Ecological and Environmental Impacts of Bioenergy

Impacts of bioenergy? include affects on ecosystems and species within them (including humans), termed ecological impacts; and affects on geophysical systems such as water and climate, termed environmental impacts. Impacts may be direct, like tailpipe emissions from burning biofuels, or indirect, like soil emissions of carbon dioxide from biomass? production. Bioenergy can have positive and negative ecological and environmental impacts, and the overall net impact can be either positive or negative.

Many of the ecological and environmental impacts of bioenergy are associated with land use and land use change in connection to biomass production. Bioenergy-related land use decisions may affect local, regional and global ecological and environmental systems. Of particular concern are GHG emissions, habitat change, biodiversity, soil quality, and water quantity and quality. These high-priority concerns are detailed below.

Land use and land use change

Land use decisions are affected by many factors from local to global in scope, including public policy, prices of agricultural commodities, prices of petroleum, and land values (figure 1). Profitability of specific land uses and the benefits of competing uses are also key influences on land use decision-making (figure 1). Decision-makers who choose to produce biomass must consider land use and potentially also land use change (LUC). Land use is management of land resources for economic benefit and includes tillage, maintenance and harvest activities as well as conservation practices. Land use change includes conversion of native ecosystems into agricultural use, as well as switching from one crop type to another. Also included in the LUC category is diversion of food crops grown primarily for food into bioenergy feedstock? use, for example, corn grain.

Figure 1. Factors and their interactions influencing land use decisions. (CL Williams, 2011.)

Biomass demand is thought to be a local or regional level influence on land use decision-making. However, competing uses, such as production of conventional commodity crops for example, are driven by complex global financial and trade systems. Land use decisions in response to biomass and bioenergy demand, then, are coupled with local and global economies.

Native and managed ecosystems are sources of financial benefit when materials are removed from these systems and exchanged in markets. Native ecosystems and managed ecosystems also provide many benefits which indirectly affect humans. Water and nutrient cycling are but two examples of the benefits ecosystems provide that have no direct economic value. Land use and LUC associated with biomass production can increase or decrease the direct and indirect benefits of native and managed ecosystems. Whether land use and LUC increase or decrease these benefits depends on the type and amount of benefits occurring prior to LUC.

Greenhouse gases and climate impacts

Greenhouse gases are gases in the atmosphere that absorb and emit thermal radiation in a processes known as the greenhouse effect - the mechanism by which solar radiation is captured and earth is warmed to an extent necessary for supporting life (figure 2, “Natural Greenhouse Effect”). The primary GHGs? are water vapor, carbon dioxide, methane, nitrous oxide and ozone. These gases differ in their abundances in the atmosphere as well as their warming power. The science of global climate change indicates an overall warming trend for the earth as a whole in association with rising levels of GHGs. While natural sources effect the concentrations of GHGs over time, global scientific consensus indicates that human sources of GHGs also contribute to global climate change (figure 2, “Human Enhanced Greenhouse Effect”). For more information on global warming and climate change see here, and here.

Figure 2. The greenhouse effect is the primary mechanism by which solar radiation is captured by earth’s atmosphere. Human activity has enhanced the warming ability of this mechanism. (Will Elder, U.S. National Park Service.)

Bioenergy has the potential to be carbon-neutral by balancing the amount of carbon released in use of bioenergy products with an equivalent amount put into and stored in soils, plant and animal tissues, or other material such as the ocean floor. That is, bioenergy is part of a global carbon cycle (figure 3) where plants take up atmospheric carbon dioxide and convert it into plant tissue. That is, they sequester carbon (figure 4). The carbon is later released back to the atmosphere as carbon dioxide when the plant biomass is burned directly or after it has been converted into a fuel and used – called emissions (figure 4). From there the carbon dioxide is available again for plant sequestration. However, land use, and more specifically LUC, effects the flux of GHGs between the atmosphere, soils, water, and tissues of living things (figure 4). Converting native habitats to croplands, for example, can lead to releases of CO2 into the atmosphere due to burning of vegetation for land clearing. Carbon dioxide can also be released by microbial decomposition of organic matter leading to release CO2 into atmosphere. In the case of clearing of new land (i.e., native habitat) for biomass production, the amount of GHG emissions will depend on the ecosystem being converted (figure 4). In some cases, the amount of CO2 emitted will be large and will require decades if not hundreds of years to be sequestered again by bioenergy crops or native vegetation.

Figure 3. The carbon cycle and biofuels: carbon dioxide (CO2) from the atmosphere is taken up by plants and converted into plant tissues. Plants are harvested and converted into fuels which are burned, where it becomes available again for plants. However, instead of a “closed loop”, as depicted here, emissions of CO2 from conversion of untilled soil and emissions from use of fossil fuels in fertilizer production and diesel use in farm equipment can increase the amount of atmospheric carbon dioxide from bioenergy systems rather reduce it. (US DOE.)

Carbon sequestering potential of some biomass systems is much less than some native ecosystems at the same location. The reverse can also be true though, where some biomass cropping systems are capable of sequestering more carbon than a native ecosystem at the same location.

Figure 4. Land use impacts on carbon flux and the ecosystem mechanisms that regulate carbon emissions and sequestration. (CL Williams, 2011.)

To-date, there is no scientific consensus on whether bioenergy as a whole contributes to or abates global climate change. Rather, scientific evidence appears to indicate that “it depends”. First generation biofuel systems, such as ethanol made from corn grain, tend to emit more GHGs than cellulosic ethanol? systems, particularly CO2. Compared to perennial biomass production, corn cropping requires more fertilizer and pesticide inputs, and results in greater soil disturbance leading to land use- induced carbon emissions. Moreover, when agricultural commodity prices are high, marginal lands and lands set-aside for conservation purposes tend to be converted into row-crops such as corn and thus lead to LUC-induced CO2 emissions. In comparison, second and third generation biofuels offer greater potential for GHG mitigation through use of cellulosic feedstocks which originate from production systems that tend to have less land-use related GHG emissions. Additionally, biochar – the co-product of pyrolysis?, is carbon rich and stable, and when added to soil it serves as a long-term carbon bank. While second, third, and even fourth generation biofuel systems potentially reduce GHGs they are not yet widely available at commercial scales and future demand is uncertain.

Wildlife habitat and biodiversity

Bioenergy and biomass crops are often promoted by environmentalists and government leaders as having the potential to provide tremendous amounts of wildlife habitat and to support biodiversity. Several important studies provide evidence of the negative impacts of first generation biofuel on wildlife and biodiversity (e.g., Brooke et al., 2009; Meehan et al., 2010) while others provide evidence that biopower? and second generation biofuels have positive effects on wildlife and biodiversity (e.g., Meehan et al., 2010; Robertson et al.,2011; Roth et al., 2005). However, policies to outline environmental standards for bioenergy production are lacking, and financial programs for compensating land owners and farmers for habitat- and biodiversity-protecting land practices are also lacking. Most significantly, land conversion could decrease native habitats, reduce biodiversity and decrease ecosystem services?. Key issues are habitat loss and fragmentation with expanding corn and soybean acres; loss of Conservation Reserve Program land; persistence of pesticides in the environment associated with conventional row crops; timing of harvest of perennial crops and forests; and impacts to water quality associated with agricultural run-off.

Figure 5. Grassland bird nest in mixed perennial biomass production field in central Wisconsin. (Photo by Andrew XXXX, 2010.)

Water quantity and quality

Bioenergy potentially impacts water resources through two pathways: water use in biomass production and water use during feedstock conversion. Emission of air pollutants from biopower combustion and burning of biofuels also potentially impacts water quality mostly via precipitation. However, water use potentially has the greatest effect on water availability and water quality. The impact of bioenergy to water is often referred to as the “water footprint”.

In areas where there is sufficient precipitation biomass yields may be close to yield potential. However, in areas lacking sufficient precipitation irrigation is required for achieving commercially viable yields. Use of irrigation water has the potential to depress groundwater supplies, divert water used to grow food crops to the growth of energy crops, and contribute to soil salinization. In both irrigated and rainfed systems, crops that remain longer on the landscape (i.e., perennial) and crops which provide good ground cover increase structural filtering of precipitation promoting more rainfall interception and retention and better control of sediment run-off. Grasslands?, once established, may provide better water services than traditional annual row crops because of greater soil coverage and root density.

In addition to sediment run-off, pesticides and fertilizers associated with conventional row crop production threaten water resources. One of the top pollutants to aquatic ecosystems, as recognized by the U.S. EPA, is nitrogen. Nitrogen in excess can be harmful to both ecosystem and human health. Nitrogen (N) and other agronomic pollutants like phosphorous (P), can enter water resources through runoff and leaching. Nutrient pollution is a leading cause of water quality impairment in lakes and the Gulf of Mexico. The major concern for surface water polluted with N and P, is the promotion of algal growth (eutrification) accompanied by aquatic oxygen depletion, fish mortality, clogged pipelines, and reduced recreational values.

Figure 6. A comparison of water use in production of ethanol versus other industrial processes. (US EPA.)

Water use in conversion of feedstock to bioenergy also has potential negative impacts on water availability and quality. Biopower generation requires use of water to produce high-pressure steam to drive turbines and low-pressure steam to deliver heat/cooling in centralized heating/cooling districts. Some biopower plants also use water for cooling, particularly in co-firing of coal or natural gas with biomass. Water is also required during fermentation of ethanol and in post-transesterification of biodiesel (figure 6). Also, effluents from these processes must be treated before being discharged to nearby surface waters. Water use for fermentation may deplete surrounding surface or groundwater supplies and limit their availability for other uses including drinking water, wildlife habitat, and recreation.

Anerobic Digestion and Biogas

UW Extension have created seven modules focused on the use of anaerobic digestion technologies. Details of the process are introduced, as well as factors that influence start-up, operation and control of anaerobic digesters at different scales.

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Carol Williams clwilliams4@wisc.edu
(608) 890-3858 (office)
(515) 520-7494 (mobile)
Department of Agronomy
1575 Linden Dr.
University of Wisconsin, Madison, WI 53706

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A visit to switchgrass? trial plots run by Iowa State University researchers; near Ames, IA. Photo by CL Williams, 2010.