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Geothermal Energy and the Environment
Everyone is interested in the environmental impacts
of the energy resources we use, and this is also true of geothermal energy.
While the areas of concern are the same—air, land, and water quality—there
are many differences in terms of gaseous emissions, land use, noise, and
potential ground subsidence. Geothermal fluids contain dissolved gases, mainly
carbon dioxide (CO2) and hydrogen sulfide (H2S), small amounts of ammonia,
hydrogen, nitrogen, methane and radon, and minor quantities of volatile species
of boron, arsenic, and mercury. Using these fluids to generating electricity
provides significant environmental advantage because releases no nitrogen
oxides (NOx), virtually no sulfur dioxide (SO2), and much less carbon dioxide
(CO2) than fossil-fueled power. The reduction in nitrogen and sulfur emissions
in turn reduces local and regional potential for acid rain.
Geothermal power plant CO2 emissions can vary from plant to plant depending
on both the characteristics of the reservoir fluid and the type of power
generation plant. Binary plants have no CO2 emissions, while dry steam and
flash steam plants have CO2 emissions on the order of 0.2 lb/kWh, less than
one tenth of the CO2 emissions of coal-fired generation. Improved and increased
injection to sustain geothermal reservoirs has helped reduce CO2 emissions
from geothermal power plants.
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Figure 18 - Geothermal energy resources pose much less of a
problem in the two most common emissions of fossil fuels.
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The odor of hydrogen sulfide, often characterized as that of rotten eggs,
is common near volcanic areas, such as Yellowstone National Park. The concentration
of H2S emissions from geothermal plants is 0.03–6.4 g/kWh, varying significantly
from field to field, depending on the amount of hydrogen sulfide contained
in the geothermal fluid and the type of plant used to exploit the reservoir.
While such emissions do not contribute to acid rain or global climate change,
the odor they produce has created objections in many areas.
Usually, these emission do not pose a significant impediment to development,
but occasionally the have produced controversy. For example, at The Geysers,
especially in the late 1970s and early 1980s, the odor of hydrogen sulfide
threatened the development because it was interfering with the tourist economy
downwind at the nearby resorts along Clear Lake. As this activity and the
geothermal development are largely located in the same county, local politicians
were forced to weigh one source of economic development against the other.
Because the geothermal development itself is immovable, another solution
was needed. Today, the removal of H2S from geothermal steam is mandatory
in the United States, and the most common process is the Stretford process,
which produces pure sulfur and is capable of reducing H2S emissions by more
than 90%. More recent techniques include burning the hydrogen sulfide to
produce sulfur dioxide, which can be dissolved, converted to sulfuric acid
and sold to provide income.
Land use is a particularly sensitive issue in the development of geothermal
energy. On the credit side of the ledger, geothermal installations don’t
require damming of rivers or harvesting of forests. Nor do they require mineshafts,
tunnels, open pits, or waste heaps. Moreover, the long fuel chain of fossil
and nuclear fuels is largely absent; all phases of this fuel chain are
in one location. This trait concentrates whatever impacts that exist in
one location. If, as at The Geysers, the terrain is steep and unstable,
geothermal developments must take these conditions into account. If, on
the other hand, the terrain is flat and agriculture, these conditions must
be addressed.
In every case of geothermal development, existing land use conditions
are critical to everything from exploration to generation. Any environmental
impacts cannot be spread out and diluted as they can with fossil and other
fuels. Nonetheless, if one were to add up the actual land needs, they would
find that geothermal power plants require relatively little land. An entire
geothermal field uses only1–8 acres per MW versus 5–10 acres per MW for nuclear
plants and 19 acres per MW for coal plants. This makes geothermal a
land use bargain.
Power Source
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Land Requirement (Acre/MW)
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Geothermal
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1-8
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Nuclear
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5-10
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Coal
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19
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Water contamination has in the past been a concern for geothermal developments,
mostly with regard to water-dominated systems. In the Imperial Valley, the
total dissolved solids (TDS) of much of the geothermal water exceed 300,000
mg/liter. If this were allowed to flow out onto the surface—as is permitted
in other countries—the impact on the surrounding agricultural fields would
be ruinous. The potential problem has been neatly solved, however,
by the use of reinjection back into the reservoirs from which the fluids
were derived. This has the added benefit of maintaining reservoir pressure
and prolonging the life expectancy of the reservoir. Binary systems, as described
above, use this procedure routinely.
Reinjection is also used to slow or prevent ground subsidence that can
result in some geological circumstances once water is withdrawn. Indeed,
the possibility of subsidence was the subject of long delays in the development
of the water-dominated Imperial Valley fields in California. The concern
there was that the removal of geothermal water would result in compaction
underground. Were such compaction to reach the surface as local authorities
feared, it could have a devastating impact on the delicate balance of the
irrigation and drainage system that makes the Imperial Valley so valuable
for agriculture.
To date, little if any geothermal subsidence has occurred in the Imperial
Valley, but the concern was justified because of the experience at Wairakei,
New Zealand. Here the ground has subsided as much as 42 feet. Monitoring
has shown that a maximum subsidence rate of 18 inches/year occurred in a
small region, outside the production area, with subsidence of at least 1
inch/year occurring all over the production field. Although Wairakei presents
an extreme example, there is little that can be done to prevent or mitigate
subsidence effects other to re-inject water at some distance from the production
well to avoid the cooler rejected waste fluid from lowering the temperature
of the production fluid.
Another concern is noise, especially during exploration drilling and
construction phases. Noise levels from these operations can range from 45
to 120 decibels (dBa). For comparison, noise levels in quiet suburban residences
are on the order of 50 dBa, noise levels in noisy urban environments are
typically 80–90 dBa, and the threshold of pain is 120 dBa at 2,000–4,000
Hz. Site workers can be protected by wearing ear mufflers. With best practices,
noise levels can be kept to below 65 dBa, and construction noise should be
practically indistinguishable from other background noises at distances
of half a mile.
Operation
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Noise Level (dBa)
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Air drilling
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85–120
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Mud drilling
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80
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Discharging wells after drilling
(to remove drilling debris)
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Up to 120
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Well testing
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70–110
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Diesel engines (to operate compressors
and provide electricity)
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45–55
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Heavy machinery (e.g., for earth
moving during construction)
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Up to 90
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