaking underground storage tanks, 28

protocols, 29, 31, 33, 213, 215, 227, 228-229, 232, 233, 234-235, 236, 243, 244, 247, 248-250, 252-253, 254

site modeling requirements, 166

Superfund programs, 3, 27, 33-34, 43, 44

voluntary cleanup/brownfield programs, 27

see also Regulatory issues

Statistical analyses

health effects, 45

time-series analyses, 162, 174, 178

site modeling, 162, 172, 173, 174-176, 178-179, 187-189, 195, 202

St. Joseph, Michigan, 120-121

Storage tanks, see Leaking underground storage tanks

Superfund (Comprehensive Environmental Response, Compensation, and Liability Act), 3, 18, 20, 21-22, 27, 29, 31

community concerns/participation, 33-34, 42, 43, 50, 51-52, 60

health threats, 42-43

protocols, 221-222, 244, 249, 253

remedial process, steps involved, 51-52

state programs, 3, 27, 33-34, 43, 44

Superfund Community Relations Handbook, 50

Sustainability issues, 2, 10, 13, 14, 17, 18, 73, 97, 103, 104, 106, 165, 172, 201-203, 205, 206, 208

protocols, 2, 13, 14, 17, 18, 217, 219, 224, 226, 237, 239-240, 251-252, 253

see also Monitoring

Sveso, Italy, 43

T

TCA, see Trichloroethane

TCE, see Trichloroethene

Technical Assistance for Public Participation, 57-58

Technical Guidelines for Evaluating Monitored Natural Attenuation, 227-228

Technical Protocol for Evaluating Natural Attenuation of Chlorinated Solvents in Ground Water, 222-223

Technical Protocol for Implementing Intrinsic Remediation with Long-Term Monitoring for Natural Attenuation of Fuel Contamination in Groundwater, 226

Temporal factors, see Time factors

Tetrachloroethene (PCE), 68, 93, 95, 96-97, 114, 119-120, 227

Tetrachlorodibenzo-p-dioxin (TCDD -Agent Orange), 43, 100

Suggested Citation:"Index." National Research Council. 2000. Natural Attenuation for Groundwater Remediation. Washington, DC: The National Academies Press. doi: 10.17226/9792.
×

Time factors, 7

community concerns/participation, 5, 39, 40, 41, 45, 49, 50, 52, 58, 236

definition of natural attenuation, 23

health effects, 45

monitoring, 140, 162, 174, 178, 203-204, 206-207, 229, 234

radioactive decay, 113

site modeling, 156-157, 162, 174, 178, 194

sorption, 111

source removal effects, 73, 76-77

Time-series analyses, 162, 174, 178

TNT, see Trinitrotoluene

Toluene, see Benzene, toluene, ethylbenzene, and xylene (BTEX)

Toxic Substances Control Act, 25

Training, see Education and training

Transport processes, 70, 78-82, 185-200

advection, 78-80, 114, 135, 175-177, 180-183 (passim)

dispersion, 22, 23, 38, 40, 80-81, 78, 79

[ALL]

see also Plume factors;

Sorption

Trichloroethane (TCA), 112, 123-127, 138, 152, 167, 245

Trichloroethene (TCE), 6, 32, 39, 42, 45, 48, 93, 94, 95, 97, 114, 120-127, 138, 151, 152, 153, 166-167, 170-171, 191-192, 227, 245

Trinitrotoluene (TNT), 32, 68, 101, 138

U

Underground storage tanks, see Leaking underground storage tanks

Uranium Mill Tailings Remediation Control Act, 27, 32

Use of Monitored Natural Attenuation at Superfund, RCRA Corrective Action, and Underground Storage Tank Sites, 221

U.S. Geological Survey, see Geological Survey (U.S.)

V

Vietnam, Agent Orange, 43

Vinyl chloride (VC), 6, 32, 39, 68, 94, 114, 120, 124, 126, 138, 167, 191-192

Volatilization, 2, 22, 23, 40, 81-82, 89, 103, 135, 180, 181, 221

biodegradation, 84, 86, 102

public opinion, 38

W

Woburn, Massachusetts, 42, 45

X

Xylene, see Benzene, toluene, ethylbenzene, and xylene (BTEX)

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In the past decade, officials responsible for clean-up of contaminated groundwater have increasingly turned to natural attenuation-essentially allowing naturally occurring processes to reduce the toxic potential of contaminants-versus engineered solutions. This saves both money and headaches. To the people in surrounding communities, though, it can appear that clean-up officials are simply walking away from contaminated sites.

When is natural attenuation the appropriate approach to a clean-up? This book presents the consensus of a diverse committee, informed by the views of researchers, regulators, and community activists. The committee reviews the likely effectiveness of natural attenuation with different classes of contaminants-and describes how to evaluate the "footprints" of natural attenuation at a site to determine whether natural processes will provide adequate clean-up. Included are recommendations for regulatory change.

The committee emphasizes the importance of the public's belief and attitudes toward remediation and provides guidance on involving community stakeholders throughout the clean-up process.

The book explores how contamination occurs, explaining concepts and terms, and includes case studies from the Hanford nuclear site, military bases, as well as other sites. It provides historical background and important data on clean-up processes and goes on to offer critical reviews of 14 published protocols for evaluating natural attenuation.

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