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Using The Budget Constraint To Monetarise Impact Assessment Results

机译:使用预算约束来衡量影响评估结果

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Recent developments in Life Cycle Impact Assessment (LCIA) provide a basis for reducing the uncertainty in monetarisation of environmental impacts. The LCIA method "Ecoindicator99" provides impact pathways ending in a physical score for each of the three safeguard subjects humans, ecosystems, and resources. We redefine these damage categories so that they can be measured in terms of Quality Adjusted Life Years (QALYs) for impacts on human well-being, Biodiversity Adjusted Hectare Years (BAHYs) for impacts on ecosystems, and monetary units for impacts on resource productivity. The monetary value of a QALY can be derived from the budget constraint, i.e. the fact that the average annual income is the maximum that an average person can pay for an additional life year. Since a QALY by definition is a life-year lived at full well-being, the budget constraint can be determined as the potential annual economic production per capita at full well-being. We determine this to be 74,000 EUR with an uncertainty estimate of 62,000 to 84,000 EUR. This corresponds well to the 74,627 EUR willingness-to-pay estimate of the ExternE project. Differences to other estimates can be explained by inherent biases in the valuation approaches used to derive these estimates.rnThe value of ecosystems can be expressed in monetary terms or in terms of QALYs, as the share of our well-being that we are willing to sacrifice to protect the ecosystems. While this trade-off should preferably be done by choice modelling, only one such study was found at the level of abstraction that allows us to relate BAHYs to QALYs or monetary units. Stressing the necessity for such studies, we resort to suggest a temporary proxy value of 1400 EUR/ BAHY (or 52 BAHY/QALY), with an uncertainty range of 350 to 3500 EUR/BAHY. The practical consequences of the above-described monetarisation values has been investigated by combining them with the midpoint impact categories of two recent LCIA methods, thus providing a new LCIA method with the option of expressing results in both midpoints and an optional choice between QALY and monetary units as endpoint. From our application of the new method to different case studies, it is noteworthy that resource impacts obtain less emphasis than in previous LCIA methods, while impacts on ecosystems obtain more importance. This shows the significance of being able to express impacts on resources and ecosystems in the same units as impacts on human well-being.
机译:生命周期影响评估(LCIA)的最新发展为减少环境影响货币化的不确定性提供了基础。 LCIA方法“ Ecoindicator99”为人类,生态系统和资源这三个保障主题的每一个提供以物理评分结尾的影响路径。我们重新定义了这些损害类别,以便可以根据对人类福祉的影响的质量调整生命年(QALY),对生态系统的影响的生物多样性调整公顷年(BAHY)和对资源生产力的影响的货币单位来衡量它们。 QALY的货币价值可以从预算约束中得出,即平均年收入是普通人可以为额外的生命年支付的最大值。由于从定义上来说,QALY是生活在充分健康状态下的生命年,因此可以将预算约束条件确定为在充分健康状态下人均潜在的年经济生产量。我们确定这是74,000欧元,不确定性估计为62,000到84,000欧元。这与ExternE项目的74,627欧元的支付意愿很相称。与其他估计的差异可以用得出这些估计的估值方法中的固有偏差来解释。rn生态系统的价值可以用货币或QALY表示,因为我们愿意牺牲的福祉所占份额保护生态系统。虽然这种权衡最好应通过选择模型进行,但在抽象层次上仅发现了一项这样的研究,使我们能够将BAHY与QALY或货币单位相关联。强调进行此类研究的必要性,我们求助于建议临时代理价格为1400欧元/百威(或52个BAHY / QALY),不确定性范围为350至3500欧元/百威。通过将上述货币化价值与两种最近的LCIA方法的中点影响类别结合起来,对上述货币化价值的实际后果进行了研究,从而提供了一种新的LCIA方法,可以在中点和结果中均表示结果,并且可以选择在QALY和货币之间进行选择单位作为端点。从我们对新方法的应用到不同的案例研究,值得注意的是,与以前的LCIA方法相比,资源影响的重视程度更低,而对生态系统的影响则更为重要。这表明了能够以与人类福祉影响相同的单位表达对资源和生态系统的影响的重要性。

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