| Preface to the second edition |
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xii | |
| Acknowledgement |
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xiv | |
| Contributors |
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xv | |
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1 | (9) |
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1 | (1) |
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Differences in national responses to land contamination |
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2 | (6) |
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Various national viewpoints |
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2 | (1) |
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The complexity of soil systems |
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3 | (2) |
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Identification of land contamination and necessary clean-up standards |
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5 | (2) |
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Variation in legislation and controls |
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7 | (1) |
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Signs of an international consensus |
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8 | (2) |
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Risks from contaminated land |
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10 | (18) |
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10 | (1) |
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What is 'contaminated land'? |
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11 | (1) |
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Estimating the amount of contaminated land |
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12 | (1) |
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Standards and criteria to establish if land is contaminated |
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13 | (4) |
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Risk assessment of ground contamination |
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17 | (3) |
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The development of legislation, policy and practices in the UK |
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20 | (5) |
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Netherlands policies and practices |
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25 | (1) |
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26 | (2) |
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Rational site investigations |
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28 | (50) |
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28 | (1) |
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Purposes of site investigation |
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29 | (6) |
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30 | (1) |
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Effects on the environment |
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31 | (2) |
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33 | (1) |
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34 | (1) |
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Site investigation strategy |
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35 | (1) |
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36 | (12) |
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36 | (3) |
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Recorded physical conditions |
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39 | (1) |
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Previous uses and contamination potential |
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40 | (4) |
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Preliminary conceptual model |
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44 | (1) |
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45 | (2) |
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47 | (1) |
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Designing an investigation |
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48 | (14) |
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48 | (1) |
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49 | (1) |
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50 | (3) |
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53 | (1) |
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54 | (1) |
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54 | (1) |
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Groundwater and surface water sampling |
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55 | (3) |
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58 | (1) |
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59 | (1) |
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60 | (2) |
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62 | (4) |
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62 | (1) |
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62 | (2) |
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Light cable percussion boreholes |
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64 | (1) |
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64 | (1) |
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Dynamic probes and small diameter boreholes |
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65 | (1) |
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65 | (1) |
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66 | (6) |
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66 | (1) |
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66 | (2) |
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68 | (1) |
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69 | (1) |
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70 | (1) |
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70 | (2) |
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Reporting and interpretation |
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72 | (4) |
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72 | (1) |
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73 | (2) |
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Assessment of targeted testing |
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75 | (1) |
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Assessment of water testing |
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75 | (1) |
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76 | (1) |
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76 | (2) |
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78 | (21) |
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78 | (1) |
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Reclamation choice in the United Kingdom |
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78 | (6) |
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Evolution of the UK's emphases on land contamination |
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78 | (3) |
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Challenges to current UK emphases |
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81 | (3) |
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Reclamation choices when health and environmental concerns dominate |
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84 | (3) |
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Engineering-based (broad spectrum) techniques |
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87 | (6) |
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87 | (1) |
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88 | (1) |
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Dilution of contamination |
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89 | (1) |
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90 | (1) |
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90 | (1) |
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91 | (2) |
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Innovative (narrow spectrum) techniques |
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93 | (5) |
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93 | (1) |
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Remediation of oily contamination |
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93 | (3) |
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Removal of cyanides and heavier hydrocarbon contamination |
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96 | (1) |
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Treatment of metal contaminated sites |
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97 | (1) |
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98 | (1) |
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99 | (29) |
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99 | (1) |
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100 | (12) |
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What does a cover have to do? |
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100 | (1) |
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How long does a cover have to remain effective? |
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101 | (1) |
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What materials can be included in a cover? |
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102 | (1) |
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Detailing the necessary material properties |
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103 | (4) |
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Quantifying the cover design |
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107 | (1) |
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Identifying possible failure mechanisms |
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108 | (3) |
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The time before any failure becomes apparent |
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111 | (1) |
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Ensuring that the client appreciates the design methodology and any liabilities this may imply |
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112 | (1) |
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112 | (1) |
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Covers intended to combat upward migration of contamination |
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113 | (6) |
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Designing a capillary break layer cover |
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113 | (3) |
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116 | (3) |
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Covers designed to minimize groundwater pollution |
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119 | (7) |
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119 | (1) |
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Rainfall infiltration and cover design |
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119 | (5) |
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124 | (2) |
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126 | (1) |
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Appropriate and non-appropriate applications of clean covers |
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126 | (2) |
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128 | (30) |
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128 | (2) |
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The requirements for a cut-off |
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130 | (1) |
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131 | (1) |
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Potentials tending to cause flow |
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132 | (1) |
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Types of vertical barrier |
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133 | (2) |
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134 | (1) |
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134 | (1) |
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Cut-and-fill type barriers |
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134 | (1) |
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The slurry trench process |
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135 | (1) |
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Types of slurry trench cut-offs |
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136 | (3) |
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Soil--active clay cut-offs |
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136 | (1) |
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136 | (1) |
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Clay--cement--aggregate cut-offs |
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137 | (1) |
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138 | (1) |
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139 | (1) |
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139 | (1) |
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139 | (1) |
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Requirements for the excavation slurry |
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140 | (2) |
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141 | (1) |
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141 | (1) |
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142 | (1) |
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142 | (1) |
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142 | (1) |
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Compatibility of materials |
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142 | (3) |
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142 | (2) |
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Cements and cement replacement materials |
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144 | (1) |
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145 | (1) |
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145 | (1) |
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Sample containers, storage and handling |
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146 | (1) |
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146 | (3) |
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146 | (1) |
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147 | (1) |
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148 | (1) |
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148 | (1) |
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Testing hardened properties |
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149 | (1) |
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Unconfined compression tests |
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149 | (1) |
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Confined drainage triaxial testing |
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149 | (1) |
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150 | (1) |
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Specifications for slurry trench cut-offs |
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150 | (4) |
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Mechanical performance: permeability |
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151 | (1) |
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152 | (1) |
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153 | (1) |
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153 | (1) |
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154 | (2) |
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155 | (1) |
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156 | (1) |
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156 | (1) |
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156 | (1) |
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156 | (2) |
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Reclaiming potentially combustible sites |
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158 | (19) |
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158 | (1) |
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158 | (4) |
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158 | (3) |
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161 | (1) |
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162 | (11) |
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162 | (1) |
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162 | (1) |
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Direct combustion testing |
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162 | (1) |
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163 | (1) |
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163 | (2) |
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Fire Research Station test method |
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165 | (1) |
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Combustion potential test |
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165 | (6) |
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171 | (2) |
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Use of the combustion potential test |
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173 | (2) |
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173 | (1) |
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174 | (1) |
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174 | (1) |
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174 | (1) |
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175 | (1) |
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175 | (1) |
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175 | (2) |
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Gas and vapour investigations |
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177 | (38) |
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177 | (1) |
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Principal subsurface gases and their properties |
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177 | (1) |
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Gas and vapour monitoring |
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178 | (10) |
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178 | (1) |
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Gas monitoring observation works |
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179 | (7) |
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Gaseous properties of importance |
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186 | (2) |
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Establishing most hazardous gassing conditions |
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188 | (6) |
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188 | (1) |
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Factors affecting landfill gas (and other degradation product gas) results |
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188 | (3) |
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Factors affecting the measurements of gases not generated by degradation |
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191 | (2) |
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193 | (1) |
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Gas and vapour survey procedures |
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194 | (5) |
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194 | (1) |
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Selecting observation hole locations |
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194 | (1) |
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Including more hazardous gassing conditions in gas and vapour surveys |
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195 | (2) |
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197 | (1) |
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197 | (2) |
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Solutions to subsurface gaseous contaminants |
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199 | (3) |
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199 | (2) |
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Gas source identification |
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201 | (1) |
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Legislative controls and official advice on redevelopment |
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202 | (2) |
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202 | (1) |
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203 | (1) |
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204 | (1) |
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204 | (9) |
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204 | (1) |
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Paper mill site, central Scotland |
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205 | (2) |
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Former steel mill site, West Midlands |
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207 | (2) |
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209 | (2) |
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Leisure development, London Docklands |
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211 | (2) |
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213 | (2) |
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Establishing new landscapes |
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215 | (21) |
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215 | (1) |
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216 | (6) |
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216 | (1) |
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217 | (2) |
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219 | (2) |
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221 | (1) |
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222 | (4) |
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222 | (1) |
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222 | (2) |
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224 | (2) |
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226 | (1) |
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227 | (1) |
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228 | (2) |
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Establishing trees and shrubs |
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230 | (2) |
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232 | (1) |
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233 | (1) |
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234 | (1) |
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235 | (1) |
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236 | (25) |
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236 | (1) |
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Sources of law relating to contaminated land |
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236 | (3) |
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Legislation: primary and subordinate |
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236 | (1) |
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237 | (1) |
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237 | (1) |
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Guidance Notes and Codes of Practice |
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238 | (1) |
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European Union regulations, decisions and directives |
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238 | (1) |
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Law relating to contaminated land |
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239 | (8) |
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239 | (1) |
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239 | (7) |
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246 | (1) |
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247 | (9) |
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Other relevant legislation |
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256 | (4) |
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256 | (1) |
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Government overall policy |
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256 | (1) |
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257 | (1) |
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257 | (2) |
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259 | (1) |
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260 | (1) |
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Introduction to waste management practices in the United States of America |
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261 | (27) |
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261 | (1) |
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Regulatory impetus for remediation |
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261 | (7) |
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Background on regulations |
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262 | (2) |
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264 | (1) |
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BDATs (Best Demonstrated and Available Technologies) |
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265 | (1) |
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Characteristic wastes versus listed wastes |
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266 | (2) |
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Phase II disposal role -- Universal Treatment Standards |
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268 | (1) |
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Regulation escalation and backlash |
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268 | (7) |
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The remediation process under CERCLA |
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275 | (7) |
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Preliminary assessment/site investigation |
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277 | (1) |
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Assignment to National Priority List |
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277 | (1) |
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Remedial investigation/feasibility study |
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277 | (2) |
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The remedy selection process |
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279 | (1) |
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Remedial action selection |
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280 | (1) |
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Remedial process selection |
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281 | (1) |
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Remedial design/remedial action |
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281 | (1) |
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281 | (1) |
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281 | (1) |
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282 | (1) |
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282 | (1) |
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Trends in remediation technology |
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282 | (1) |
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283 | (1) |
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284 | (1) |
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285 | (1) |
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Remediation business outlook |
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286 | (1) |
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286 | (2) |
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Netherlands' reclamation practices |
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288 | (13) |
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288 | (1) |
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Legal and administrative controls |
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288 | (2) |
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Private-sector initiatives |
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290 | (1) |
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Decision-making on contaminated sites |
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291 | (3) |
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291 | (1) |
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291 | (3) |
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Designing a risk assessment |
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294 | (2) |
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294 | (1) |
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294 | (1) |
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Ecotoxicological assessments |
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295 | (1) |
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295 | (1) |
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296 | (2) |
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296 | (1) |
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Remediation plan and specifications |
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297 | (1) |
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Regulation of excavated soils |
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297 | (1) |
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Soil remediation practices |
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298 | (2) |
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298 | (1) |
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298 | (1) |
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299 | (1) |
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300 | (1) |
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Effective management of contaminated land reclamations |
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301 | (28) |
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301 | (1) |
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301 | (4) |
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301 | (1) |
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Information to contractors |
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302 | (2) |
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304 | (1) |
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Contact with external bodies |
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304 | (1) |
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305 | (1) |
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Health and Safety at Work Regulations and Legislation |
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305 | (3) |
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305 | (1) |
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Breaches of Health and Safety Regulations |
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305 | (1) |
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Consequences of information limitations |
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306 | (2) |
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308 | (1) |
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The site investigation period |
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308 | (7) |
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308 | (2) |
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Information to be collected |
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310 | (1) |
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311 | (4) |
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Quality assurance of reclamations |
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315 | (13) |
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315 | (1) |
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315 | (7) |
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Appropriate quality systems |
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322 | (6) |
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328 | (1) |
| Appendix I Soil guidelines (UK) and Dutch Intervention Values |
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329 | (6) |
| Appendix II Semi-quantified risk assessment methodology |
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335 | (2) |
| Appendix III Other useful guidelines and standards |
|
337 | (21) |
| References |
|
358 | |