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环境成本【外文翻译】

环境成本【外文翻译】
环境成本【外文翻译】

外文文献翻译译文

原文:

Environmental Costs

Today, the importance of the environment is widely recognized by companies. With an increase in environmental legislation, corporations realize that they have to factor the environment into their everyday management decisions. However, because some corporations are too focused on earnings and financial costs, the impact of their operations on the environment can only be taken into account if it is quantified in dollar terms —this is significant since environmental costs are often grossly underestimated. According to a 2006 Statistic Canada study, Canadian firms are estimated to have spent a total of $8.6 billion on environmental protection, including 44per cent for capital expenditures and 56 per cent for operating expenditures. This underestimation is due to widespread “hidden” costs. In a study published in 2001, U.S. researcher revealed that for every dollar of environmental costs identified as such by companies, there were hidden environmental costs of $10. Companies can’t manage what they can’t measure; therefore, they need to measure their environmental costs in order to manage and reduce them; or perhaps, turn environmental management into a strategic advantage.

What to include in environmental costs

The first challenge is how to define environmental costs. One solution is to use a classification developed by the United States Environmental Protection Agency in 1995. This classification makes a distinction between internal costs (borne by a company) and external costs (assumed by society as a whole, but generated by the company’s operations). Internal costs include conventional costs (e.g., direct and indirect materials, energy, etc.), potentially hidden costs (e.g., site investigation and preparation, audit, disclosure of information, follow-up of data, etc.), potential costs (e.g., penalties, fines, legal fees, etc.) and costs related to corporate image and relationships (e.g., reputation, campaign to influence perceptions, etc.). Moreover, external costs refer to environ mental degradation and to adverse impacts for

humanbeings, their property and their welfare. There is a debate about whether or not external costs should be part of corpora cost management. However, more stringent regulations in terms of environmental liability are increasingly internalizing costs that have heretofore been considered external. This distinction between internal and external costs is crucial to measuring environmental costs.

Life-cycle costing, environmental balance, full-cost accounting, total-cost accounting and activity-based costing are costing methods used by companies. These methods are not mutually exclusive and a number of parameters are common to several methods.

Life-cycle costing

Life-cycle costing is based on a more global approach of life-cycle analysis. There are two major methods based on a product’s life cycle, e.g. from research and development to disposal (the “cradle to grave” approach) or its reuse/ recycling by the producer (the “cradle to cradle” or C2C approach), tak ing into account factors such as transportation. Life-cycle analysis, a method recognized by ISO 14000 standards, consists in analyzing each and every flow of input and output materials for each product. More specifically, in environmental terms, this approach analyzes the actual and potential impacts of these flows on the environment. As such, it includes three stages: (i) an inventory of all flows related to energy, water, raw materials, air and emissions; (ii) a follow-up of the qualitative or quantitative measure of the induced environmental impact; and (iii) an interpretation of the results and an assessment of opportunities for reducing environmental impacts. This approach only makes it possible to include environmental impacts, and not environmental costs.

Life-cycle costing recognizes the environmental costs generated by a company throughout a product’s life cycle, using two types of analysis jointly (on a weighted or unweighted basis) or individually: (i) the financial life-cycle cost that discounts monetary impacts from the environment to the firm, and (ii) the environmental life-cycle cost that monetizes all environmental impacts that were identified during the life-cycle analysis, e.g., impaired resources. Life-cycle costing demonstrates that costs can be several times higher than investments over a product’s life cycle. This

makes life-cycle costing especially relevant for products with a long lifespan or with relatively high operating costs, such as real estate and highways. In addition, the discounting of costs, e.g. the recognition of time, makes it possible to compare the costs of two products. However, this advantage may also be the main drawback of this method, as it raises the problem of correctly planning for future costs and selecting an appropriate discount rate. In fact, discounting specific environmental costs is controversial, since environmental impacts increase over time. It is therefore not unusual for costs to be nil today, but exceedingly high a few years from now, which is contrary to the very principle of discounting. Accordingly, discounting environmental costs could lead to minimizing financial interest for projects that reduce future environmental costs.

Moreover, these two methods raise the same problem of uncertainty as to future repercussions. It may be a good idea to use sensitivity analyses, scenarios, and ranges to allow for the probability that certain contingencies will occur. A more meaningful restriction relates to the fact that these methods exclude consideration of all types of costs. Intangible costs, including those driven by relations with stakeholders, are not considered, nor are contingent costs, since it is not easy to relate such costs to a specific phase in the life-cycle of a product, making it highly improbable that they will be included in life cycle methods.

Environmental balance

The environmental balance method consists in identifying, and then measuring, the flows of inputs and outputs of a firm, a service, a process or a product in terms of energy, water, materials, waste or emissions. It can therefore be used at the inventory stage of the life-cycle analysis or as an initial step of many other methods. The underlying assumption of this method is based on the law of conservation of thermodynamic masses—total inputs are by definition equal to total outputs plus the net accumulation of materials in the system. All inputs become outputs, hence the term “balance.” The part of a flow that actually goes into the production of goods can be used to indicate the percentage loss of materials and, accordingly, the opportunities to improve the production process. Similarly, a large number of

environmental performance indicators can be determined from the data produced by an environmental balance. Traditionally, an environmental balance is performed in physical, non-monetary terms (kilograms, kilowatts, etc.). Moreover, a sub-category of environmental balance, called material flow analysis (MFA), allows a company to include an allocation stage of flows to each of its various products.

Two major criticisms have been levelled at the environmental balance method. First, its input/output analyses fail to measure environmental impacts, as they relate strictly to a company’s use of natural resources without regard to their valu e for the environment. The second major criticism is that this method fails to provide monetary information. However, the value of flows could be estimated in monetary terms if required. In addition, the environmental balance is generally used only as a prerequisite to the use of other methods.

Full-cost accounting

The full cost represents an allocation of all costs to a product (materials, labour, overhead, etc.) including potential and actual environmental costs. With this approach, it is possible to obtain enhanced operational knowledge and to select products with a lower cost (whether it be environmental or not). However, in environmental terms, full cost often refers to a consideration of the monetary value of external costs. This raises the problem of how complex it is to monetize the cost of externalities.

Total-cost assessment

The total-cost assessment method, developed by the Tellus Institute, is similar to full-cost accounting. Whereas the latter approach is generally used to measure the cost of products, total-cost assessment is often carried out to measure the cost of capital investments. Additionally, the classification of costs used for a total-cost assessment requires the identification of costs that are specifically related to the environment. The full-cost accounting method deals with all of the costs related to a product, and does not require that environmental costs be identified.

The major advantage of total-cost assessment is that it includes more of the costs relating to a capital investment or a product than life-cycle costing, e.g. intangible and contingent costs, while still taking the entire life cycle into account. Thus, it measures

direct and indirect costs, contingent and intangible costs with due consideration for risks and, accordingly, the related probabilities that they will occur. In addition, external costs can be included in a total-cost assessment, and this method can be applied simply by using software containing a database to assess external costs related to pollutants and compute them according to the probability that they will occur. Activity-based costing

One of the primary problems with measuring and managing environmental costs is related to the allocation of such costs to the activities or products that generated them. In fact, many companies treat environmental costs as overhead and don’t identify them as related to the environment, which contributes heavily to the underestimation of environmental costs. Activity-based costing can therefore enable a firm to allocate environmental costs to activities, and then to products, overcoming any inaccuracies related to their inclusion in overhead. It should be noted, though, that using this approach requires the prior identification of environmental costs. Activity-based costing can be used the traditional way or by inserting an “environmental” driver to allocate environmental costs either to activities first and products second, or from an “environmental” activity to the products that generate the costs.

How to measure external environmental costs

Although there are several methods to measure external costs, the three major methods are: 1) control costs, 2) restoration costs and 3) damage costs.

1) Control costs

The underlying assumption for this method is that the cost of environmental impacts (including pollution) for a company would be equal to the cost of installing, operating and maintaining technologies that might have enabled the company to avoid such damage to the environment. The logic is based on marginal cost, e.g. the cost of an additional unit of damage is estimated by the cost that the company would have been required to spend to avoid such damage. This is the most simple method of measuring external costs, and the easiest to justify, as it generates the cost that a company would actually have incurred to avoid the production of externalities or that

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DISCLAIMER This report was prepared as an account of work sponsored by an agency of the United States。Government. Neither the United States Government nor any agency thereof, nor any of their employees, makes any warranty, express or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, or represents that its use would not infringe privately owned rights. Reference herein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Government or any agency thereof. The views and opinions of authors expressed herein do not necessarily state or reflect those of the United States Government or any agency thereof. Evolution of an Environmental Audit Program Joseph H. Maday, Jr. (ASQC-CQA) Technical Group Leader - Quality Verification Department and Tapio Kuusinen Senior Research Scientist Environmental Policy and Compliance Group Pacific Northwest Laboratory Richland, Washington 99352

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Costcontrol成本控制外文翻译

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