|Environmental Handbook Volume II: Agriculture, Mining/Energy, Trade/Industry (GTZ, 1995, 736 p.)|
|Mining and energy|
|43. Renewable sources of energy|
The utilization of energy, no matter what the source, is bound to have certain environmental consequences (land consumption, pollution,...) that need to be identified and evaluated, preferably in advance.
2.1 Solar energy
The use of solar energy via collectors or photovoltaic systems places no immediate material burden on the environment. However, the collector system can be expected to contain a heat transfer medium (fluid), the escape of which could result in pollution. The acceptable media include such readily degradable substances as propylene glycols. Noxious additives serving as preservatives should be replaced by less harmful alternatives (carboxylic acid).
The use of solar cookers involves the danger of blinding, and solar energy collected by solar cells and stored in batteries demands proper handling and appropriate disposal of the spent batteries. The materials used for the battery case, as well as the hydrochloric acid and lead contents, can be recycled in suitable facilities.
Land consumption for small-scale systems can be avoided by installing them on roofs and facades. Well-considered integration can prevent optical/aesthetic impairment, and annoying reflections can be diminished by lumenizing and/or delustering.
With the exception of reduced reflections, no such measures can be applied to large-area systems. Consequently, optical/aesthetic expectations may stand in conflict with other natural surface potentials (soils for agricultural production, protection of species and biotopes; unless, of course, the site in question is located in the desert).
Depending on the local situation, the shading and altered albedo resulting from large-scale installations can affect the flora, fauna and microclimate (evaporation rates, airflow, temperature).
Solar cells and various collectors have a substantial space requirement relative to the amount of energy produced (per 100 MW: ~ 1 km² for solar cells and ~ 3 km² for solar-thermal power plants, compared to ~ 0.4 km² for hard-coal power plants).
Additional environmental impacts derive from the manufacture of materials used in the production of collectors and solar cells. Steel, copper and aluminum, all of which are used frequently, cause environmental problems in the form of emissions, i.e., particulates, fluorine compounds, solid and liquid waste and high levels of energy consumption, particularly for aluminum.
Some rare and toxic metals such as cadmium, arsenic, selenium and gallium used in solar cells are mildly pollutive at the processing stage (wastewater, exhaust gases). These substances are characterized by high chemical stability, and the environmental risk remains confined to the production site. Thus, adequate monitoring and safety measures can minimize the risk; cf. environmental brief Non-ferrous Metals.
2.2 Biomass energy
Used as a substitute for metal, cement, plastic and diverse other raw materials, biomass can help reduce the energy expenditures for processing and manufacturing such materials.
In the present context, however, our interest in biomass is limited to its being a source of energy.
Significant utilization of biomass presupposes that the biomass cycle of growth and extraction remains essentially intact, i.e., that the biomass source (a forest, perhaps), is always allowed to adequately regenerate.
The burning of biomass (wood, straw, dung, etc.) liberates pollutants -
- from the fuel and the combustion air
- or which form as a result of incomplete combustion [CO, tar, soot and hydrocarbons, including carcinogenic polycyclic aromatic hydrocarbons (PAH)].
The main cause of emission problems with biomass is incomplete combustion. The following measures can help achieve complete combustion:
- sufficiently large incinerator
- sufficiently hot combustion chamber
Those conditions are inherently satisfied by systems equipped with prefiring chambers or for bottom firing.
- use of dry fuel (< 20 % wood moisture).
Mode of operation
- full-load operation
- uniform fuel supply.
The exhaust gases, particularly in the case of straw, contain large amounts of solid particulates; large-scale systems therefore should include appropriate cyclone separators or filters.
On a country-specific basis, biomass can cover as much as 90 % of the overall demand for energy. As a rule, wood, dung and straw are burned in open fires from which the aforementioned pollutants escape and can be inhaled by the users (primarily women and children).
This can amount to a formidable health hazard, particularly because of the carcinogenicity of polycyclic hydrocarbons. In addition, respiratory ailments can also result from such exposure.
The use of stoves with some form of chimney substantially reduces the indoor smoke nuisance and improves the combustion efficiency, thereby reducing fuel consumption and, hence, emission levels.
The use of straw and dung as fuel can lead to conflicts concerning agricultural production and the sustenance of soil fertility due to loss of nitrogen and reduced humification, because what has been burned cannot be returned to the soil. In some climate zones, using the ashes as fertilizer can cause a dust-evolution problem.
From an ecological standpoint, the use of scrap wood and various forms of wood residue calls for a somewhat sophisticated frame of reference: while tending felling can be both ecologically compatible and advisable, the safe extent of wood removal from forests and plantations depends on the climate, the soil conditions and the vegetation. The removal of wood residue impacts the nutrient cycle, humification, microflora and microfauna. This applies as well to large-scale stump-grubbing, which also makes the ground more susceptible to erosion.
Long-term natural wood production does not satisfy the "firewood criteria" of easy, short-term availability. Agroforestry projects involving certain harmonized plant species in certain spatial arrangements designed to make the individual species and combinations serve different functions (shading, soil amelioration, shelterbelting, improvement of water regimen, mulching, fuel, food/fodder, starting material), are able to more quickly satisfy fuel requirements by reason of brief rotation periods. Such - noncentralized - configurations facilitate the gathering of wood while abating environmental burdens in connection with road transport and helping to bridge over fuel shortages.
Intensive (energy farming) techniques based on fast-growing combustibles treated with high doses of pesticides and fertilizers can pollute, i.e., eutrophize, surface waters due to nutrient loading, possibly in combination with erosion, a loss of diversity, and health hazards emanating from residual pesticides. The use of machines on sensitive ground (marginal soils) can induce erosion; cf. environmental brief Forestry.
Large-scale felling of trees (= land clearing) affects the water economy and microclimate, is harmful to flora and fauna, and can cause erosion, the extent of which depends on the type of soil, the climate and the angle of slope.
If cleared land is not appropriately reafforested, or if the soil is overused for a prolonged period, both the soil and the water regimen may sustain irreversible damage.
Any attempt to substantially expand fuelwood production without integrating the effort into the general agricultural scheme can generate conflicts over space requirements for food production; cf. corresponding environmental briefs on agriculture, such as Plant Production, Forestry etc.
As a rule, any gas extracted from biomass by such means as pyrolysis is used as fuel, either for heating purposes or for driving gas-fueled power generators.
While the environmental effects of fuel extraction from biomass are dealt with in section 2.2.1, additional ecological impacts can derive from:
- carburetion (accidents, deflagration);
- the gas itself (accidents, fire, poisoning due to leaks);
- wastewater from gas scrubbing;
- carbonization residue (ash, tar);
- combustion emissions (exhaust, cooling water, lubricant).
Generator gas obtained from large plants (as opposed to small wood gasifiers, e.g., for tractors) should be cleaned and dedusted prior to use. The wastewater from gas scrubbing can be expected to contain ammonia, phenols, perhaps even cyanides and potentially carcinogenic polycyclic aromatic hydrocarbons (PAH). Consequently, they cannot be disposed of freely. To the extent possible, the incidental tars and oils should be returned to the gasification process. In addition to the mechanical extraction of solids, e.g., in a settling basin, the effluent can be put through a biological clarifying plant in which phenols are digested by suitable strains of bacteria.
Solid residue from the gasification process is usually heavily polluted and therefore problematic with regard to its disposal. The harmful-substance contents require case-by-case determination, because they vary according to the raw material in question and the process employed.
The exhaust from generator gas combustion may also require treatment, depending on the quantity involved and its pollutive load. It is likely to contain oxides of nitrogen, PAH's, carbon monoxide or soot (plus negligible amounts of sulfur dioxide). The NOx and hydrocarbon contents can be extensively decomposed with the aid of catalytic converters.
Biogas resulting from anaerobic bacterial fermentation of biomass consists primarily of methane (principal component), carbon dioxide, carbon monoxide and small amounts of hydrogen sulfide. Small biogas plants provide fuel for cooking, lighting, etc., while large-scale facilities can produce enough biogas for fueling gas motors.
Accidents can occur when a slurry pit or a fixed-dome digester has to be entered for cleaning (danger of asphyxiation).
Since hydrogen sulfide has toxic effects of humans, corrodes materials, and forms sulfur dioxide in the combustion process, its removal should be given due consideration. However, the precleaning process is rather complicated and generates end products with a pollutive potential. The chemicals used for cleaning biogas (e.g., iron oxide), as well as their reaction products (mixture of iron oxide and sulfur) demand proper storage, use and subsequent disposal.
Whereas biogas often requires interim storage, appropriate pertinent safety standards must be heeded (danger of poisoning, fire, explosion); cf. environmental brief Petroleum and Natural Gas.
The raw material may contain toxic heavy metals that are prejudicial to health. While such constituents (deriving from polluted soil) remain unaffected by the digestion process they nevertheless should be monitored (tested for). And while the digestion process does not kill off all pathogens and worm ova, the digested sludge nonetheless counts as safe and benign from the standpoint of epidemic control. Used improperly, its high nitrogen content can emburden both surface water and groundwater. Thus, the use of biosludge as a fertilizer must be properly timed (availability for plants), effected with suitable equipment, and applied in accordance with the soil's nutrient reserves.
Considering methane's relevance as a greenhouse gas, its collection and combustion is ecologically advantageous as long as it is being generated by anaerobic digestive processes.
Various technical processes are available for deriving oil and alcohol from biomass and using them as substitutes for conventional fuels.
The cultivation of biomass as a raw material for obtaining fuel by alcoholic fermentation (e.g., of sugar cane) or by extracting oil from soybeans stands in direct competition with foodstuff farming. Large monocultures involving high levels of fertilization and pesticide spraying have environmental impacts of the kind discussed in section 2.2.1; cf. environmental brief Plant Protection.
The following environmental loads result from the production of ethanol and oil:
- exhaust gases deriving from the provision of process
energy (e.g., distillation, burning or refining of crude oil) - cf. section
- carbon dioxide as a product of fermentation;
- nontoxic but very pollutive organic sludge and wastewater (slops) from ethanol production, all containing large amounts of nitrogen-phosphorus and potassium components.
The slops, or distiller's wash, can serve as a fertilizer or fodder additive. If it contains enough residual sugar or starch, it is suitable for fermentation, i.e., biodigestion.
The biogas yield can serve as a substitute for part of the conventional process energy, while the organic substances remaining in the effluent must be decomposed in a clarifying plant.
The production of alcohol is very energy-intensive.
The use of ethyl alcohol (ethanol) as a fuel additive in internal-combustion engines produces relatively low pollution in the form of NOx, CO, soot and simple hydrocarbons, but is accompanied by certain aldehydes, some of which are carcinogenic.
Motors fueled by alcohol alone should be specially tuned and optimized in order to minimize harmful emissions. Catalytic converters, for example, reduce the aldehyde emission levels to that of gasoline engines. Compared to gasoline/petrol, ethyl alcohol contains practically no carcinogenic polycyclic hydrocarbons.
Like alcohol, biomass-base oil for diesel engines gives off no sulfur or lead but some amounts of soot, simple hydrocarbons and particulate emissions. Soot filters are conditionally suitable for cleaning the exhaust gases.
2.3 Wind energy
Even large wind power plants have modest environmental impacts. Their material and space requirements are also relatively modest. The manufacture of some steel and plastic components, however, does involve certain environmental problems.
The following substantial environmental problems arise in connection with their operation:
- landscape impairment;
- danger of accidents due to rotor-blade detachment;
- electromagnetic interference;
- negative effects on fauna, birds in particular.
How much noise is produced depends on how fast the propellor is rotating. The faster the speed of rotation, the louder the noise.
Old aerogenerators have been known to produce sound intensities on the order of 130 dB(A). Small wind generators tend to make more "wind" noise than running noise. New facilities have aerodynamically optimized blades and encapsulated generators-cum-transmissions that minimize the noise nuisance. Nevertheless, a minimum distance of roughly 100 meters should be maintained between wind generators and residential areas. There is, of course, always the possibility that the safe clearances designated at the planning stage will eventually be transgressed by uncontrolled settlement (squatting).
Impairment of the landscape is unavoidable. The degree of impairment depends on local circumstances, including the intensity of wind-power utilization. Wind parks do more to impair the landscape than individual plants. Especially large aerogenerators with metal motors tend to disrupt natural electromagnetic fields and interfere with radio reception. Modern wind power plants have fiberglass rotor blades and therefore cause no such interference.
The danger of accidents attributable to rotor-blade detachment can be minimized, if not precluded, by routine inspections and maintenance, plus adherence to the appropriate safety clearances.
Hydropower is the by far the most important renewable source of energy. The incidental reservoirs often serve other, additional purposes such as irrigation and the supply of drinking water.
The harnessing of hydropower entails substantial intervention in the environment (land consumption, altered hydrological regimen, etc.). Due to the importance of hydraulic engineering with respect to the environment, and with deference to the vast experience that has been accumulated in connection with such facilities, a separate brief has been devoted to that sector.
2.5 Geothermal energy
Geothermal sources of energy include:
- warm and hot water in deep-reaching joint systems of
crystalline rock formations or deep-lying groundwater stories within expansive
- hot-water and steam occurring deep within structurally disturbed zones or in regions marked by current or recent volcanic activity,
- exploitation of geothermal energy according to the dry hot rock process (DHR technology presently under development).
DHR technology aims to establish artificial heat-exchange surfaces in hot rock (with temperatures > 200°C) from which geothermal energy can then be extracted by pumping water into and back out of the artificial hot-rock joint system. Despite substantial research funding to date, however, the method's economic feasibility has not yet been established.
The environmental impacts of exploiting geothermal energy depend on the concrete situation. Environmental burdens can result from entrained pollutants (various salts, sulfur compounds, arsenic, boron) and gases in the geothermal fluids. In modern geothermal facilities the spent (cooled-down) fluids and their entrained pollutants are pumped back into the ground, preferably to a point below the pay zone of the occurrence, while the incidental gases are released to the atmosphere.
The extraction of geothermal fluids, particularly in dry-climate regions, can negatively influence near-surface groundwater stories and, hence, their utilization (potable water, irrigation) by causing the groundwater table to recede (phreatic decline).
Sustained use of a particular geothermal reservoir can lead to gradual and extensive subsidence and frequent consequential damage to railroads, highways, power transmission lines and, particularly, the pipelines through which the geothermal fluids are pumped from the wells to the power plant/user. The local hydrological situation can be substantially influenced and modified by attendant phenomena such as the diversion of streams and rivers or even the formation of lakes in ground depressions.
The space requirements of geothermal installations (wells, pipelines) are quite modest - so much so that such facilities hardly interfere with agricultural utilization of the surrounding land.
The drilling of wells in a geothermal field is somewhat hazardous in that unforeseen eruptions of steam can occur without notice and then take weeks or even months to get under control. In the meantime, the environment may have become substantially contaminated by impurities in the steam.