General Introduction | p. 1 |
Environmental technology | p. 1 |
The beginning | p. 1 |
The environmental effects of the oil industry | p. 2 |
Air emissions | p. 2 |
Water management | p. 5 |
Waste management | p. 7 |
Technology used in the oil industry | p. 10 |
Pollution control | p. 10 |
Pollution prevention | p. 12 |
Oil Industry future: design for the environment | p. 13 |
Design out the production problems | p. 13 |
Summary | p. 15 |
References | p. 15 |
Environmental Control Technology for Oilfield Processes | p. 17 |
Introduction | p. 17 |
Environmental control technology | p. 20 |
Evolution of environmentally controlled oilfield processes | p. 21 |
Scope and characteristics of oilfield ECT | p. 23 |
Methodology of ECT design | p. 25 |
ECT analysis of drilling process | p. 28 |
Mechanisms of drilling waste discharge | p. 28 |
Sources of drilling waste toxicity | p. 36 |
Waste generation mechanisms in petroleum production | p. 38 |
Sources of toxicity in produced water | p. 42 |
References | p. 48 |
Environmental Control of Well Integrity | p. 53 |
Introduction | p. 53 |
Mechanism of cement seal failures | p. 53 |
Improved cementing for annular integrity | p. 56 |
Cement pulsation after placement | p. 57 |
Integrity of injection wells | p. 60 |
Measurements of well integrity | p. 63 |
Sustained casinghead pressure | p. 65 |
Rig methods for SCP isolation | p. 66 |
Rig-less technology for SCP isolation | p. 68 |
References | p. 71 |
Environmental Control of Drilling Fluids and Produced Water | p. 77 |
Control of drilling fluid volume | p. 77 |
Control of mud dispersibility | p. 77 |
Improved solids-control-closed-loop systems | p. 79 |
Dewatering of drilling fluids: 'dry' drilling location | p. 82 |
Control of drilling fluid toxicity | p. 85 |
Drilling fluid toxicity testing | p. 85 |
Low-toxicity substitutes | p. 87 |
Synthetic base drilling fluids | p. 88 |
Source separation - drill cuttings de-oiling | p. 90 |
Control of produced water volume | p. 93 |
Source reduction - water shut-off technology | p. 94 |
Source separation-downhole oil/gas/water separation | p. 96 |
Source reduction with downhole water sink | p. 99 |
Control of produced water pollutants | p. 103 |
Oil-free water from DWS drainage-production systems | p. 104 |
Deoiling of produced water | p. 107 |
Removal of dissolved organics from produced water | p. 111 |
Produced water salinity reduction | p. 112 |
References | p. 113 |
Oilfield Waste Disposal Control | p. 123 |
Introduction | p. 123 |
Oilfield waste disposal to land | p. 124 |
Impact of oilfield pit contaminants | p. 124 |
Oilfield pit sampling and evaluation | p. 126 |
Oilfield pit closure: liquid phase | p. 127 |
Oilfield pit closure: solid phase | p. 127 |
Subsurface waste disposal to wells | p. 129 |
Description of slurry injection process of muds and cuttings | p. 133 |
Slurry fracture injection of muds and cuttings | p. 139 |
Properties of injected slurries | p. 144 |
Environmental implications of subsurface slurry injection | p. 145 |
Periodic injection to multiple fractures | p. 147 |
References | p. 151 |
Drilling and Production Discharges in the Marine Environment | p. 155 |
Introduction | p. 155 |
Nature of offshore discharges | p. 157 |
Produced water | p. 157 |
Drilling waste | p. 158 |
Magnitude of waste discharges | p. 160 |
Accidental discharges | p. 161 |
Wastes that require handling during site abandonment | p. 164 |
Potential impacts on the environment | p. 165 |
Introduction | p. 165 |
Potential impacts from produced water | p. 166 |
Potential impacts from drilling waste | p. 167 |
Potential impacts from treating chemicals | p. 168 |
Potential impacts from accidental discharges | p. 168 |
Regulatory approaches | p. 170 |
Regulations for waste discharges | p. 170 |
OSPAR agreements and national regulations for the OSPAR area | p. 171 |
United states regulations | p. 172 |
Comparing and contrasting OSPAR and United States EPA regulations | p. 174 |
Russian and former Soviet Republics regulations | p. 175 |
Other regulatory systems | p. 175 |
Accidental discharges | p. 175 |
Should the release be re-mediated? | p. 184 |
Sources of data on discharges to the marine environment | p. 185 |
References | p. 186 |
Decommissioning of Offshore Oil and Gas Installations | p. 189 |
Introduction | p. 189 |
Legal framework of platform decommissioning | p. 190 |
Planning | p. 195 |
Abandonment phases | p. 195 |
Well abandonment | p. 196 |
Preabandonment surveys/data gathering | p. 196 |
Engineering | p. 197 |
Decommissioning | p. 199 |
Structure removal | p. 201 |
Disposal | p. 209 |
Site clearance | p. 211 |
Conclusion | p. 212 |
References | p. 212 |
Tanker Design: Recent Developments from an Environmental Perspective | p. 215 |
Introduction | p. 215 |
Tanker accidents | p. 216 |
Tanker design | p. 219 |
New tanker design standards: the USA takes the lead | p. 220 |
New tanker designs: the international debate in the early 1990s | p. 221 |
Some developments since the adoption of the new MARPOL regulations in 1992 | p. 225 |
Some observations regarding the effectiveness of MARPOL's double hull requirements | p. 226 |
Epilogue | p. 227 |
References | p. 228 |
Pipeline Technology | p. 229 |
Introduction | p. 229 |
Environmental pressures | p. 231 |
Onshore pipelines | p. 232 |
Design | p. 233 |
Construction | p. 237 |
Operation | p. 250 |
Decommissioning | p. 256 |
Offshore pipelines | p. 256 |
Design | p. 256 |
Construction | p. 258 |
Operation | p. 265 |
Decommissioning | p. 267 |
Pipeline landfalls | p. 267 |
Design | p. 270 |
Construction | p. 279 |
References | p. 279 |
Environmental Management and Technology in Oil Refineries | p. 281 |
Function of an oil refinery | p. 281 |
Overview | p. 282 |
Control of atmospheric emissions | p. 283 |
Minimizing combustion-related emissions | p. 284 |
Minimizing flare-related emissions | p. 289 |
Minimizing fugitive emissions | p. 289 |
Odour control | p. 292 |
Sulphur removal and recovery | p. 293 |
Control of aqueous emissions | p. 295 |
Source control | p. 296 |
Effluent treatment | p. 298 |
Soil and groundwater protection | p. 301 |
Source control | p. 301 |
Monitoring | p. 302 |
Remediation | p. 303 |
Preventive techniques | p. 303 |
Control of solid wastes | p. 304 |
Source control | p. 304 |
Waste treatment | p. 306 |
Waste disposal | p. 308 |
Recycling to minimize waste | p. 311 |
Reuse on-site | p. 311 |
Off-site recycling | p. 311 |
Environmental management | p. 312 |
Environmental control | p. 312 |
Environmental training | p. 313 |
Environmental auditing | p. 314 |
References | p. 314 |
Distribution, Marketing and Use of Petroleum Fuels | p. 315 |
Introduction | p. 315 |
Main refinery product types | p. 315 |
Protection of the environment | p. 317 |
The atmosphere | p. 317 |
Sea waters: compliance with maritime regulations | p. 319 |
Soil and groundwater | p. 319 |
Distributing the products | p. 320 |
Distribution systems | p. 320 |
Anti-pollution controls | p. 322 |
The atmosphere | p. 322 |
The high seas | p. 322 |
Coastal and inland waterways | p. 324 |
Soil and groundwater | p. 325 |
Marketing the products | p. 327 |
Large industrial customer installations | p. 327 |
Small industrial and domestic customers | p. 328 |
Service stations | p. 328 |
Environmental technologies related to product use | p. 329 |
Fuels | p. 329 |
Marine diesel engines and fuels | p. 329 |
Fuels for large industrial power plants | p. 332 |
Fuels for small industrial and domestic installations | p. 332 |
Aircraft engines and fuels | p. 334 |
Engines for rail transport | p. 335 |
Automotive engines | p. 335 |
Into the next millenium | p. 347 |
Further reading | p. 347 |
Lubricants | p. 351 |
Introduction | p. 351 |
Performance | p. 353 |
Components | p. 353 |
Base fluids | p. 354 |
Mineral oils | p. 354 |
Synthetic base oils | p. 356 |
Polyol esters | p. 356 |
Poly-a-olefins | p. 356 |
Hydrocracked mineral oils | p. 357 |
Additives | p. 357 |
Actual environmental effects | p. 358 |
Biodegradability | p. 359 |
Biodegradation is not necessary in a lubricant | p. 360 |
A biodegradable lubricant will encourage dumping at the expense of collection and disposal | p. 360 |
A biodegradable lubricant will degrade in the engine | p. 360 |
A biodegradable lubricant will result in high concentrations of toxic residues that are detrimental to the environment | p. 361 |
Biodegradation is not necessary, as motor manufacturers are now producing sealed lubricant systems | p. 361 |
Collection and recycling of used oils | p. 361 |
Conclusion | p. 363 |
References | p. 364 |
Climate Change Scenarios and Their Potential Impact on World Agriculture | p. 367 |
What causes the climate system to change? | p. 367 |
Past climatic changes | p. 369 |
Anthropogenic forcing of the climate system | p. 372 |
Future changes in anthropogenic forcing | p. 374 |
Implications of SRES scenarios on global climate | p. 375 |
Temperature | p. 376 |
Precipitation | p. 377 |
Sea level rise | p. 378 |
Mitigation possibilities within the agricultural sector | p. 379 |
Implications of SRES scenarios on regional climate | p. 379 |
Europe | p. 379 |
North America | p. 385 |
Impacts of future climate change on agriculture | p. 385 |
Europe | p. 386 |
North America | p. 387 |
References | p. 388 |
Color Plates | p. 391 |
Index | p. 397 |
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