Environmental Management: Principles and practice
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5 2020 03 04!03 12 11 PM
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- A brief history of pollution and waste problems 208 ♦ Pollution and waste associated with urbanization 210
- Electromagnetic radiation (non-ionizing) 221 ♦ Coping with pollution and waste 222 ♦ Agricultural pollution and waste 224
Recommended reading
Journals which publish articles on environmental management of difficult and vulnerable environments Arctic and Alpine Research Desertification Control Bulletin Journal of Arid Environments Journal of Range Management Journal of Tropical Geography (Singapore) Land Degradation & Development Mountain Research & Development Savannah Society & Natural Resources 205 C h a p t e r 1 1 Pollution and waste management ♦ A brief history of pollution and waste problems 208 ♦ Pollution and waste associated with urbanization 210 ♦ Industrial waste and pollution (non-radioactive) 216 ♦ Radioactive waste and pollution 220 ♦ Electromagnetic radiation (non-ionizing) 221 ♦ Coping with pollution and waste 222 ♦ Agricultural pollution and waste 224 ♦ Recycling and re-use of pollution and waste 231 ♦ Recommended reading 233 206 This chapter gives a broad introduction to pollution and waste management. The following Routledge Environmental Management Series text offers further coverage: A.Farmer (1998) Managing Environmental Pollution Pollution can be defined as the introduction by humans, deliberately or inadvertently, of substances or energy (heat, radiation, noise) into the environment— resulting in a deleterious effect (O’Riordan, 1995). Contamination is the presence of elevated concentrations of substances in the environment, food, etc., which may not necessarily be harmful or a nuisance. Pollution involves contamination, but contamination need not constitute pollution. Nature can generate toxic or nuisance compounds (e.g. volcanic ash). Waste can be defined as movable material that is perceived, often erroneously, to be of no further value. Once discarded, it may be no problem, or a nuisance or a hazard (Hill, 1998). As waste may indirectly give rise to pollution, it is necessary to view both together. Pollution and waste management can focus on (1) prevention, or (after escape or release), (2) collection and disposal, or (3) treatment/mitigation (which sometimes may be difficult and costly or impossible). There are thus three pollution and waste management strategies: 1 Prevention 2 Reclamation 3 Disposal In an ideal situation, where environmental management has full support, one might add a fourth: Avoidance (elimination at source, by using longer-lasting construction materials; avoiding dangerous and problematic materials; better processes and machines) — prevention may involve catching waste or pollution before release while avoidance seeks elimination from the outset. Ideally, environmental management seeks a shift from (2) and (3) to (1) (Young, 1990; Bradshaw et al., 1992). A hierarchy of desirability can be agreed. The following is that favoured in the USA (Middleton, 1995:217): (a) reuse; (b) waste reduction; (c) recycling; (d) resource recovery; (e) incineration; (f) landfill. POLLUTION AND WASTE MANAGEMENT 207 Pollution can be ‘primary’, having an effect immediately on release to the environment, or ‘secondary’, the product of interaction after release with moisture, other pollutants, sunlight, etc. Pollution may be local, regional, transboundary, or global. The effects may be direct, indirect or cumulative, felt intermittently or constantly, immediately or after a delay; affecting the atmosphere, soil, oceans, water bodies, groundwater or be restricted to certain organisms, produce or localities. The effects of pollution may be short term or longer term; pose a hazard or a nuisance; be toxic or non-toxic; take the form of a chemical, biological, radiation, heat, light, noise, dust, or smell problem. The environment may render pollution and waste harmless until a threshold (the absorptive capacity) is exceeded, after which, if there is no effective control, there will be gradual or sudden problems. Loss of absorptive capacity may be very difficult to recover from, so it is important that environmental managers model or monitor to avoid exceeding thresholds. The risks from pollution and wastes are far from fully understood, and available standards and monitoring techniques need improvement. What was considered safe twenty years ago is often no longer accepted, and what is acceptable today may not be in the future. A ‘safe’ background level of a pollutant may become dangerous to organisms near the top of a food web (through bioaccumulation or biomagnification), as food organisms concentrate it by feeding or absorption. Some pollutants become concentrated in certain tissues of higher organisms: e.g. DDT and polychlorinated biphyenyls (PCBs) in the fat; radioisotopes like strontium-90 in the bone and radioiodine in the thyroid. This can damage the affected and surrounding tissues (Odum, 1975:103). Wastes and pollutants can also be concentrated by tidal action, sudden rain-out by storms, chemical bonding to certain soil compounds, localized interception of contaminated rainfall, etc., to form hot spots. Some pollutants change little after release, some decay or disperse and become harmless, others are unstable and may be converted into harmful compounds. Pollutants or wastes initially discharged into water or the atmosphere may exchange between these two systems, for example airborne dust may settle on water and sink or polluted water may form aerosols or contaminate groundwater which surfaces at a different time and place. Monitoring and modelling can consequently be difficult and costly. Pollution sources may be: a point (e.g. an explosion), linear (e.g. a road) or extensive (e.g. dust from a desert). Releases can be: continuous, single, brief, random events, or periodic emissions. The distance pollution and waste disperses depends on its qualities and how it is released. Gases or dust are affected by the height of the release, their temperature relative to the air, weather conditions (especially windspeed), and their density or particle size, presence of inversion layers, whether any obstacle is encountered and the texture of that obstacle, and many other factors. Dispersal in water is affected by an equally diverse set of factors. Larger particles may be scattered by natural or artificial explosions, especially if material is projected into a jet-stream, storm or ocean current. It is not uncommon for a temperature inversion in the atmosphere effectively to put a lid over an area, trapping pollution. Water bodies (the sea, lakes, etc.) may also be stratified, with only the upper few metres mixing. Generalization is unwise so environmental managers must model and check each situation. |
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