Bioenergy from wood, waste, and alcohol fuels accounted for an estimated 2.9 quadrillion British thermal
TABLE 10.1
Energy production by source, 1949–2002
(Quadrillion Btu)
| Fossil fuels | Renewable energy1 | |||||||||||||
| Year | Coal | Natural gas (dry) | Crude oil2 | Natural gas plant liquids | Total | Nuclear electric power | Hydroelectric pumped storage3 | Conventional hydroelectric power | Wood, waste, alcohol4 | Geothermal | Solar | Wind | Total | Total |
| 1949 | 11.974 | 5.377 | 10.683 | 0.714 | 28.748 | 0 | 5 | 1.425 | 1.549 | NA | NA | NA | 2.974 | 31.722 |
| 1950 | 14.060 | 6.233 | 11.447 | 0.823 | 32.563 | 0 | 5 | 1.415 | 1.562 | NA | NA | NA | 2.978 | 35.540 |
| 1951 | 14.419 | 7.416 | 13.037 | 0.920 | 35.792 | 0 | 5 | 1.424 | 1.535 | NA | NA | NA | 2.958 | 38.751 |
| 1952 | 12.734 | 7.964 | 13.281 | 0.998 | 34.977 | 0 | 5 | 1.466 | 1.474 | NA | NA | NA | 2.940 | 37.917 |
| 1953 | 12.278 | 8.339 | 13.671 | 1.062 | 35.349 | 0 | 5 | 1.413 | 1.419 | NA | NA | NA | 2.831 | 38.181 |
| 1954 | 10.542 | 8.682 | 13.427 | 1.113 | 33.764 | 0 | 5 | 1.360 | 1.394 | NA | NA | NA | 2.754 | 36.518 |
| 1955 | 12.370 | 9.345 | 14.410 | 1.240 | 37.364 | 0 | 5 | 1.360 | 1.424 | NA | NA | NA | 2.784 | 40.148 |
| 1956 | 13.306 | 10.002 | 15.180 | 1.283 | 39.771 | 0 | 5 | 1.435 | 1.416 | NA | NA | NA | 2.851 | 42.622 |
| 1957 | 13.061 | 10.605 | 15.178 | 1.289 | 40.133 | (s) | 5 | 1.516 | 1.334 | NA | NA | NA | 2.849 | 42.983 |
| 1958 | 10.783 | 10.942 | 14.204 | 1.287 | 37.216 | 0.002 | 5 | 1.592 | 1.323 | NA | NA | NA | 2.915 | 40.133 |
| 1959 | 10.778 | 11.952 | 14.933 | 1.383 | 39.045 | 0.002 | 5 | 1.548 | 1.353 | NA | NA | NA | 2.901 | 41.949 |
| 1960 | 10.817 | 12.656 | 14.935 | 1.461 | 39.869 | 0.006 | 5 | 1.608 | 1.320 | 0.001 | NA | NA | 2.929 | 42.804 |
| 1961 | 10.447 | 13.105 | 15.206 | 1.549 | 40.307 | 0.020 | 5 | 1.656 | 1.295 | 0.002 | NA | NA | 2.953 | 43.280 |
| 1962 | 10.901 | 13.717 | 15.522 | 1.593 | 41.732 | 0.026 | 5 | 1.816 | 1.300 | 0.002 | NA | NA | 3.119 | 44.877 |
| 1963 | 11.849 | 14.513 | 15.966 | 1.709 | 44.037 | 0.038 | 5 | 1.771 | 1.323 | 0.004 | NA | NA | 3.098 | 47.174 |
| 1964 | 12.524 | 15.298 | 16.164 | 1.803 | 45.789 | 0.040 | 5 | 1.886 | 1.337 | 0.005 | NA | NA | 3.228 | 49.056 |
| 1965 | 13.055 | 15.775 | 16.521 | 1.883 | 47.235 | 0.043 | 5 | 2.059 | 1.335 | 0.004 | NA | NA | 3.398 | 50.676 |
| 1966 | 13.468 | 17.011 | 17.561 | 1.996 | 50.035 | 0.064 | 5 | 2.062 | 1.369 | 0.004 | NA | NA | 3.435 | 53.534 |
| 1967 | 13.825 | 17.943 | 18.651 | 2.177 | 52.597 | 0.088 | 5 | 2.347 | 1.340 | 0.007 | NA | NA | 3.694 | 56.379 |
| 1968 | 13.609 | 19.068 | 19.308 | 2.321 | 54.306 | 0.142 | 5 | 2.349 | 1.419 | 0.009 | NA | NA | 3.778 | 58.225 |
| 1969 | 13.863 | 20.446 | 19.556 | 2.420 | 56.286 | 0.154 | 5 | 2.648 | 1.440 | 0.013 | NA | NA | 4.102 | 60.541 |
| 1970 | 14.607 | 21.666 | 20.401 | 2.512 | 59.186 | 0.239 | 5 | 2.634 | 1.431 | 0.011 | NA | NA | 4.076 | 63.501 |
| 1971 | 13.186 | 22.280 | 20.033 | 2.544 | 58.042 | 0.413 | 5 | 2.824 | 1.432 | 0.012 | NA | NA | 4.268 | 62.723 |
| 1972 | 14.092 | 22.208 | 20.041 | 2.598 | 58.938 | 0.584 | 5 | 2.864 | 1.503 | 0.031 | NA | NA | 4.398 | 63.920 |
| 1973 | 13.992 | 22.187 | 19.493 | 2.569 | 58.241 | 0.910 | 5 | 2.861 | 1.529 | 0.043 | NA | NA | 4.433 | 63.585 |
| 1974 | 14.074 | 21.210 | 18.575 | 2.471 | 56.331 | 1.272 | 5 | 3.177 | 1.540 | 0.053 | NA | NA | 4.769 | 62.372 |
| 1975 | 14.989 | 19.640 | 17.729 | 2.374 | 54.733 | 1.900 | 5 | 3.155 | 1.499 | 0.070 | NA | NA | 4.723 | 61.357 |
| 1976 | 15.654 | 19.480 | 17.262 | 2.327 | 54.723 | 2.111 | 5 | 2.976 | 1.713 | 0.078 | NA | NA | 4.768 | 61.602 |
| 1977 | 15.755 | 19.565 | 17.454 | 2.327 | 55.101 | 2.702 | 5 | 2.333 | 1.838 | 0.077 | NA | NA | 4.249 | 62.052 |
| 1978 | 14.910 | 19.485 | 18.434 | 2.245 | 55.074 | 3.024 | 5 | 2.937 | 2.038 | 0.064 | NA | NA | 5.039 | 63.137 |
| 1979 | 17.540 | 20.076 | 18.104 | 2.286 | 58.006 | 2.776 | 5 | 2.931 | 2.152 | 0.084 | NA | NA | 5.166 | 65.948 |
| 1980 | 18.598 | 19.908 | 18.249 | 2.254 | 59.008 | 2.739 | 5 | 2.900 | 2.485 | 0.110 | NA | NA | 5.494 | 67.241 |
| 1981 | 18.377 | 19.699 | 18.146 | 2.307 | 58.529 | 3.008 | 5 | 2.758 | 2.590 | 0.123 | NA | NA | 5.471 | 67.007 |
| 1982 | 18.639 | 18.319 | 18.309 | 2.191 | 57.458 | 3.131 | 5 | 3.266 | 2.615 | 0.105 | NA | NA | 5.985 | 66.574 |
| 1983 | 17.247 | 16.593 | 18.392 | 2.184 | 54.416 | 3.203 | 5 | 3.527 | 2.831 | 0.129 | NA | (s) | 6.488 | 64.106 |
| 1984 | 19.719 | 18.008 | 18.848 | 2.274 | 58.849 | 3.553 | 5 | 3.386 | 2.880 | 0.165 | (s) | (s) | 6.431 | 68.832 |
| 1985 | 19.325 | 16.980 | 18.992 | 2.241 | 57.539 | 4.076 | 5 | 2.970 | 2.864 | 0.198 | (s) | (s) | 6.033 | 67.647 |
| 1986 | 19.509 | 16.541 | 18.376 | 2.149 | 56.575 | 4.380 | 5 | 3.071 | 2.841 | 0.219 | (s) | (s) | 6.132 | 67.087 |
| 1987 | 20.141 | 17.136 | 17.675 | 2.215 | 57.167 | 4.754 | 5 | 2.635 | 2.823 | 0.229 | (s) | (s) | 5.687 | 67.608 |
| 1988 | 20.738 | 17.599 | 17.279 | 2.260 | 57.875 | 5.587 | 5 | 2.334 | 2.937 | 0.217 | (s) | (s) | 5.489 | 68.951 |
| 1989 | 21.346 | 17.847 | 16.117 | 2.158 | 57.468 | 5.602 | 5 | R2.837 | 3.062 | R0.317 | 0.055 | R0.022 | R6.294 | R69.364 |
| 1990 | 22.456 | R18.326 | 15.571 | 2.175 | R58.529 | 6.104 | 0.036 | R3.046 | R2.662 | R0.336 | 0.060 | R0.029 | R6.133 | R70.729 |
| 1991 | 21.594 | 18.229 | 15.701 | 2.306 | 57.829 | 6.422 | 0.047 | R3.016 | 2.702 | R0.346 | 0.063 | R0.031 | R6.158 | R70.362 |
| 1992 | 21.629 | 18.375 | 15.223 | 2.363 | 57.590 | 6.479 | 0.043 | 2.617 | 2.847 | 0.349 | 0.064 | 0.030 | 5.907 | 69.933 |
| 1993 | 20.249 | 18.584 | 14.494 | 2.408 | 55.736 | 6.410 | 0.042 | 2.892 | 2.804 | 0.364 | 0.066 | 0.031 | 6.157 | 68.262 |
TABLE 10.1
Energy production by source, 1949–2002
| Fossil fuels | Renewable energy1 | |||||||||||||
| Year | Coal | Natural gas (dry) | Crude oil2 | Natural gas plant liquids | Total | Nuclear electric power | Hydroelectric pumped storage3 | Conventional hydroelectric power | Wood, waste, alcohol4 | Geothermal | Solar | Wind | Total | Total |
| 1994 | 22.111 | 19.348 | 14.103 | 2.391 | 57.952 | 6.694 | 0.035 | 2.683 | 2.939 | 0.338 | 0.069 | 0.036 | 6.065 | 70.676 |
| 1995 | 22.029 | R19.082 | 13.887 | 2.442 | R57.440 | 7.075 | 0.028 | 3.205 | 3.068 | 0.294 | 0.070 | 0.033 | 6.669 | R71.156 |
| 1996 | 22.684 | R19.344 | 13.723 | 2.530 | R58.281 | 7.087 | 0.032 | 3.590 | 3.127 | 0.316 | 0.071 | 0.033 | 7.137 | R72.472 |
| 1997 | 23.211 | 19.394 | 13.658 | 2.495 | 58.758 | 6.597 | 0.041 | 3.640 | 3.006 | 0.325 | 0.070 | 0.034 | 7.075 | 72.389 |
| 1998 | 23.935 | 19.613 | 13.235 | 2.420 | 59.204 | 7.068 | 0.046 | 3.297 | 2.835 | 0.328 | 0.070 | 0.031 | 6.561 | 72.787 |
| 1999 | 23.186 | 19.341 | 12.451 | 2.528 | 57.505 | 7.610 | 0.062 | 3.268 | R2.885 | 0.331 | 0.069 | 0.046 | R6.599 | R71.652 |
| 2000 | 22.623 | R19.662 | 12.358 | 2.611 | R57.254 | 7.862 | 0.057 | 2.811 | R2.907 | 0.317 | 0.066 | 0.057 | R6.158 | R71.218 |
| 2001 | R23.053 | R20.227 | 12.282 | R2.547 | R58.109 | 8.028 | 0.090 | R2.201 | R2.678 | R0.311 | R0.065 | R0.068 | R5.324 | R71.372 |
| 2002P | 22.554 | 19.561 | 12.314 | 2.561 | 56.990 | 8.145 | 0.089 | 2.668 | 2.756 | 0.304 | 0.064 | 0.106 | 5.899 | 70.946 |
| 1End-use consumption and electricity net generation. | ||||||||||||||
| 2Includes lease condensate. | ||||||||||||||
| 3Pumped storage facility production minus energy used for pumping. | ||||||||||||||
| 4Alcohol is ethanol blended into motor gasoline. | ||||||||||||||
| 5Included in "Conventional Hydroelectric Power." | ||||||||||||||
| R = Revised. P = Preliminary. NA = Not available. (s) = Less than 0.0005 quadrillion Btu. | ||||||||||||||
| Note: Totals may not equal sum of components due to independent rounding. | ||||||||||||||
| SOURCE: "Table 1.2. Energy Production by Source, 1949–2002," in Annual Energy Review 2002, U.S. Department of Energy, Energy Information Administration, Washington, DC, October 2003 | ||||||||||||||
FIGURE 10.3
Renewable energy consumption by type, 2003
units (Btu) of energy in 2003, comprising 47 percent of renewable energy consumed. (See Figure 10.3.)
Biomass Conversion
There are two types of biomass conversion processes: thermochemical conversion and biochemical conversion. Thermochemical conversion uses heat to produce chemical reactions in biomass. Direct combustion is the easiest and most commonly used method. Materials such as dry wood or agricultural wastes are chopped and burned to produce steam, electricity, or heat for industries, utilities, and homes. Wood burning in stoves and fireplaces is one example. The burning of agricultural wastes is also becoming more widespread. In Florida, for example, sugar cane producers use the residue from the cane to generate much of their energy.
Pyrolysis, also called gasification or carbonization, uses heat to break down biomass to yield liquid, gaseous, and solid fuels. Converting wood to charcoal is an example of this process.
The second type of conversion process, biochemical conversion, uses enzymes, fungi, or other microorganisms to convert high-moisture biomass into either liquid or gaseous fuels. Bacteria convert manure, agricultural wastes, paper, and algae into methane, which is used as fuel. Sewage treatment plants have used anaerobic (without oxygen) digestion for many years to generate methane gas. Small-scale digesters have been used on farms, primarily in Europe and Asia, for hundreds of years. The DOE estimates that many thousands of biofuel plants are in use in Korea, and perhaps half a million plants operate in China.
Another type of biochemical conversion process, fermentation, uses yeast to decompose carbohydrates to yield ethyl alcohol (ethanol) and carbon dioxide. Sugar crops, grains (corn, in particular), potatoes, and other starchy crops are common feedstocks that supply the sugar for ethanol production.
Wood
Wood energy was the first energy source in America's industrialization. Wood, the most commonly used biofuel, is still used to heat millions of homes every year. In 2003 it provided 2.1 quadrillion Btu, accounting for 34 percent of renewable energy consumption (See Figure 10.3.)
When wood is widely used as a fuel in an area, deforestation can occur, resulting in the possibility of soil erosion and mud slides. Burning wood, as with the burning of fossil fuels, also pollutes the environment.
Ethanol and Methanol—Important Agricultural By-Products
Ethanol is a colorless, nearly odorless, flammable liquid derived from fermenting plant material that contains carbohydrates in the form of sugar. U.S. ethanol production has grown steadily since 1980, reaching 2.81 billion gallons in 2003, according to the U.S. Department of Energy. Production capacity is largely located in the farming regions of the upper Midwest. (See Figure 10.6.)
Most of the ethanol manufactured for use as fuel is derived from corn, wood, and sugar. A mixture of 10 percent ethanol and 90 percent gasoline is usable in any internal combustion engine without the need to modify the motor. Although the DOE claims that the demand for alcohol/gasoline blends is increasing because alcohol can substitute for lead as an octane booster, there is little question that the development of ethanol depends more on the continued support of farm state legislators than any economic benefit.
Ethanol is difficult and expensive to produce in bulk. Methanol-blend fuels have also been tested successfully. (Methanol is methyl alcohol.) Using methanol instead of diesel fuel virtually eliminates sulfur emissions and reduces other environmental pollutants usually emitted from trucks and buses. Burning biofuels in vehicle engines creates a "carbon cycle" in which the earth's vegetation can in turn make use of the products of combustion and, therefore, reduce net greenhouse gases. (See Figure 10.7.) Producing methanol from biofuels, however, is costly.
Some scientists believe ethanol made from wood, sawdust, corncobs, or rice hulls could liberate the alcohol
FIGURE 10.4
Renewable energy consumption by major sources, 1973–2002
fuel industry from its dependence on food crops such as corn and sugar cane. Worldwide, there are enough corncobs and rice hulls left over from annual crop production to produce more than 40 billion gallons of ethanol.
Advocates of wood-derived ethanol believe that the eventual result of wood-to-ethanol conversion research could create a sustainable liquid fuel industry that does not rely on pollution-generating fossil fuels. For instance if new trees were planted to replace those that were cut for fuel, they would be available for later harvesting and, in the meantime, contribute to the prevention of global warming by continuing their carbon dioxide processing function. Other scientists warn that a huge demand for transportation fuels could create a demand for wood that might accelerate the destruction of old-growth forests and endanger ecosystems. Without careful attention to forestry practices, ethanol production might aggravate rather than solve the fuel problem.
Municipal Solid Waste
Each year millions of tons of municipal solid waste (MSW), or garbage as it is commonly called, are buried in landfills and city dumps. This method of disposal is not only costly but is becoming increasingly difficult as some landfills across the nation are near capacity. Many communities have discovered that they can solve two problems at once by constructing waste-to-energy (WTE) plants. Not only is garbage burned and reduced in volume by 90 percent, energy in the form of steam or electricity is generated in a cost-effective way. The potential energy benefit is significant.
WASTE-TO-ENERGY PLANTS.
The two most common WTE plant designs are the mass burn (also called direct combustion) and the refuse derived fuel (RDF) systems.
Most WTE plants in the United States use the mass burn system. This system's advantage is that the waste does not have to be sorted or prepared before burning, except for removing obviously noncombustible, oversized objects. The mass burn eliminates expensive sorting, shredding, and transportation machinery that may be prone to break down.
Waste is carried to the plant in trash trucks and dropped into a storage pit. Large overhead cranes lift the garbage into a furnace feed hopper that controls the amount and rate of waste that is fed into the furnace. Next, the garbage is moved through a combustion zone so that it burns to the greatest extent possible. The burning garbage produces heat, and that heat is used to produce steam. The steam can be used directly for industrial needs or heat can be sent through a turbine to power a generator to produce electricity.
RDF systems process waste to remove noncombustible objects and to create homogeneous and uniformly sized fuel. Large items such as bedsprings, dangerous materials, and flammable liquids are removed by hand. The trash is then shredded and carried to a screen to remove glass, rocks, and other material that cannot be burned. The remaining material is usually sifted a second time with an air separator to yield fluff. The fluff is sent to storage bins before being burned, or it can be compressed into pellets or briquettes for long-term storage. This fuel can be used as an energy source by itself in a variety of systems, or it can be used with other fuels such as coal or wood.
The major obstacle to increasing the use of municipal WTE plants is their effect on the environment. Noise from trucks, fans, and processing equipment at RDF plants can
FIGURE 10.5
Biomass to bioenergy
be unpleasant for nearby residents. The emission of particles into the air is controlled by electrostatic precipitators, and most gases can be eliminated by proper combustion techniques. There is concern, however, about the amounts of dioxin (a very dangerous air pollutant) that are often emitted from these plants.
LANDFILL GAS RECOVERY.
Landfills contain a large amount of biodegradable matter. Gas is created because of the lack of oxygen that helps the growth of methagens—types of bacteria that produce methane gas and carbon dioxide. In the past, as landfills aged, these gases built up and leaked out. This gas leakage prompted some communities to drill holes and burn off the flammable and dangerous methane.
The energy crisis of the 1970s made this methane gas an energy resource too valuable to waste, and efforts were made to find an inexpensive way to tap the gas. The first landfill gas-recovery site was finished in 1975 at the Palos Verdes Landfill in Rolling Hills Estates, California. Depending on the extraction rates, most existing sites can produce gas for about 20 years.
In a typical operation, garbage is allowed to decompose for several months. When a sufficient amount of methane gas has developed, it is piped out to a generating plant where it is burned to produce electricity. In its purest form methane gas is equivalent to natural gas and can be used in exactly the same way.
The advantages of tapping gas from a landfill go beyond the energy provided by the methane. When internal pressure forces methane gas to seep into the air, it carries very unpleasant odors into the surrounding neighborhoods. The released methane can also be a danger because, if it accumulates and is accidentally ignited, it can explode. Extracting the methane gas for energy eliminates both of these problems.
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