US energy system configurations are changing at an unprecedented rate. Increasing environmental concerns and energy security worries, as well as falling prices, have contributed to the growth of renewable energy in the United States. Because renewable energy has become more feasible to develop over the past decade, it now competes more successfully against fossil fuels. Given that this trend is likely to continue, more land will be required to site renewable energy projects. Public lands cover large portions of the American West, and therefore the issue of renewable energy siting on western public lands carries great significance.
Davis (2001) identifies three factors that explain the dynamics of fossil energy development on public lands: (1) interest group tensions, (2) political party configurations, and (3) bureaucratic procedures. The first two factors are contested areas. First, the divergence of interests among industry groups and environmentalists results in lobbying battles over preferable policy outcomes. Second, partisanship influences the course of action in the energy policy domain—generally, Republicans tend to adopt pro-business policies that favor the fossil fuel industry, while Democrats tend to be more attentive to environmental consequences.
Compared to fossil fuel policy dynamics, renewable energy policy developments are to some extent less contentious, yet they present some unique challenges. In terms of interest group involvement, both business and environmental coalitions generally support renewable energy development. As illustrated below, however, a unique set of clashes between environmental groups—known as the “green versus green” phenomenon—has been growing recently (Yonk et al. 2013). Furthermore, despite overall public support for renewable energy development, some local communities do not welcome such development proposals (Pierce and Steel 2017). In terms of political party alignments, renewable energy enjoys bipartisan support because it helps achieve environmental goals as well as national energy security and economic development goals. Finally, federal agencies responsible for project permitting processes have been active in improving and expediting procedures pertaining to siting of renewable energy.
This chapter first presents a synopsis of the legislative shift toward renewable energy development is depicted. Second, it provides an overview of regulatory regimes regarding solar, wind, geothermal, and biomass development on public lands. Third comes a snapshot of solar, wind, geothermal, and biomass developments on western public lands. Finally, I outline the controversy regarding renewable energy siting on public lands, including case studies of wind and geothermal energy projects.
Movement toward Renewable Energy Development
Bernell and Simon (2016) maintain that energy systems in the United States have a major task of ensuring energy security, further specifying the following four goals in that task. The first is to safeguard abundance of energy resources that can guarantee widespread access to energy. The second goal for the energy system actors is to guarantee reliability, which implies that consumers will continue to have undisrupted access to energy sources. The third goal is to ensure affordability of energy sources, that is, that customers have access to energy at reasonable and predicted costs. The fourth goal is to achieve the system’s sustainability. Goals can also change over time. In the early twentieth century, the main goal was to provide access to electricity at affordable prices. More recently, concerns over dangers posed by climate change have elevated the importance of energy sustainability.
Advanced energy systems are often associated with societal progress, yet they are also responsible for negative consequences. Burning of fossil fuels (coal, oil, and natural gas) contributes to negative health-related impacts. In addition, climate change due to carbon dioxide emissions associated with the burning of fossil fuels is also an enormous and challenging global issue. The Fifth Assessment Report prepared by the Intergovernmental Panel on Climate Change (2014) states that “human influence on the climate system is clear and growing.” A decrease in the use of fossil fuels and an increase of renewable energy generation can reduce both negative health-related impacts and carbon dioxide emissions.
External shocks and crises also significantly affect energy policy. According to Grossman (2015, p. 57), “in the United States progress on energy policy requires a crisis.” In response to an energy crisis caused by the oil embargo of 1973 declared by the Organization of Arab Petroleum Exporting Countries, the US Congress passed the National Energy Act of 1978. The act aimed to reduce the country’s dependence on fossil fuels by supporting the domestic development of alternative fuel sources and promoting energy efficiency and conservation. One of the most important sections of the act was the Public Utility Regulatory Policies Act (PURPA), which brought significant changes to the governing mechanisms of the US electricity sector. Most notably, PURPA created a regulatory framework enabling electricity production from renewable sources by nonutility players. The legislation was resisted by traditional energy players who questioned the legality of PURPA in court. The Supreme Court decision ultimately upheld the rule (Shively and Ferrare 2008).
Given the great importance of having stable and sufficient sources of energy, the Arab oil embargo was a disruptive force for a global economy deeply dependent on energy: “The embargo also sparked a fundamental shift in the definition of energy supply, from a solely technological problem to a bundle of social ones” (Rosa et al. 1988, p. 164). Since the 1970s (following the first oil embargo), the issue of energy diversification became more critical. Concerns over unimpeded access to energy sources and issues pertaining to the finite nature of fossil fuels led to policies aimed to diversify energy production.
The Persian Gulf War of 1990-1991 and several abrupt oil price increases in the late 1980s and early 1990s once again demonstrated the importance of stable access to energy resources. To further enhance resource diversification and domestic renewable energy production, the US Congress passed the Energy Policy Act of 1992. The act created financial assistance for renewable energy development and incentives for the commercialization of renewable energy technologies. Among other provisions, the act introduced a number of significant regulatory changes that set the state for the deregulation of the energy sector. A host of new players emerged in the energy market, including independent power producers procuring renewable energy sources (Shively and Ferrare 2008).
In addition to significant changes in energy policy owing to shocks and crises, substantial modifications can occur without major external disruptions. Mahoney and Thelen (2010, p. 2) underline that incremental endogenous processes can bring about shifts in a policy subsystem. Incremental policy changes cumulatively work toward accomplishing a larger goal (i.e., different institutional changes and policy initiatives increase the prospects for energy sustainability). Governments adopt a broad range of policies that affect energy markets, including financial incentives and regulations affecting energy production and actions limiting or altering consumption patterns (Geri and McNabb 2016).
In the 1970s, environmentalists achieved significant progress in pushing for environmental legislation. A number of major environmental protection acts were adopted during that time, including the Clean Air Act, the Clean Water Act, the Endangered Species Act, the National Environmental Policy Act, and the National Forest Management Act. Several policy provisions have also incrementally increased the utilization of renewable energy sources. First, federal financial incentives—such as the Renewable Electricity Production Tax Credit (PTC) and Business Energy Investment Tax Credit (ITC)—have had a goal to increase the share of renewable energy in the national energy mix. Second, the adoption of regulatory mandates (renewable portfolio standards or renewable portfolio goals) by US states has stimulated the use of renewable energy technologies. Even western states, excluding Idaho and Wyoming, have regulatory policies in place mandating that electric utilities operating in the state procure a certain percentage of electricity using renewable energy sources by a certain year. The most ambitious renewable portfolio standard was adopted by the California State Legislature in 2018, which increased the required level of renewables from 50% to 60% by 2030 and introduced an additional target of 100% of electricity from renewable energy resources and zero-carbon resources by 2045 (California Public Utilities Commission 2020). In some states (e.g., Utah), however, the regulatory provisions are not mandatory and require that utilities procure a certain percentage of renewable energy only if it is “cost-effective” (Database of State Incentives for Renewables and Efficiency 2018).
In addition to federal and state measures, regional agreements have promoted the use of renewable energy. The West Coast Governors’ Global Warming Initiative of 2003 and the succeeding Pacific Coast Action Plan on Climate and Energy of 2013 signed by the governors of California, Oregon, and Washington and the premier of British Columbia have demonstrated the regional agreement to coordinate efforts in reducing greenhouse gas emissions and to increase the use of renewable energy sources. The governors from the aforementioned jurisdictions have also actively participated in the Governors’ Global Climate Summits held in partnership with the United Nations Environmental Programme (UNEP) (Pierce and Steel 2017).
History of Regulatory Context
The US Department of the Interior—including the Bureau of Land Management (BLM), the Minerals Management Service (MMS), the US Geological Survey (USGS), and the US Forest Service—is the main manager of public lands that host a majority of renewable energy projects. The BLM authorizes wind and solar energy development; in turn, geothermal energy projects are processed by the BLM, the MMS, and the USGS; and biomass energy development is managed by the US Forest Service. Several federal policy acts comprise the regulatory base for the permitting process of renewable energy projects. Table 11.1 provides a list of major policy acts affecting renewable energy development on public lands.
Table 11.1. List of Major Public and Land Use Policies That Regulate the Development of Renewable Energy on Public Lands
|Federal Law||Impact on Renewable|
|National Historic Preservation Act of 1966||Ensures the preservation of historical and cultural foundations; as a result, some portions of public lands may excluded from a pool of potential sites for renewable energy development|
|National Environmental Policy Act of 1969, Endangered Species Act of 1973, and National Forest Management Act of 1976||Guarantee environmental protection, as a result, some portions of public lands may be excluded from a pool of potential sites for renewable energy development.|
|Geothermal Steam Act of 1970||Regulates the authorization process of geothermal energy projects.|
|Federal Land Policy and Management Act of 1976||Establishes procedures for land-use planning processes on public lands.|
|Energy Policy Act of 2005||Provides incentives fro renewable energy development on public lands.|
The federal government has encouraged renewable energy development on public lands in a number of ways. Section 211 of the Energy Policy Act of 2005 signed into law by President George W. Bush mandates that “the Secretary of the Interior should, before the end of the 10-year period beginning on the date of enactment of this Act, seek to have approved non-hydropower renewable energy projects located on the public lands with a generation capacity of at least 10,000 megawatts of electricity.”1 President Obama’s Climate Action Plan of 2013 directed the US Department of the Interior to permit 10,000 megawatts of renewables on public lands by 2020 (in addition to previously mandating 10,000 megawatts of renewable energy by 2012, which was achieved by the US Department of the Interior ahead of schedule) (Executive Office of the President 2013).
Wind and Solar
Title V of the Federal Land Policy and Management Act of 1976, as amended, and Title 43 of the Code of Federal Regulations authorize the permitting process of wind and solar energy projects under rights-of-way grants (Bureau of Land Management 2019a). In addition, the National Environmental Policy Act, the Endangered Species Act, the National Historic Preservation Act of 1966, and the Tribal Consultation requirements regulate siting procedures of wind and solar energy projects.
In 2005, the BLM issued the Wind Energy Development Final Programmatic Environmental Impact Statement, which provided guidelines for assessing environmental impacts of wind energy development on public lands in the western United States (Bureau of Land Management 2005). In addition, in 2008, the BLM released guidelines on processing wind energy authorizations and summaries of best management practices of wind energy siting, which aimed at mitigating the impact on avian habitat and other potential wildlife threat as well as alleviating any resource conflicts (Bureau of Land Management 2018b).
The West-Wide Wind Mapping Project is an example of the BLM’s effort to identify areas with high wind energy generation potential and low resource conflict to make the siting process less complicated. The West-Wide Wind Mapping Project identifies areas across eleven states of the American West that (1) possess high potential for wind energy generation, (2) are located in land-use exclusion zones, and (3) elicit high environmental concerns and generate other potential resource conflicts (West-Wide Wind Mapping Project 2019). This systematic classification of public lands helps the stakeholders anticipate possible siting complications.
There are restrictions in terms of the type of land that can be utilized for renewable energy development. For example, lands located within the BLM’s National Landscape Conservation System face restrictions for solar energy development; likewise, lands located within Areas of Critical Environmental Concern may be unavailable for solar energy development (Bureau of Land Management 2018a). In 2007, the BLM issued an instruction memorandum (IM) for the processing of right-of-way applications for solar energy development projects on public lands, superseding the agency’s Solar Energy Development Policy of 2004. The IM explicated in a great detail the authorization process in the hopes of encouraging renewable energy development according to the goals of the National Energy Policy of 2001 and the Energy Policy Act of 2005 as well as ensuring environmentally responsible developments (Bureau of Land Management 2007).
In 2012, the BLM launched the Solar Energy Program (known as the Western Solar Plan) to facilitate utility-scale solar energy development on public lands in six southwestern states (Arizona, California, Colorado, Nevada, New Mexico, and Utah). The program was based on the Final Programmatic Environmental Impact Statement (PEIS) for Solar Energy Development in Six Southwestern States (Solar PEIS) prepared by the BLM and the US Department of Energy (DOE) as well as nineteen cooperating agencies, including various federal-, state-, and county-level entities. More than 200,000 public comments were received on a series of drafts of this document (Bureau of Land Management and US Department of Energy 2012). Solar PEIS established systematic guidelines designed to make the permitting process of utility-scale solar energy projects more efficient and to maximize the mitigation of potential environmental impacts (Bureau of Land Management and US Department of Energy 2012).
In addition, the BLM identified nineteen solar energy zones (SEZs) in six southwestern states as areas “well suited for utility-scale production of solar energy, where the BLM will prioritize solar energy and associated transmission infrastructure development” (Bureau of Land Management 2014). If fully developed, SEZs would provide 27,000 megawatts of solar energy, which is equivalent to the amount of energy necessary to power about eight million homes (US Department of the Interior 2016).
In 2017, the BLM amended existing regulatory guidelines for wind and solar energy development on public lands by enacting the Solar and Wind Rule. The rule expanded the BLM’s prerogative to employ a competitive bidding processes on lands for wind and solar development. It also brought the BLM fee structure for new wind and solar energy development in line with existing market conditions (Bureau of Land Management 2019b). In addition, the rule promoted the development of designated leasing areas (DLAs) that would be preferred for solar and wind energy development. These areas would have high energy generation potential, access to transmission lines, and low resource conflict (Bureau of Land Management 2016). In short, this provision aimed to simplify the application process and enhance renewable energy development at sites with fewer resource conflicts (Block 2016).
The Geothermal Steam Act of 1970, as amended, regulates the authorization process of geothermal energy projects on public lands under competitive leasing procedures (Bureau of Land Management 2019a). The Energy Policy Act of 2005 substantially amended the Geothermal Steam Act. Section 225 of the act required the BLM and the Forest Service to issue an interagency memorandum of understanding (MOU) to advance coordination in the leasing and permitting process of geothermal energy applications. The MOU, officially issued in 2006, focused on reducing the lease application backlog by 90% in five years and established a shared database for tracking applications (Bureau of Land Management and US Forest Service 2016).
Section 226 of the Energy Policy Act of 2005 required the USGS to update a geothermal resource assessment first introduced in 1978. The assessment projected the region’s total geothermal energy potential and identified areas with the most geothermal energy development promise (Aird 2006).
In 2003, an MOU between the US Department of the Interior, the US Department of Agriculture, and the US Department of Energy established the Biomass Research and Development Board with the goal to promote wood biomass development (Aird 2006). Section 210 of the Energy Policy Act of 2005 authorized grants for biomass energy projects (guaranteeing $20 per green ton of biomass delivered). These projects were to be located in preferred communities, including areas near federal lands “at significant risk of catastrophic wildfire, disease, or insect infestation or which suffers from disease or insect infestation.”2 To establish eligibility for the federal grants, Section 210 of the act defined biomass as “nonmerchantable materials or precommercial thinnings that are byproducts of preventive treatments, such as trees, wood, brush, thinnings, chips, and slash, that are removed—(A) to reduce hazardous fuels; (B) to reduce or contain disease or insect infestation; or (C) to restore forest health.”3
Wind, Solar, Geothermal, and Biomass Energy Developments on Western Public Lands
Wind energy is the United States’ largest source of renewable energy besides hydropower. The first utility-scale wind energy project on public lands was approved by the Bureau of Land Management in 1982—the 40-megawatt Cabazon Wind Energy Facility in Riverside County, California. As of November 2018, the BLM had approved thirty-five wind energy projects located on public lands with a total capacity of 3,249 megawatts, which is sufficient to power about one million homes. Twenty-eight of the approved projects are in California, having a total capacity of 944 megawatts; two projects are in Wyoming with a total capacity of 1,521 megawatts; two projects are in Arizona with a total capacity of 530 megawatts; two projects are in Utah with a total capacity of 100 megawatts; one project is in Nevada with a capacity of 150 megawatts; and one project is in Oregon with a capacity of 4 megawatts. The approved projects range widely in size and capacity—from the 3-megawatt wind energy facilities in California to the 1,500-megawatt Chokecherry and Sierra Madre Wind Energy Project in Carbon County, Wyoming (Bureau of Land Management 2019e).
The southwestern United States possesses tremendous solar energy potential. The first utility-scale solar energy project on public lands was approved by the BLM in 2010—the 50-megawatt Silver State North thin film photovoltaic system in Clark County, Nevada. As of November 2018, the Bureau of Land Management approved twenty-eight solar energy projects located on public lands with a total capacity of 7,171 megawatts, which is sufficient to power about two million homes. Sixteen of the approved projects are in California, having a total capacity of 5,261 megawatts; nine projects are in Nevada with a total capacity of 1,430 megawatts; two projects are in Arizona with a total capacity of 400 megawatts; and one project is in Wyoming with a capacity of 80 megawatts. The approved projects range widely in size and capacity, from the 20-megawatt Ocotillo Sol photovoltaic system on 100 acres of public lands in Imperial County, California, to the 750-megawatt McCoy Solar Project on 7,700 acres of public lands in Riverside County, California (750 megawatts approved and 250 megawatts in operation), and the 550-megawatt Desert Sunlight Solar Farm on 4,165 acres of public lands in Riverside County, California (all 550 megawatts are in operation) (Bureau of Land Management 2019d).
California possesses the largest amount of geothermal energy potential in the United States because it is located on the Pacific’s “ring of fire” and because of tectonic plate conjunctions (California Energy Commission 2020). The first utility-scale geothermal energy project on public lands was approved by the BLM in 1978: the 30-megawat Geysers Units 5&6 and the 30-megawatt Geysers Units 7&8 in Lake County, California. As of March 2018, the Bureau of Land Management approved fifty geothermal energy projects located on public lands with a total capacity of 1,648 megawatts. Out of all approved projects, twenty-five projects are in California with a total capacity of 664 megawatts, twenty-one projects are located in Nevada with a total capacity of 867 megawatts, two projects are located in Utah with a total capacity of 70 megawatts, one project with a capacity of 32 megawatts is located in Idaho, and one project with a capacity of 15 megawatts is located in New Mexico. The approved projects widely range in size and capacity—from the smallest 4-megawatt San Emidio geothermal plant in Washoe County, Nevada, to the largest 120-megawatt Salt Wells Vulcan projects in Churchill County, Nevada (Bureau of Land Management 2019c).
The US Energy Information Administration (2019a) reported that about 2% of US energy consumption in 2017 was from wood and wood waste. Shelly (2011) identifies several sources of woody biomass, including (1) nontimber tree removal (dead trees and trees preventing land and urban development); (2) forest management (small-diameter tree removal related to hazard fuel treatment, precommercial thinning related to timber production, and forest health improvement); (3) timber harvesting residues; (4) wood manufacturing residues (sawdust, bark, defective wood pieces); and (5) fast-growing tree plantations. Western states significantly differ in the extent of wood biomass utilization: Pacific coastal states utilize significantly larger amounts of woody biomass compared to the Rocky Mountain region and the four corner states (Arizona, Colorado, New Mexico, and Utah) (Nicholls et al. 2018). Thirty-two electric-generating facilities that use woody biomass feedstocks are located in western states with a total capacity of 847 megawatts, including eighteen facilities in California with a total capacity of 457 megawatts, six facilities in Washington with a total capacity of 193 megawatts, five facilities in Oregon with a total capacity of 156 megawatts, one facility in Arizona with a total capacity of 27 megawatts, one facility in Colorado with a total capacity of 11.5 megawatts, and one facility in Montana with a total capacity of 3 megawatts (Nicholls et al. 2018). In the western United States, issues pertaining to forest have been strongly debated for decades, and environmental opposition has occurred to proposals for biomass energy facilities (Sundstrom et al. 2012).
Renewable Energy Siting Controversy
Despite wide public support for renewable energy development, in some cases the siting of renewable energy facilities proves problematic because of opposition from surrounding communities and environmental organizations. Specifically, the siting of wind energy farms has sparked a significant amount of controversy. This controversy occurs when local ecosystems or the quality of life of the surrounding community are threatened (Pierce and Steel 2017).
Opposition to wind energy projects has been extensively studied by scholars around the world examining Canadian, European, New Zealand, and US contexts. Scholars identified several groups of factors that help explain opposition to proposed projects. First, procedural factors have an effect on how proposed projects are perceived by the surrounding communities. Trust in developers and government agencies is likely to increase the project’s acceptance. In addition, community member perceptions on whether decisions are made in an unbiased manner and whether communities are treated fairly determine attitudes toward the project development process (Bidwell 2013). Second, the distribution of positive and negative outcomes of wind energy development on the surrounding community affects the project siting process. Among positive outcomes are the creation of new local jobs and increased tax revenue, while negative outcomes include visual and noise pollution, wildlife threats, public health and safety issues, local infrastructure damage, and decreasing property values (Fischlein et al. 2013; Groth and Vogt 2014; Jones and Eiser 2010). Finally, community-unique contextual factors play a role in the siting process (e.g., past community experiences with energy facility siting and differences in community identity). Devine-Wright (2009) argues that community place attachment and symbolic meanings influence attitudes toward wind energy projects.
Environmental organizations occasionally fight renewable energy developments when they are seen as damaging to local ecosystems (Pierce and Steel 2017). For instance, the Audubon Society has opposed wind and solar energy projects on the basis of potential negative avian impacts—an example of a “green versus green” clash (Yonk et al. 2013). In some cases, however, the biocentric environmental organizations coordinate efforts with developers and regulators in the search of appropriate habitat mitigation solutions.
Giordono et al. (2018) conducted a systematic analysis of fifty-three proposals for wind energy development in California, Idaho, Oregon, and Washington to identify the amount of opposition and understand the processes that affect it. The research concluded that “while some level of local opposition to wind proposals is not rare, it is typically restricted to more benign activities that require few resources and take place in standard institutional settings” (Giordono et al. 2018, p. 119). Specifically, in most cases, opposition was represented by writing letters to the editor and providing comments on drafts of environmental impact assessments, while protests and lawsuits were rare forms of opposition. The following case studies further illustrate this phenomenon.
The Cotterel Mountain Wind Energy Project
In 2001, Boise-based Windland, Inc., in partnership with Shell Wind Energy, filed a right-of-way application to build the 200-megawatt Cotterel Mountain Wind Farm in Cassia County, Idaho. The project site was located mainly on public lands that were managed by the BLM. Residents of Albion, Idaho, a nearby town, became concerned with potential visual impacts, wildlife threats, and negative economic effects associated with the proposed wind energy facility. Twelve residents joined their efforts in opposing the project and created the Committee against Windmills in Albion. The group gathered 224 signatures to sign a petition against the project (Giordono et al. 2018).
In 2005, a draft environmental impact statement was issued and made available to the public. Seventy-two written comments were submitted during the comment period. The comments raised a number of issues related to the proposed project. Several key issues were addressed in detail: sage grouse habitat conservation, protection of tribal treaty rights, mitigation of potential impacts on migratory birds and threatened or endangered species, maintenance of public access to the land, protection of visual resources, and ensuring consistency with the Cassia County Resource Management Plan of 1985. About twenty other issues and concerns were considered, although not as extensively as the key issues. In 2006, the BLM prepared the final environmental impact statement specifying the agency’s preferred alternative: the project to be constructed with actions taken to mitigate wildlife issues and concerns (Bureau of Land Management 2006). In 2012, however, the developers decided not to proceed with the project and withdrew their application. In summary, this case is an example of the trade-offs between the needs to produce low-carbon energy sources and the potential negative impacts on a surrounding community and ecosystem. In addition, this is also an example of low-level opposition to wind energy projects.
The Newberry Crater Geothermal Energy Project
Geothermal energy is an important energy source because it emits low levels of air pollution and carbon dioxide. Compared to power plants that use fossil fuels, geothermal power plants emit 97% less sulfur compounds, which contribute to acid rains, and 99% less carbon dioxide, which drives climate change (US Energy Information Administration 2019b). At the same time, geothermal energy provides a consistent energy supply, unlike solar and wind energy sources that are intermittent in their nature. But some geothermal energy projects have sparked controversy owing to their potential local environmental impacts (Pierce and Steel 2017). The case of the Newberry Crater Geothermal Energy Project details how siting processes occur.
The proposed site for the Newberry Crater Geothermal Energy Project is in central Oregon, near the Newberry Volcano, about twenty miles southeast of Bend, Oregon. The project has had a long development history but has not been built to date. The project has been developed by Davenport Power and AltaRock Energy in partnership with a wide range of organizations such as GE Global Research, Lawrence Berkeley National Laboratory, Oregon State University, Pacific Northwest National Laboratory, Statoil, Texas A&M, Temple University, the University of Oregon, the University of Utah, and the US Geological Survey (Grasso 2016; Petty 2010).
Several governmental bodies have overseen the project’s permitting process, including the US Bureau of Land Management, the US Department of Energy, the US Forest Service, the Oregon Department of Energy, and several other Oregon agencies (Petty 2010). A number of policy and regulatory acts have comprised the regulatory base for the permitting process: the National Environmental Policy Act of 1969, the Geothermal Steam Act of 1970, the National Forest Management Act of 1976, the Federal Land Policy and Management Act of 1976, the Energy Policy Act of 2005, and the Programmatic Environmental Impact Statement for Geothermal Leasing in the Western US of 2008. In addition, in 1990, Congress issued an act that established the Newberry National Volcanic Monument. The act restricted geothermal energy development inside the monument and provided guidance for geothermal development in the adjacent areas.4
In 2007, Davenport Power obtained a permit from the BLM for an exploratory well-drilling program. The program involved road maintenance and pad preparation (three five-acre well pads), which required clearing trees and compacting the ground. The well pads were situated on federal geothermal leases west of the Newberry National Volcanic Monument (Davenport Power 2008). In 2008, the developer submitted a notice of intent to obtain a site certificate for a geothermal energy facility with a 35- to 45-megawatt capacity and a 12-mile transmission line to a Bonneville Power Administration substation near the town of La Pine, Oregon. The proposed project site was located outside of the Newberry National Volcanic Monument (Oregon Department of Energy 2008). Several public meetings were held by the government agencies to familiarize the public with the proposed project and siting procedures (Davenport Power 2008).
In 2009, Davenport Energy in partnership with AltaRock received a $21 million federal matching grant through the American Recovery and Reinvestment Act for the development of the Newberry Enhanced Geothermal System (EGS) Demonstration Project. The goal of the project was to test the EGS technology with the possibility of applying it later at other sites. The developers submitted to the BLM a notice of intent for developing the Demonstration Project to test the EGS technology. As required by the National Environmental Policy Act, the project was subject to environmental analysis, conducted by the BLM, the US Department of Energy, and the US Forest Service. A number of public meetings were held at different locations in central Oregon (Bend, La Pine, and Sunriver) (Bureau of Land Management 2011). The BLM issued a draft environmental assessment, which received seven comments from nongovernmental organizations and government entities (Blue Mountain Biodiversity Project, Central Oregon Land Watch, the Klamath Tribe, Leaning Pine Ranch, the Northwest Environmental Defense Center, Oregon Wild, and Region 10 of the Environmental Protection Agency) and four comments from private individuals (Bureau of Land Management 2011). The final environmental assessment identified several “key issues” regarding the project development: (1) safety of the EGS technology; (2) issues related to water quantity and water quality; (3) earthquake risks; (4) impacts to the Newberry National Volcanic Monument; (5) potential visual impact; and (6) threats to wildlife.
As required by the National Environmental Policy Act, the BLM, the Department of Energy, and the Forest Service conducted the environmental assessment to either issue a finding of no significant impact (FONSI) or to prepare an environmental impact statement (EIS). In April 2012, the authorities issued a FONSI concluding that no significant environmental impacts would take place. As a result, the developers were allowed to begin construction of the Newberry Enhanced Geothermal System Demonstration Project (Bureau of Land Management 2012). The Demonstration Project has the goal of providing information on the economic viability of developing a 35-megawatt geothermal energy facility at the Newberry site. Currently, the Newberry Geothermal Energy (NEWGEN) team, a joint partnership of AltaRock Energy, Oregon State University, and Pacific Northwest National Laboratory, continues efforts to make progress on the project, although no final date has been issued for its completion. Obtaining adequate financial resources for the project remains a significant challenge (AltaRock Energy 2019).
Renewable energy development is on the rise in the United States. More public lands, especially in the American West, will be identified as possible sites of renewable energy projects. Development of solar, wind, geothermal, and biomass energy is a less contentious area compared to development of fossil fuels. Both business and environmental coalitions are largely in favor of renewable energy development. In addition, renewable energy generally enjoys bipartisan support because it serves several societal goals (i.e., national energy security, economic development, and environmental protection). Furthermore, federal agencies responsible for permitting of renewable energy projects have made significant efforts to create more efficient siting procedures and mitigate potential negative impacts associated with renewable energy developments. Yet siting of renewable energy projects occasionally meets some unique challenges. Specifically, environmental organizations and local communities in some cases oppose proposed projects. Several factors may play a role in increased contentiousness: (1) procedural factors (lack of trust and unfair siting procedures); (2) factors related to uneven distribution of positive and negative outcomes associated with renewable energy developments; and (3) community-unique contextual factors. Thus scholars and policymakers should stay attuned to the challenge of finding a balance between the need to produce low-carbon energy sources and mitigating impacts on local communities and the ecosystem.
- Public Law 109-58.
- Energy Policy Act of 2005, 119 STAT 594, Pub. L. No. 109-58 (2005). To Establish the Newberry National Volcanic Monument in the State of Oregon, and for Other Purposes, 104 STAT 2288, Pub. L. No. 101-522 (1990).
- Energy Policy Act of 2005, 119 STAT 594, Pub. L. No. 109-58 (2005).
- Energy Policy Act of 2005, 119 STAT 594, Pub. L. No. 109-58 (2005).
Aird, Brenda. 2006. “The Role of Federal Government and Federal Lands in Fueling Renewable and Alternative Energy in America: Hearings before the Subcommittee on Energy and Mineral Resources of the House Resources Committee.” Office of Congressional and Legislative Affairs, Department of the Interior, April 6, 2006. https://www.doi.gov/ocl/Renewable-Energy. (↵ Return 1) (↵ Return 2)
AltaRock Energy. 2019. “Newberry Geothermal Energy (NEWGEN), Oregon.” Accessed November 12, 2019. http://altarockenergy.com/projects/newberry-geothermal-energy-newgen/. (↵ Return)
Bernell, David, and Christopher A. Simon. 2016. The Energy Security Dilemma: US Policy and Practice. New York: Routledge. (↵ Return)
Bidwell, David. 2013. “The Role of Values in Public Beliefs and Attitudes towards Commercial Wind Energy.” Energy Policy 58: 189–99. (↵ Return)
Block, Greg. 2016. “Creating a Path for Renewable Energy on Public Lands.” The Hill, November 17, 2016. https://thehill.com/blogs/congress-blog/energy-environment/306509-creating-a-path-for-renewable-energy-on-public-lands. (↵ Return)
Bureau of Land Management. 2005. Final Programmatic Environmental Impact Statement on Wind Energy Development on BLM-Administered Lands in the Western United States. Washington, DC: Bureau of Land Management. http://windeis.anl.gov/eis/index.cfm. (↵ Return)
Bureau of Land Management. 2006. Final Environmental Impact Statement for the Proposed Cotterel Wind Power Project. Washington, DC: Bureau of Land Management. https://archive.org/details/finalenvironment02twin. (↵ Return)
Bureau of Land Management. 2011. Wildlife Report: Newberry Volcano Enhanced Geothermal System (EGS) Demonstration Project. Washington, DC: Bureau of Land Management. http://www.blm.gov/or/districts/prineville/plans/files/Wildlife_Report.pdf. (↵ Return 1) (↵ Return 2)
Bureau of Land Management. 2012. Decision Record: Newberry Volcano Enhanced Geothermal System (EGS) Demonstration Project. Washington, DC: Bureau of Land Management.http://www.blm.gov/or/districts/prineville/plans/newberry/files/Newberry_EGS_Demo_Project_Decision_Record.pdf. (↵ Return)
Bureau of Land Management. 2016. “Competitive Processes, Terms, and Conditions for Leasing Public Lands for Solar and Wind Energy Development and Technical Changes and Corrections.” December 19, 2016. https://www.federalregister.gov/documents/2016/12/19/2016-27551/competitive-processes-terms-and-conditions-for-leasing-public-lands-for-solar-and-wind-energy. (↵ Return)
Bureau of Land Management. 2018a. “BLM Fact Sheet. Renewable Energy: Solar.” Updated March, 2018. https://www.blm.gov/sites/blm.gov/files/Solar%20Fact%20Sheet.pdf. (↵ Return)
Bureau of Land Management. 2018b. “BLM Fact Sheet. Renewable Energy: Wind.” Updated March, 2018. https://www.blm.gov/sites/blm.gov/files/Wind%20Fact%20Sheet.pdf. (↵ Return)
Bureau of Land Management. 2019a. “New Energy for America.” Accessed November 20, 2019. https://www.blm.gov/programs/energy-and-minerals/renewable-energy. (↵ Return 1) (↵ Return 2)
Bureau of Land Management. 2019b. “Laws and Regulations.” Accessed November 12, 2019. https://www.blm.gov/programs/energy-and-minerals/renewable-energy/laws. (↵ Return)
Bureau of Land Management. 2019c. “Geothermal Energy.” Accessed November 12, 2019. https://www.blm.gov/programs/energy-and-minerals/renewable-energy/geothermal-energy. (↵ Return)
Bureau of Land Management. 2019d. “Solar Energy.” Accessed November 12, 2019. https://www.blm.gov/programs/energy-and-minerals/renewable-energy/solar-energy. (↵ Return)
Bureau of Land Management. 2019e. “Wind Energy.” Accessed November 12, 2019. https://www.blm.gov/programs/energy-and-minerals/renewable-energy/wind-energy. (↵ Return)
Bureau of Land Management and US Department of Energy. 2012. Final Programmatic Environmental Impact Statement (PEIS) for Solar Energy Development in Six Southwestern States. Washington, DC: Bureau of Land Management and US Department of Energy. http://solareis.anl.gov/documents/fpeis/Solar_FPEIS_ExecutiveSummary.pdf. (↵ Return 1) (↵ Return 2)
Bureau of Land Management and US Forest Service. 2016. Memorandum of Understanding: Implementation of Section 225 of the Energy Policy Act of 2005 Regarding Geothermal Leasing and Permitting. Washington, DC: Bureau of Land Management and US Forest Service. https://openei.org/wiki/Memorandum_of_Understanding_between_DOI_and_DOA_-_Implementation_of_Section_225_of_the_Energy_Policy_Act_of_2005_Regarding_Geothermal_Leasing_and_Permitting. (↵ Return)
California Energy Commission. 2020. “California Geothermal Energy Statistics & Data.” Accessed February 8, 2020. https://www.energy.ca.gov/almanac/renewables_data/geothermal/. (↵ Return)
Database of State Incentives for Renewables and Efficiency. 2018. “Renewable Portfolio Goal.” Last updated July 3, 2018.http://programs.dsireusa.org/system/program/detail/2901. (↵ Return)
Davenport Power. 2008. “Newberry Geothermal Project Update.” https://www.wou.edu/las/physci/taylor/newberry/NEWBERRY_GEOTHERMAL_NEWS_2008.pdf. (↵ Return 1) (↵ Return 2)
Davis, David H. 2001. “Energy on Federal Lands.” In Western Public Lands and Environmental Politics, edited by C. Davis, 141–68. Boulder, CO: Westview Press. (↵ Return)
Devine‐Wright, Patrick. 2009. “Rethinking NIMBYism: The Role of Place Attachment and Place Identity in Explaining Place‐Protective Action.” Journal of Community & Applied Social Psychology 19 (6): 426–41. (↵ Return)
Executive Office of the President. 2013. The President’s Climate Action Plan. Washington, DC: Executive Office of the President. https://obamawhitehouse.archives.gov/sites/default/files/image/president27sclimateactionplan.pdf. (↵ Return)
Fischlein, Miriam, Elizabeth J. Wilson, Tarla R. Peterson, and Jennie C. Stephens. 2013. “States of Transmission: Moving towards Large-Scale Wind Power.” Energy Policy 56: 101–13. (↵ Return)
Geri, Laurance R., and David E. McNabb. 2016. Energy Policy in the US: Politics, Challenges, and Prospects for Change. Boca Raton, FL: CRC Press. (↵ Return)
Giordono, Leanne S., Hilary S. Boudet, Anna Karmazina, Casey L. Taylor, and Brent S. Steel. 2018. “Opposition ‘Overblown’? Community Response to Wind Energy Siting in the Western United States.” Energy Research & Social Science 43: 119–31. (↵ Return 1) (↵ Return 2) (↵ Return 3)
Grasso, Kyla. 2016. Newberry Geothermal Energy: A Candidate Site for the DOE FORGE. Salem: Oregon Department of Energy. https://www.oregon.gov/energy/energy-oregon/Documents/2016%20OGWG%20AltaRock%20Presentation.pdf. (↵ Return)
Grossman, Peter Z. 2015. “Energy Shocks, Crises and the Policy Process: A Review of Theory and Application.” Energy Policy 77: 56–69. (↵ Return)
Groth, Theresa M., and Christine Vogt. 2014. “Residents’ Perceptions of Wind Turbines: An Analysis of Two Townships in Michigan.” Energy Policy 65: 251–60. (↵ Return)
Intergovernmental Panel on Climate Change. 2014. Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change, edited by R. K. Pachauri and L. A. Meyer. Geneva: Intergovernmental Panel on Climate Change. (↵ Return)
Jones, Christopher R., and J. Richard Eiser. 2010. “Understanding ‘Local’ Opposition to Wind Development in the UK: How Big Is a Backyard?” Energy Policy 38(6): 3106–17. (↵ Return)
Mahoney, James, and Kathleen Thelen, eds. 2010. “A Theory of Gradual Institutional Change.” In Explaining Institutional Change: Ambiguity, Agency, and Power. Cambridge: Cambridge University Press. (↵ Return)
Nicholls, David L., Jeffrey Halbrook, Michelle E. Benedum, Han-Sup Han, Eini C. Lowell, Dennis R. Becker, and R. James Barbour. 2018. “Socioeconomic Constraints to Biomass Removal from Forest Lands for Fire Risk Reduction in the Western US.” Forests 9(5): 264. (↵ Return 1) (↵ Return 2)
Oregon Department of Energy. 2008. “Minutes: Energy Facility Siting Council Meeting.” July 25, 2008. http://www.oregon.gov/energy/Siting/docs/Minutes/EFSC_7-25-08.pdf. (↵ Return)
Petty, S. 2010. Geothermal Energy Protecting the Environment—and Our Future. Seattle: AltaRock Energy. http://altarockenergy.com/projectupdates/WhitePaper.pdf. (↵ Return 1) (↵ Return 2)
Pierce, John C., and Brent S. Steel. 2017. Prospects for Alternative Energy Development in the US West: Tilting at Windmills? Vol. 8. New York: Springer. (↵ Return 1) (↵ Return 2) (↵ Return 3) (↵ Return 4) (↵ Return 5)
Rosa, Eugene A., Gary E. Machlis, and Kenneth M. Keating. 1988. “Energy and Society.” Annual Review of Sociology 14(1): 149–72. (↵ Return)
Shelly, John R. 2011. Woody Biomass Factsheet—WB1. Berkeley: University of California Berkeley. http://www.ucanr.org/sites/WoodyBiomass/newsletters/InfoGuides43284.pdf. (↵ Return)
Shively, Bob, and John Ferrare. 2008. Understanding Today’s Electricity Business. Laporte, CO: Enerdynamics Corp. https://www.enerdynamics.com/ProductDetails.aspx?ProductID=4. (↵ Return 1) (↵ Return 2)
Sundstrom, Shiloh, Max Nielsen-Pincus, Cassandra Moseley, and Sarah McCaffery. 2012. “Woody Biomass Use Trends, Barriers, and Strategies: Perspectives of US Forest Service Managers.” Journal of Forestry 110(1): 16–24. (↵ Return)
US Energy Information Administration. 2019a. “Biomass Explained: Wood and Wood Waste.” Last updated May 13, 2019. https://www.eia.gov/energyexplained/index.php?page=biomass_wood. (↵ Return)
US Energy Information Administration. 2019b. “Geothermal Explained: Geothermal Energy and the Environment.” Last updated December 5, 12, 2019. https://www.eia.gov/energyexplained/geothermal/geothermal-energy-and-the-environment.php. (↵ Return)
Yonk, Ryan M., Randy T. Simmons, and Brian C. Steed. 2013. Green vs. Green: The Political, Legal, and Administrative Pitfalls Facing Green Energy Production. New York: Routledge. (↵ Return 1) (↵ Return 2)