Biological Carbon Sequestration and Carbon Trading Re-Visited

Under Kyoto, biological activities that sequester carbon can be used to create CO2 offset credits that could obviate the need for lifestyle-changing reductions in fossil fuel use. Credits are earned by storing carbon in terrestrial ecosystems and wood products, although CO2 emissions are also mitigated by delaying deforestation, which accounts for one-quarter of anthropogenic CO2 emissions. However, nonpermanent carbon offsets from biological activities are difficult to compare with each other and with emissions reduction because they differ in how long they prevent CO2 from entering the atmosphere. This is the duration problem; it results in uncertainty and makes it difficult to determine the legitimacy of biological activities in mitigating climate change. While there is not doubt that biological sink activities help mitigate climate change and should not be neglected, in this paper we demonstrate that these activities cannot be included in carbon trading schemes.carbon offset credits, climate change, duration of carbon sinks, Environmental Economics and Policy,

Biological Carbon Sequestration and Carbon Trading Re-visited

Under Kyoto, biological activities that sequester carbon can be used to create CO2 offset credits that could obviate the need for lifestyle-changing reductions in fossil fuel use. Credits are earned by storing carbon in terrestrial ecosystems and wood products, although CO2 emissions are also mitigated by delaying deforestation, which accounts for one-quarter of anthropogenic CO2 emissions. However, non-permanent carbon offsets from biological activities are difficult to compare with each other and with emissions reduction because they differ in how long they prevent CO2 from entering the atmosphere. This is the duration problem; it results in uncertainty and makes it difficult to determine the legitimacy of biological activities in mitigating climate change. While there is not doubt that biological sink activities help mitigate climate change and should not be neglected, in this paper we demonstrate that these activities cannot be included in carbon trading schemes.carbon offset credits from biological activities, climate change, duration of carbon sinks

Biotechnology in Agriculture and Forestry: Economic Perspectives

Economists are rarely brought into the interdisciplinary research until the biophysical scientists have developed their models, made their measurements or completed their research task. The research economist is then brought in to do what amounts to a consulting task – provide some numbers that indicate impacts on the economy and employment. In this paper, I begin by illustrating cases from forestry where this leads to erroneous and costly policy outcomes. However, the main objective of this paper is to examine the role of genetic engineering in forestry and agriculture. In forestry, planting of genetically-modified (GM) tree species is nearly non-existent, with the exception of hybrid poplar that is used to produce pulp or fuel. However, as explored here, there is a role for GM tree varieties, particularly ones that are resistant to such things as the mountain pine beetle which has adversely impacted forests in British Columbia. I also examine the role of GM crops in addressing concerns about future food scarcity. As discussed here, there are various factors that suggest the world might encounter future scarcity. These include on the demand side a growing and wealthier global population, and greater demand for energy crops. On the supply side, there are fewer opportunities to expand farmland at the extensive margin, a decline in the rate of increase in productivity, limits to the amounts of inputs that can be applied at the intensive margin, and the closing of the gap between actual and potential crop yield. GM crops are one way to circumvent the potential shortages. However, there are many obstacles that need to be overcome before farmers globally can take advantage of transgenic research, including most importantly barriers put up by the European Union and various environmental NGOs on the grounds of the precautionary principle. These are discussed in some detail.precautionary principle; economics of genetically-modified organisms; agriculture and forestry; mountain pine beetle

Wind Power: The Economic Impact of Intermittency

Wind is the fastest growing renewable energy source for generating electricity, but economic research lags behind. In this study, therefore, we examine the economics of integrating large-scale wind energy into an existing electrical grid. Using a simple grid management model to investigate the impact of various levels of wind penetration on grid management costs, we show that costs of reducing CO2 emissions by relying more on wind power depend on the generation mix of the existing electricity grid and the degree of wind penetration, with costs ranging from $21 to well over$1000 per tonne of CO2 reduced. Costs are lowest if wind displaces large amounts of fossil fuel production and there is some hydroelectric power to act as a buffer. Hydro capacity has the ability to store wind generated power for use at more opportune times. If wind does nothing more than replace hydro or nuclear power then the environmental benefits (reduced CO2 emissions) of investing in wind power are small.Wind power, carbon costs, electricity grids, mathematical programming

A Dynamic Bioeconomic Model of Ivory Trade: Details and Extended Results

Trade in ivory is banned under CITES in an effort to protect the African elephant. The trade ban is supported by some range states, most notably Kenya, because they see the ban as an effective means for protecting a ‘flagship’ species, one that attracts tourists and foreign aid. It is opposed by some states, mainly in southern Africa, because their elephant populations are exceeding the capacity of local ecosystems with culling and other sources have resulted in the accumulation of large stocks of ivory. They argue that ivory trade will benefit elephant populations. The question of whether an ivory trade ban will protect elephant populations is addressed in this paper using a dynamic partial-equilibrium model that consists of four ivory exporting regions and a single demand region. Results indicate that a trade ban might not be successful in maintaining elephant populations, even if it leads to a stigma effect that reduces demand and increases the marginal costs of marketing ivory. The modeling results suggest that the species will survive only if the non-market value of elephants is taken into account. If rich countries compensate African range states according to marginal willingness to pay for elephants, optimal populations are lower than under an average payment, and, perhaps surprisingly, the interaction between tourism benefits and marginal compensation can lead to the demise of elephants in some regions where this would not occur otherwise. Finally, elephant populations are even projected to crash if range states can operate an effective quota scheme, even one that excludes poaching. Free trade in ivory and effective institutions that translate numbers of elephants into monetary payments may be the best hope for the elephant.economics of elephant conservation, economics of ivory trade, trade bans, cartels and quota

Economic Analysis of Feed-in Tariffs for Generating Electricity from Renewable Energy Sources

Feed-in tariffs, renewable energy

Biological Carbon Sinks: Transaction Costs and Governance

Activities that remove CO2 from the atmosphere and store it in forest and agricultural ecosystems can generate CO2-offset credits that can thus substitute for CO2 emissions reduction. Are biological CO2-uptake activities competitive with CO2 offsets from reduced fossil fuel use? In this paper, it is argued that transaction costs impose a formidable obstacle to direct substitution of carbon uptake offsets for emissions reduction in trading schemes, and that separate caps should be set for emissions reduction and sink-related activities. While a tax/subsidy scheme is preferred to emissions trading for incorporating biologically-generated CO2 offsets, contracts that focus on the activity and not the amount of carbon sequestered are most likely to lead to the lowest transaction costs.carbon sequestration; transaction costs; climate change

Elephants and the Ivory Trade Ban: Summary of Research Results

economics of elephant conservation, economics of ivory trade,trade bans

Resolving Range Conflict in Nevada? The Potential for Compensation via Monetary Payouts and Grazing Alternatives

In response to environmental pressure, public land agencies in Nevada have reduced animal unit months (AUMs) of grazing on public lands. This has resulted in economic losses to ranchers, increased conflict between ranchers and the public land agencies, and general unrest in the ranch community. One approach to resolving the problems might be to compensate ranchers for lost grazing privileges. In this study, we employ the results of the Nevada Ranch Survey to examine ranchers’ willingness to accept a one-time payment to retire grazing rights, as well as three other means of “compensating” ranchers that enable them to earn a living from the public lands despite reduced access to public forage. The results suggest that ranchers are not keen on being compensated in any form, expressing a desire to continue ranching. However, those most amenable to compensation and a reworking of the social contract are those who have the best relationship with the public land manager and view the public agencies in a positive light.range economics, environmental services from public land, compensation for grazing rights, social capital and trust

CAN DOMESTICATION OF WILDLIFE LEAD TO CONSERVATION? THE ECONOMICS OF TIGER FARMING IN CHINA

Tigers are a threatened species that might soon disappear in the wild. Not only are tigers threatened by deteriorating and declining habitat, but poachers continue to kill tigers for traditional medicine, decoration pieces and so on. Although international trade in tiger products has been banned since 1987 and domestic trade within China since 1993, tigers continue to be poached and Chinese entrepreneurs have established tiger farms in anticipation of their demise. While China desires to permit sale of tiger products from captive-bred tigers, this is opposed on the grounds that it likely encourages illegal killing. Instead, wildlife conservationists lobby for more spending on anti-poaching and trade-ban enforcement. In this study, a mathematical bioeconomic model is used to investigate the issue. Simulation results indicate that, unless range states are characterized by institutions (rule of law, low corruption) similar to those found in the richest countries, reliance on enforcement alone is insufficient to guarantee survival of wild tigers. Likewise, even though conservation payments could protect wild tigers, the inability to enforce contracts militates against this. Our model indicates that wild tigers can be protected by permitting sale of products from tiger farms, although this likely requires the granting of an exclusive license to sellers. Finally, it is possible to tradeoff enforcement effort and sale of products from captive-bred animals, but such tradeoffs are worsened by deteriorating tiger habitat.endangered species and extinction, wildlife farming, economics of natural, mathematical bioeconomics, Environmental Economics and Policy, Q27, C61, Q57,