Using surface water for irrigation purposes and disturbing local species through the noise and light produced at a processing site both impact biodiversity directly. In relation to shadow carbon pricing, which of the following is incorrect?单项选择题
A
Shadow carbon pricing is used to conceal the true cost of an entity's carbon emissions.
B
Shadow carbon pricing is used to create a theoretical cost per ton of carbon emissions by establishing a business's internal price on carbon
C
Shadow carbon pricing is used to understand potential impact of external prices on the profitability of a project
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Question at position 40 Which of the following represent negative externalities from the Fishbanks simulation (this question has multiple answers) Loss of fish species that could affect the health of the ocean ecosystemLoss of public services in the local communities as a result of lost tax revenue from the bankrupt fishing businessesImpact on those ocean species dependent on the fish populationClosing down of restaurants and other small businesses in the local communityThe loss of your jobs as managers of these fishing companies
Which of the following is an example of quasi-option value?
For this question, consider an asymmetric externality. The utility possibility frontier depicted in Figure 5 below maps the downstream party without the property on the vertical axis and the upstream party with the property right on the horizontal axis. Point B represents the outcome with exploitation of the ecosystem (Nash Bargaining impasse point) prior to Payments for Ecosystem Services (PES). Point E is the outcome with conservation but without PES and without a Pareto-efficient solution, and Point F is an outcome with PES and with a Pareto-efficient solution. Figure 5: Payments for Ecosystem Services Which line segment best represents the maximum willingness to pay (WTP) by the downstream party without the property right (vertical axis) for a move from E to F in Figure 5 above?
For this question, please refer to Figure 2 below. Consider whales that could be harvested (private good) or conserved (public good). Figure 2: Optimal Mix Increasing international environmentalism, especially in the early 1970s, simultaneously shifted preferences in favor of whale conservation and against commercial use of whale products. This shift is represented in Figure 2 as:
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