环境会计【外文翻译】

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企业环境成本会计外文翻译

企业环境成本会计外文翻译

企业环境成本会计外文翻译ACCOUNTING IN SMALL AND MEDIUM-SIZEDCOMPANIES1.ENVIRONMENTAL COST ACCOUNTING IN SMESSince its inception some 30 years ago, Environmental Cost Accountin g (ECA) has reached a stage of development where individual ECA syste ms are separated from the core accounting system based an assessment of environmental costs with (see Fichter et al., 1997, Letmathe and Wagner , 2002).As environmental costs are commonly assessed as overhead costs, nei ther the older concepts of full costs accounting nor the relatively recent o ne of direct costing appear to represent an appropriate basis for the imple mentation of ECA. Similar to developments in conventional accounting, th e theoretical and conceptual sphere of ECA has focused on process-based accounting since the 1990s (see Hallay and Pfriem, 1992, Fischer and Bla sius, 1995, BMU/UBA, 1996, Heller et al., 1995, Letmathe, 1998, Spengl er and H.hre, 1998).Taking available concepts of ECA into consideration, process-based c oncepts seem the best option regarding the establishment of ECA (see He upel and Wendisch , 2002). These concepts, however, have to be continuo usly revised to ensure that they work well when applied in small and me dium-sized companies.Based on the framework for Environmental Management Accounting presented in Burritt et al. (2002), our concept of ECA focuses on two ma in groups of environmentally related impacts. These are environmentally i nduced financial effects and company-related effects on environmental syst ems (see Burritt and Schaltegger, 2000, p.58). Each of these impacts relat e to specific categories of financial and environmental information. The e nvironmentally induced financial effects are represented by monetary environmental information and the effects on environmental systems are represe nted by physical environmental information. Conventional accounting deals with both –monetary as well as physical units –but does not focus on environmental impact as such. To arrive at a practical solution to the implementation of ECA in a company’s existing accounting system, and t o comply with the problem of distinguishing between monetary and physi cal aspects, an integrated concept is required. As physical information is often the basis for the monetary information (e.g. kilograms of a raw mat erial are the basis for the monetary valuation of raw material consumptio n), the integration of this information into the accounting system database is essential. From there, the generation of physical environmental and mo netary (environmental) information would in many cases be feasible. For many companies, the priority would be monetary (environmental) informati on for use in for instance decisions regarding resource consumptions and investments. The use of ECA in small and medium-sized enterprises (SM E) is still relatively rare, so practical examples available in the literature are few and far between. One problem is that the definitions of SMEs va ry between countries (see Kosmider, 1993 and Reinemann, 1999). In our work the criteria shown in Table 1 are used to describe small and mediu m-sized enterprises.Table 1. Criteria of small and medium-sized enterprisesNumber of employees TurnoverUp to 500 employees Turnover up to EUR 50mManagement Organization- Owner-cum-entrepreneur -Divisional organization i s rare- Varies from a patriarchal management -Short flow of inform ation stylein traditional companies and teamwork -Strong personal commitm entin start-up companies -Instruction and controllin g with- Top-down planning in old companies direct personal contact- Delegation is rare- Low level of formality- High flexibilityFinance Personnel- family company -easy to survey number of employees- limited possibilities of financing -wide expertise-high satisfaction of employeesSupply chain Innovation-closely involved in local -high potential of innovati oneconomic cycles in special fields- intense relationship with customersand suppliersKeeping these characteristics in mind, the chosen ECA approach shou ld be easy to apply, should facilitate the handling of complex structures a nd at the same time be suited to the special needs of SMEs.Despite their size SMEs are increasingly implementing Enterprise Res ource Planning (ERP) systems like SAP R/3, Oracle and Peoplesoft. ERP systems support business processes across organizational, temporal and geo graphical boundaries using one integrated database. The primary use of E RP systems is for planning and controlling production and administrationprocesses of an enterprise. In SMEs however, they are often individually designed and thus not standardized making the integration of for instance software that supports ECA implementation problematic. Examples could b e tools like the “eco-efficiency”approach of IMU (2003) or Umberto (2 003) because these solutions work with the database of more comprehensi ve software solutions like SAP, Oracle, Navision or others. Umberto softw are for example (see Umberto, 2003) would require large investments and great background knowledge of ECA –which is not available in most SMEs.The ECA approach suggested in this chapter is based on an integrati ve solution –meaning that an individually developed database is used, a nd the ECA solution adopted draws on the existing cost accounting proce dures in the company. In contrast to other ECA approaches, the aim was to create an accounting system that enables the companies to individually obtain the relevant cost information. The aim of the research was thus to find out what cost information is relevant for the company’s decision o n environmental issues and how to obtain it.2.METHOD FOR IMPLEMENTING ECASetting up an ECA system requires a systematic procedure. The proje ct thus developed a method for implementing ECA in the companies that participated in the project; this is shown in Figure 1. During the impleme ntation of the project it proved convenient to form a core team assigned with corresponding tasks drawing on employees in various departments. S uch a team should consist of one or two persons from the production dep artment as well as two from accounting and corporate environmental issue s, if available. Depending on the stage of the project and kind of inquiry being considered, additional corporate members may be added to the pro ject team to respond to issues such as IT, logistics, warehousing etc.Phase 1: Production Process VisualizationAt the beginning, the project team must be briefed thoroughly on the current corporate situation and on the accounting situation. To this end, t he existing corporate accounting structure and the related corporate inform ation transfer should be analyzed thoroughly. Following the concept of an input/output analysis, how materials find their ways into and out of the company is assessed. The next step is to present the flow of material and goods discovered and assessed in a flow model. To ensure the complete ness and integrity of such a systematic analysis, any input and output is t o be taken into consideration. Only a detailed analysis of material and en ergy flows from the point they enter the company until they leave it as p roducts, waste, waste water or emissions enables the company to detect c ost-saving potentials that at later stages of the project may involve more efficient material use, advanced process reliability and overview, improved capacity loads, reduced waste disposal costs, better transparency of costs and more reliable assessment of legal issues. As a first approach, simplifi ed corporate flow models, standardized stand-alone models for supplier(s), warehouse and isolated production segments were established and only c ombined after completion. With such standard elements and prototypes def ined, a company can readily develop an integrated flow model with produ ction process(es), production lines or a production process as a whole. Fr om the view of later adoption of the existing corporate accounting to EC A, such visualization helps detect, determine, assess and then separate pri mary from secondary processes.Phase 2: Modification of AccountingIn addition to the visualization of material and energy flows, modelin g principal and peripheral corporate processes helps prevent problems invo lving too high shares of overhead costs on the net product result. The flo w model allows processes to be determined directly or at least partially i dentified as cost drivers. This allows identifying and separating repetitiveprocessing activity with comparably few options from those with more lik ely ones for potential improvement.At manufacturing companies participating in the project, computer-inte grated manufacturing systems allow a more flexible and scope-oriented pr oduction (eco-monies of scope), whereas before only homogenous quantitie s (of products) could be produced under reasonable economic conditions (economies of scale). ECA inevitably prevents effects of allocation, compl exity and digression and becomes a valuable controlling instrument where classical/conventional accounting arrangements systematically fail to facilit ate proper decisions.Thus, individually adopted process-based accounting produces potential ly valuable information for any kind of decision about internal processing or external sourcing (e.g. make-or-buy decisions).Phase 3: Harmonization of Corporate Data –Compiling and Acquisi tionPhase 4: Database conceptsWithin the concept of a transparent accounting system, process-based accounting can provide comprehensive and systematic information both on corporate material/ energy flows and so-called overhead costs. To deliver reliable figures over time, it is essential to integrate a permanent integrat ion of the algorithms discussed above into the corporate information syste m(s). Such permanent integration and its practical use may be achieved b y applying one of three software solutions (see Figure 2).For small companies with specific production processes, an integrated concept is best suited, i.e. conventional and environmental/process-oriente d accounting merge together in one common system solution.For medium-sized companies, with already existing integrated producti on/ accounting platforms, an interface solution to such a system might be suitable. ECA, then, is set up as an independent software module outsidethe existing corporate ERP system and needs to be fed data continuousl y. By using identical conventions for inventory-data definitions within the ECA software, misinterpretation of data can be avoided.Phase 5: Training and CoachingFor the permanent use of ECA, continuous training of employees on all matters discussed remains essential. To achieve a long-term potential o f improved efficiency, the users of ECA applications and systems must be able to continuously detect and integrate corporate process modifications and changes in order to integrate them into ECA and, later, to process th em properly.中小企业环境成本会计的实施一、中小企业的环境成本会计自从成立三十年以来,环境成本会计差不多进展到一定时期,环境会计成本体系差不多从以环境成本评估为基础的会计制度核心中分离出来(参考Fichter et al., 1997, Letmathe 和Wagner , 2002)。

外文:环境会计

外文:环境会计

环境会计我们现在在哪里,我们将走向何方作者:Joy E. Hecht国民收入核算制度不断改变,利率处于上升趋势,增加对经济和环境之间联系的理解。

环境成本会计领域取得了大的进步是在过去20年里,成为数十个几个国家一个变化而神秘的努力,并且在一些国家建立起来。

但是这种观点可能结合国家的经济作用账目环境问题纳入他们的收入,既不是快速销售,也不是很快的过程,自从20世纪60年代就已经进行讨论。

尽管本文介绍了困难和争议,但是利息在不断变化的国民收入核算体系中增长,以促进了解的经济与环境的关系为什么要改变?世界各国政府在发展被称为国民收入账户经济数据系统作为计算总的宏观经济指标,例如国内产品。

建设一个国家的经济把环境放入这样一个账户,是对一些明显的作为国家确定、联合国与国际通用的账户的弊端在全国系统账户体系(SNA)的一个回应。

SNA的一个缺陷往往是他们对环境的保护成本无法确定。

因此,花的钱,比如说,把污染控制设备的烟囱来算作增加国内生产总值,即使开支不是经济生产,一些争论这样说。

这些批评者要求从其他人的账户内区分“防御性”的支出。

更误导人的是,事实上一些环境商品没有被销售,虽然他们提供了经济价值。

薪材聚集在森林,肉类和鱼类聚集消费,药用植物就是例子。

那么,饮用水和灌溉水,其销售价格反映分配和处理基础设施的成本,而不是水本身。

虽然有些国家也把这些商品放在的国民收入账户中,但是没有这样做的标准存在。

当商品包括在账目中,他们仍然不能被从那些有销售的中分辨出来。

衡量是环境服务困难的,例如的水的保护由森林承担,和农作物是由昆虫提供的。

虽然有些专家呼吁将其列入对环境调整账目,通常既没有经济价值,也不是服务退化涵盖的。

另一方面,然而,替代品和服务的需要,以取代他们,例如水处理植物,对GDP是有贡献的,可是令人误解。

还有一个问题是,国家收入账户对待制造折旧资本和自然折旧资本是不同的。

体育资本建筑物或一台机器,例如,在计算折旧按照传统的会计核算原则,而所有的自然是资本消耗计为收入。

环境会计文章翻译

环境会计文章翻译

DOI:10.1007/s00267-003-2625-2PROFILEEconomic Values and Corporate Financial StatementsV ANESSA MAGNESSSchool of Business ManagementRyerson University350VictoriaSt.Toronto, Ontario M5B2K3, CanadaABSTRACT/Corporate financial statements do not include environmental values. This deficiency has contributed to the criticism that company managers do not include environmental impacts in the internal decision-making process. The accounting profession has not developed effective environmental reporting guidelines. This situation contributes to a second problem: the apparent inability of corporate reports to provide useful information to external parties. It has been suggested that by using nonmarket valuation methodologies, financial statements can be used to measure progress toward sustainable development. Nonmarket valuations are not generally accepted by the accounting profession. They are too subjective to support effective decisions, and too costly to obtain.Furthermore, demand for this sort of information appears small. Some of these issues may be resolved overtime. The most serious challenge, however, concerns how enhanced financial reports would be used. Financial statements are supposed to help investors assess the amount, timing, and uncertainty of future cash flows. A substantial portion of environmental value is based on nonuse benefits, much of which will never be realized in company cash flows. In other words, the role of financial statements would have to change. Furthermore, since there is no general agreement as to the meaning of “sustainable development,” efforts to operationalize the term have been fraught with difficulty. Moreover, monetization of environmental values could jeopardize their preservation, leaving some to question the overall objective of this form of reporting. For these reasons, while it is to be hoped that better reporting of environmental impacts will be forthcoming, the greatest advances will likely be outside the financial statements themselves.Key words: Environmental accounting; Social responsibility; Social responsibility reportingOne goal of accounting is to secure economic growth by luring investment dollars and labor resources away from low value uses toward higher value ones (Scott1997,Wildavsky1994). Accounting procedures were designed to track and report business activity with this as the overriding objective. There was no theoretical framework, however, providing guidance as to what information company managersshould disclose in financial statements. Initial attempts to develop external reporting theory focused on the needs of a very narrow segment of society: shareholders and creditors. There is a history, however, of company annual reports including nonfinancial disclosures on human resource management, community involvement, and environmental issues. This history gave rise to what is now called “social responsibility acc ounting.”Of all social responsibility issues appearing in financial statements over time, environmental information has been the most persistent. Accounting literature, both early and recent, stresses the need for information externalities (Mobley1970, Estes1972, Ramanathan76, CICA1997) or business impacts that are omitted from accounting records but borne by outside parties, as these may result in future monetary claims against a company. Accounting procedures rely on market-based transactions, however. Given the nonmarket nature of environmental values, the development of a generally accepted disclosure format has been fraught with difficulty. While accounting users draw their information from a variety of sources, not just the financial statements (Ball and Brown 1968), the annual report remains the most common medium for communication for the general users of accounting information (CICA1994), and for financial analysts in particular (Barron and others1999). So if the accounting profession is to maintain its usefulness in the business community, it must compete with these other sources to provide investment related information in a timely and cost-effective manner(Beaver1973,Rockness1985). On the part of the companies themselves, the persistence of environment-related information implies two significant changes in managers’views of the annual corporate report:(1)that they now address a much broader based group of accounting users and(2)that environmental matters warrant a regular place in these reports.This article begins with a review of methods used by economists to quantify environmental values and the impact of business activity upon those values. Company efforts to incorporate these values into the accounting framework for both internal and external decision-making purposes are then discussed. While existing accounting procedures can accommodate such values, these methods raise both theoretical and practical issues for the accounting profession. These issues, and the idea that tailoring financial statements to reflect environmental values could help in the pursuit of sustainable development, are discussed in the following pages.Economic Valuation MethodologiesOne way to assess the value of an environmental resource, such as a park, is the travel cost method (TCM). The TCM uses a regression model to relate the number of visits to a site with the costs associated with those trips. In its crudest form, the TCM measures only the direct costs associated with travel and makes several strict assumptions, the most contentious of which is that time itself has no value. In truth,TC models are sensitive to assumptions concerning time (Bishop and Heberlein 1979, Fletcher and others 1990). However, it is not clear that one way of integrating time into the models is superior to any other (Fletcher and others 1990). Furthermore, the divergence between perceptions of site availability, distance, and cost from actual measures affects the reliability of TC models. Perceptions play a significant role in decision-making (Fletcher and others1990). Economists, however, have tended to work with real measures (Fletcher and others 1990), thus introducing measurement error into the model.Clawson and Knetch (1966) said that once a TC model has been devised to estimate demand for a recreational experience, it is simple to adapt it to measure the value of the resource area itself. However, any problems or errors in the recreational experience model will transfer into the resource value model. Nevertheless the TC method has been used extensively to measure demand for national parks in the United States (Clawson and Knetch 1966). It has also been used to estimate the value of environmental amenities such as the Louisiana wetlands ( Costanza and Wainger 1991) and fishing opportunities in the Adirondacks( Mullen and Menz 1985). Assessments of the environmental impacts on human welfare, such as changes in health, aesthetics, or recreational opportunities, are complicated by the interrelationship of diverse disciplines. For example, an estimation ( in dollars ) of the impact of air pollution on humans depends upon three functional relationships(Freeman1993) involving a combination of scientific and behavioral analyses. These relationships are between:(1) the rate of discharge into the environment, and a change in environmental quality;(2) a change in environmental quality and a change in the flows of environmental services (such as the loss of a clear view or a change in health ); and(3) a change in environmental services and a change in utility.While the travel cost method, with its emphasis on use values, is not sufficiently sensitive to quantify all of these relationships, hedonic pricing (discussed below ), is designed to capture their net effect.The hedonic method estimates the implicit prices of characteristics which differentiate closely related products. For example, if the value of a piece of real estate can be viewed as the discounted stream of costs and benefits associated with its attributes, then a change in any of those attributes, such as local air quality, should be reflected in a change in price. Complications associated with this method pertain to the quality of the data (Freeman 1993). Imprecision in the parameter estimates arises from the inability to mix and match in dependent variables, such as house size and number of rooms (Freeman 1993). Furthermore, the stochastic nature of the measurements creates serious problems with this estimation procedure(Freeman1993).The hedonic approach assumes that individuals have complete information aboutthe asset being valued (Freeman 1993). For example, in the real estate market it is assumed that individuals have complete information about the houses available for sale. In reality, buyers /sellers of houses accept or reject offers as they are received. The seller sets an asking price without knowing if there are buyers who would have paid more, and a buyer makes an offer to purchase, not knowing if the seller would have accepted less. In other words it is incorrect to assume the transaction price reflects the minimum willingness to accept, or the maximum willingness to pay for any of the attributes of the house (Freeman1993).。

环境会计【外文翻译】

环境会计【外文翻译】

外文翻译外文出处Business & Economic Review,2006(4):21-27外文作者布莱恩.斯坦科,艾琳.布罗根,艾琳,亚历山大,约瑟芬.蔡.梅齐原文:Environmental AccountingHere's why projected cleanup costs from hazardous waste sites will be findingtheir way onto the balance sheets of Corporate America.Monitoring the production and disposal of hazardous waste has been a top priority of the United States government and the Environmental Protection Agency (EPA) since the mid-1970s, largely as a result of the Love Canal environmental disaster. Unfortunately, the remediation of hazardous waste sites is not finished, and cleanup cost estimates range anywhere between $500 billion and $1 trillion. American corporations will ultimately be held accountable for these costs. What remains to be seen, however, is exactly who, when, and how much.In terms of corporate responsibilities, this article discusses requirements regarding the financial reporting of environmental liabilities and current initiativesthat should improve the measurement and disclosure of these liabilities. Investors and business professionals alike must understand the significance of these obligations asthey relate to current and future corporate financial statements.Financial ReportingFinancial reporting requirements have evolved over time under several governing bodies. The Securities Act of 1934 created the Securities and Exchange Commission (SEC) and gave it the authority to administer federal securities laws and prescribe accounting principles and reporting practices. Companies that are considered under the jurisdiction of the SEC include any company whose stock is publicly traded. As a result, these companies are required to follow SEC disclosure requirements in their filings.The Financial Accounting Standards Board (FASB) is responsible for establishing the current standards of financial accounting and reporting. The standards or pronouncements that the FASB issues, "Statements of Financial Accounting Standards" (SFASs), are officially recognized as authoritative by the Securities and Exchange Commission and the American Institute of Certified Public Accountants (AICPA), the national professional organization of CPAs.Until recently, the AICPA played a prominent role in the accounting and reporting environment. But as a result of the Sarbanes-Oxley Act of 2002, the AlCPA's Auditing Standards Board (ASB) was limited in its role of establishing Generally Accepted Auditing Standards. Auditing and related professional practice standards as they pertain to public companies are now established by the Public Company Accounting Oversight Board (PCAOB), a private-sector, nonprofit corporation created to oversee the auditors of public companies in order to protect the interests of investors and further the public interest in the preparation of informative, fair, and independent audit reports.Evolution of Environmental Accounting StandardsThe common definition of "environmental accounting" is "the identification, measurement, and allocation of environmental costs, the integration of these environmental costs into business decisions, and the subsequent communication of the information to a company's stakeholders" (AICPA).Typical environmental costs include off-site waste disposal costs, cleanup costs, litigation costs, and other related costs.The first accounting standards or interpretation of standards that could be applied to environmental liabilities were enacted by the FASB in 1975 and 1976. These rules covered a generic grouping of contingent liabilities (including environmental liabilities). Initially the FASB stated that contingent liabilities arising from environmental cleanup costs should be accounted for and disclosed according to Statement of Financial Accounting Standards (SFAS) No. 5, "Accounting for Contingencies" (FASB 1975). One year later, the FASB issued Interpretation (FIN) No. 14, "Reasonable Estimation of the Amount of a Loss" (FASB 1976), offeringadditional guidance regarding loss contingencies. Essentially, the standard required losses to be accrued for when they became "probable and reasonably estimable." SFAS No. 5 is still followed today by accountants who are considering the measurement and disclosure of environmental liabilities.SuperfundPrior to Congress passing legislation granting the EPA authority to identify and sanction Potentially Responsible Parties (PRPs), most reported environmental liabilities were minimal. That changed in 1980 when Congress passed the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (CERCLA), commonly known as the Superfund Act. CERCLA established strict regulatory requirements regarding the release of hazardous substances from existing or future waste sites.Six years later, Congress amended CERCLA with the Superfund Amendment and Reauthorization Act (SARA).This strengthened the EPA’s authority and increased the agency’s fund balance. Under the new Superfund Act, the EPA became responsible for identifying and listing those locations throughout the United States where hazardous substances or waste either have caused or may cause damage to the environment. The EPA, through administrative or legal action, seeks to require PRPs to accept responsibility for the remediation of contaminated sites.Under CERCLA, a PRP is defined as any individual or company that is potentially responsible for, or contributed to, the contamination problems at a Superfund site. According to Paul D. Hutchinson, this can include:• Current owners or operato rs of facilities where hazardous substances have been deposited• Owners or operators of facilities at the time hazardous substances were deposited• Generators of hazardous substances deposited at facilities• Transporters of hazardous substances to facilities• Persons who arranged for disposal or treatment of hazardous substances at facilitiesOnce the EPA identifies a PRP, a liability-based program is used to address the cleanup of the site. Under the liability-based program, a potentially responsible party is classified into one of three categories:• Strict Liability - the PRP is liable for cleanup costs even when there was no negligence• Joint and Several Liability – any one party can be forced to bear the full cost of the remedy, even if several parties contributed to the waste at a site• Retroactive Liability - the provisions apply to actions that took place before CERCLA was passedAfter the EPA identifies the PRPs and their respective liability, it sends notification to the SEC and the respective companies or individuals.Regulation S-K and FRR 36With the increased environmental regulation, the accounting regulatory bodies began to issue standards regarding the reporting and disclosure of environmental liabilities. In 1982, the SEC integrated all of its environmental disclosure requirements into Regulation S-K, requiring disclosure if pollution expenditures had a material effect on the company's earnings. Regulation S-K Item 101, known as the Description of Business, requires registrants to disclose, among other things, the material effects of complying or failing to comply with environmental requirements on the capital expenditures, earnings, and competitive position of the registrant and its subsidiaries. S-K Item 103 requires registrants to describe any material concerning pending legal proceedings unless the legal proceedings involve ordinary routine litigation incidental to the business. S-K Item 303, often referred to as Management Discussion and Analysis of Financial Condition and Results of Operations, requires the disclosure of environmental contingencies that may reasonably have a material impact on net sales, revenue, or income from continuing operations.In 1989, the SEC provided further guidance by issuing Financial Reporting Release (FRR) 36. FRR 36 discusses and illustrates various disclosure requirements for the Management's Discussion and Analysis (MD&A) component of the SEC annual report 10-K filing and the shareholder annual report.Staff Accounting Bulletin (SAB) 92Even with this increase in regulation, companies were still finding it difficult to estimate liabilities that needed to be disclosed. In response, the SEC issued Staff Accounting Bulletin No.92 (SAB 92) to further clarify its disclosure requirements. SAB 92 specifically discussed the disclosure of environmental liabilities in the balance sheet. The SEC's position on the disclosure of environmental liabilities was strengthened through an agreement with the EPA in 1990. Essentially, the EPA would provide the SEC with certain quarterly information, including names of PRPs, a list of all cases filed under CERCLA, and a list of civil and criminal cases under federal environmental laws. In exchange for this information, the SEC agreed to target the enforcement of environmental disclosures.AICPA Statement of Position 96-1By 1996, the EPA had identified more than 36,000 hazardous waste sites in the United States. The EPA then took what they considered to be the most severe of the contaminated sites and developed the National Priorities List (NPL). This list contained 1,405 sites, each referred to as a Superfund site. From these Superfund sites alone, the EPA proceeded to identify 15,000 PRPs connected to these sites. These PRPs would eventually be responsible for cleanup costs that would range from $35 million to $1 billion per site. The release of this information revealed to the accounting profession that the remedial liabilities of the PRPs were significant and, therefore, required better accounting and disclosure. As a result, the AICPA issued Statement of Position (SOP) 96-1, "Environmental Remediation Liabilities," which provided specific guidance on estimation and the financial reporting of environmental accruals and contingencies.Analysis of the Standards (Past and Present)(A) Recognition of Environmental LiabilitiesRecognition pertains to when a liability should be reported in the financial statements. Contingent liabilities are obligations that are dependent upon the occurrence or nonoccurrence of one or more future events to confirm the amount payable, the payee, the date payable or its existence. The most significant liability thata firm faces in relation to environmental accounting comprises the remediation costs. Remediation costs typically include cleanup costs, litigation costs, and other costs associated with legal compliance.FAS No. 5,mentioned earlier,requires that a provision for a loss contingency be recorded and a liability recognized in financial statements when both of the following conditions are met:• It is probable that an asset has been impaired or a liability has been incurred at the date of the financial statements• The amount of the loss can be reasonably estimatedFASB Interpretation (FIN) No. 14 provides additional guidance on how to recognize a loss contingency when the estimated loss is within a specified range. It recommends that the minimum amount of the range be accrued, unless some amount within the range appears at the time to be a better estimate than any other amount within the range.The AICPA SOP 96-1 expands the types of costs that may be appropriately accrued and the ability to consider technologies under development in order to help assess the ultimate cost of remediation efforts more accurately. PRPs must now use a more conservative approach (increase the probability of loss recognition) than under the prior provisions of SFAS No. 5 to ascertain if they should accrue such liabilities. According to the SOP 96-1, the probability criterion of SFAS No. 5 is met if the EPA has decided (or probably will) that the company must participate in remediation. Liabilities must now be recognized when litigation has commenced or an assertion of a claim is probable whenever the PRP is associated with that site. In addition, PRPs must now accrue potential environmental remediation liabilities "up front," all at once, rather than recognize the expenses when they are actually paid.(B) Accounting for Recognized Environmental LiabilitiesWhen a company has determined that an environmental obligation exists, it must be measured and accounted for based on available information. Key accounting issues related to the recognition of environmental liabilities are highlighted below: Estimates of the Environmental LiabilityAccording to AlCPA's SOP 96-1, once a liability is determined, its magnitude must be estimated. In developing the estimates, according to Kathleen Blackburn Hethcox, Richard Riley, and Jan R. Williams writing in National Public Accountant, the factors below should be considered:• The extent and type of hazardous substances at the site, and the costs to be included in the estimate• The effect of expected future events or developments• The range of technologies that can be used in remediation• The number and financial condition of other PRPs• T he effect of potential recoveriesEarly estimates of loss can be revised later if new information gives cause for a change. The revisions should be accounted for as a change in accounting estimate, thereby only affecting current and future financial reporting. No retroactive restatement of prior year financial statements is allowed under SOP 96-1. The SOP 96-1 also recommends that for various stages of remediation, benchmarks be used to evaluate the extent of the amount that can be estimated. At a minimum, the estimate should be evaluated as each benchmark occurs; which includes identification of the company as a PRP, receipt of a unilateral administrative order requiring a removal action, participation in a remedial investigation (Rl) or feasibility study (FS) as a PRP, completion of a feasibility study, and issuance of a record of decision.Source: Brian B Stanko, Erin Brogan, Erin Alexander, and Josephine Choy-Mee Chay.Environmental Accounting[J]. Buinese & Economic Review, 2006,(4):21-27. 译文:环境会计本文讲述了,为什么从预算有害废物的清除成本可以看出美国公司编制资产负债表的方式。

第五组 环境会计

第五组 环境会计

优点:独立的环境会计报告采用第三方鉴证方式, 有助于保证环境信息的质量,使利益关系人获得 可靠的信息,从而进行相关决策。独立的环境会 计报告既能提供量化的财务信息,又能用文字补 充说明一些措施、政策和方法,使用者可以结合 财务主表全面了解企业的经济效益和社会效益, 对企业的环境工作和环境发展前景做出正确判断。
李姗姗 李叶梅 赵耿
宋方方
宋天乐
胡纯
独立的环境会计报告
独立的环境会计报告主要包括以下几部分: (1)企业简介,主要介绍企业概况。 (2)环境政策和环境目标,主要披露企业适用的环境政策 和环境目标以及执行环境政策和实现环境目标的情况。 (3)环境财务信息,主要用会计报表反映与企业环境保护 活动相关的财务信息以及企业未来的环境支出预算等。 (4)环境绩效,主要是对企业排放废物造成污染所形成的 社会成本增加以及消除污染所形成的环境改善等环境业 绩的评价。
企业环境会计信息的披露方式


(一)补充式环境会计报告 补充式环境会计报告是指在现行财务报告中增 加专门的会计科目、在报表附注中加以说明等方 式报告企业环境信息。 (二)独立的环境会计报告 独立的环境会计报告是指采用一定的方法和形 式单独编制的报告,可以采用表格、文字、图形 等多种方法,最终形成一系列的货币指标全面反 映企业承担的环境受托责任。
环境会计
环境会计的概念
环境会计(Environmental Accounting)又称绿色 会计(Green Accounting ),是以自然资源耗费 应如何补偿为中心而展开的会计,它试图将会 计学与环境经济学相结合,通过有效的价值管 理,达到协调经济发展和保护环境的目的。其 基本目标是实现经济效益、环境效益和社会效 益的多目标协调,实现可持续发展。

环境会计

环境会计

Background
Environmental accounting is set up on the basis of environmental resources deterioration and criticism of traditional accounting. In traditional accounting,there is a price and can be reflected in the accounting statement only if it has property ownership.But like the air, the oceans and the ozonosphere,they are essential to human while they Don’t have ownership,and they can’t involve in the accounting contents. That means these things’using and damaging by enterprises are not charged to operating costs.This not only inflates profits, even more serious is this would be an incentive for the behavior of sacrificing environment for current interest. 环境会计是在环境资源恶化和批评传统会计的基础上产生的。 环境会计是在环境资源恶化和批评传统会计的基础上产生的。 传统会计中,只有存在财产所有权才有价格,才能在会计账表中得以反映, 传统会计中,只有存在财产所有权才有价格,才能在会计账表中得以反映, 而如空气、海洋、 而如空气、海洋、臭氧层等对人类至关重要但无所有权的事物却不能成为会计 核算的内容,企业对这些事物的使用和损害并不记入经营成本, 核算的内容,企业对这些事物的使用和损害并不记入经营成本,这不仅使利润 虚增,更为严重的是对以牺牲环境来取得目前利益的行为的一种鼓励。 虚增,更为严重的是对以牺牲环境来取得目前利益的行为的一种鼓励。

外文原文:环境会计

外文原文:环境会计

Environmental AccountingWhere We Are Now, Where We Are HeadingBy Joy E. HechtInterest is growing in modifying national income accounting systems to promote understanding of the links between economy and environment.The field of environmental accounting has made great strides in the past two decades, moving from a rather arcane endeavor to one tested in dozens of countries and well established in a few. But the idea that nations might integrate the economic role of the environment into their income accounts is neither a quick sell nor a quick process; it has been under discussion since the 1960s. Despite controversies described in this article, however, interest is growing in modifying national income accounting systems to promote understanding of the links between economy and environment.Why Change?Governments around the world develop economic data systems known as national income accounts to calculate macroeconomic indicators such as gross domestic product. Building a nation's economic use of the environment into such accounts is a response to several perceived flaws in the System of National as defined by the United Nations and used internationally. One flaw in the SNA often cited is that the cost of environmental protection cannot be identified. Consequently, money spent, say, to put pollution control devices on smokestacks increases GDP, even though the expenditure is not economically productive, some argue. These critics call for differentiating “defensive” expenditures from others within the account s.Also misleading is the fact that some environmental goods are not marketed though they provide economic value. Fuelwood gathered in forests, meat and fish gathered for consumption, and medicinal plants are examples. So are drinking and irrigation water, whose sale prices reflect the cost of distribution and treatment infrastructure, but not the water itself. While some countries do include such goods in their national income accounts, no standard practices exist for doing so. When nonmarketed goods are included in the accounts, they still cannot be distinguished from those that are marketed.Valuing environmental services such as the watershed protection that forests afford and the crop fertilization that insects provide is difficult. Though some experts call for their inclusion in environmentally adjusted accounts, typically neither the economic value nor the degradation of these services is included. On the other hand, however, the alternate goods and services needed to replace them-water treatment plants, for example—do contribute to GDP, which can be rather misleading.Still another problem is that national income accounts treat the depreciation of manufacturedcapital and natural capital differently. Physical capital—a building or a machine, for instance—is depreciated in accordance with conventional business accounting principles, while all consumption of natural capital is accounted for as income. Thus the accounts of a country that harvests its forests unsustainably will show high income for a few years, but will not reflect the destruction of the productive forest asset. While opinions vary on how to depreciate natural capital, they converge on the need to do so.Which Indicators Are Useful?Some proponents advocate simple “flag” indicators to alert policymakers to the broad role of the environment in the economy, for example, comparing conventional GDP with environmentally adjusted GDP, or conventional savings with so-called “genuine” savings that account for environmental factors. Both of these indicators can provide valuable warnings of the impacts of environmental degradation on an economy. However, such flags are less useful in determining the source of environmental harm or identifying a policy response. For this reason, many economists place primary importance not on the bottom line, but on the underlying data used to build environmental accounts. These data can help answer such questions as how natural catastrophes like the fires that raged in Indonesia in the summer of 1998 may affect economic growth, or how environmental protection policies such as green taxes may affect the economy.Who Is Doing This?Environmental accounting is underway in several dozen countries, where bureaucrats, statisticians, and other proponents both foreign and domestic have initiated activities over the past few decades. Several countries have made continuous investments in data systems, which are integrated into existing statistical systems and economic planning activities. Others have made more limited efforts to calculate a few indicators, or analyze a single sector. Some of the earliest research on environmental accounting was done at RFF by Henry Peskin, working on the design of accounts for the United States.One of the first countries to build environmental accounts is Norway, which began collecting data on energy sources, fisheries, forests, and minerals in the 1970s to address resource scarcity. Over time, the Norwegians have expanded their accounts to include data on air pollutant emissions. Their accounts feed into a model of the national economy, which policymakers use to assess the energy implications of alternate growth strategies. Inclusion of these data also allows them to anticipate the impacts of different growth patterns on compliance with international conventions on pollutant emissions.More recently, a number of resource-dependent countries have become interested in measuring depreciation of their natural assets and adjusting their GDPs environmentally. One impetus for their interest was the 1989 s tudy “Wasting Assets: Natural Resources in the National Income Accounts,” in which Robert Repetto and his colleagues at the World Resources Institute estimated the depreciation of Indonesia’s forests, petroleum reserves, and soil assets. Onceadjusted to a ccount for that depreciation, Indonesia’s GDP and growth rates both sank significantly below conventional figures. While “Wasting Assets” called many to action, it also operated as a brake, leading many economists and statisticians to warn against a focus on green GDP, because it tells decisionmakers nothing about the causes or solutions for environmental problems.Since that time, several developing countries have made long-term commitments to broad-based environmental accounting. Namibia began work on resource accounts in 1994, addressing such questions as whether the government has been able to capture rents from the minerals and fisheries sectors, how to allocate scarce water supplies, and how rangeland degradation affects the value of livestock.The Philippines began work on environmental accounts in 1990. The approach used there is to build all economic inputs and outputs into the accounts, including nonmarketed goods and services of the environment. Thus Filipinos estimate monetary values for such items as gathered fuelwood and the waste disposal services provided by air, water, and land; they then add in direct consumption of such services as recreation and aesthetic appreciation of the natural world. While their methodology is controversial, these accounts have provided Philippine government agencies and researchers with a rich array of data for policymaking cymaking and analysis.The United States has not been a leader in the environmental accounting arena. At the start of the Clinton administration, the Bureau of Economic Analysis (BEA) made a foray into environmental accounting in the minerals sector, but this preliminary attempt became embroiled in political controversy and faced opposition from the minerals industry. Congress then asked the National Research Council (NRC) to form a blue ribbon panel to consider what the nation should do in the way of environmental accounting. Since then, Congressional appropriations to BEA have been accompanied by an explicit prohibition on environmental accounting work. The ban may be lifted, however, once the recommendations of the NRC study are made public.How to Account?How environmental accounting is being done varies in a number of respects, notably the magnitude of the investment required, the objectivity of the data, the ability to compare different kinds of environmental impacts, and the kinds of policy purposes to which they may be applied. Here are some of the methods currently in use.Natural Resource Accounts. These include data on stocks of natural resources and changes in them caused by either natural processes or human use. Such accounts typically cover agricultural land, fisheries, forests, minerals and petroleum, and water. In some countries tries, the accounts also include monetary data on the value of such resources. But attempts at valuation raise significant technical difficulties. It is fairly easy to track the value of resource flows when the goods are sold in markets, as in the case of timber and fish. Valuing changes in the stocks, however, is more difficult because they could be the result either of a physical change in the resource or of a fluctuation in market price.For environmental goods and services that are not sold, it is that much harder to establish the value either of the flow or of a change in stock. However, even physical data can be linked to the economy for policy purposes. For example, changes in income can sometimes be traced to changes in the resource base or to the impact of environmental catastrophes on the economy.Emissions accounting . Developed by the Dutch, the National Accounting Matrix including Environmental Accounts (NAMEA) structures the accounts in a matrix, which identifies pollutant emissions by economic sector, Eurostat, the statistical arm of the European Union, is helping EU members apply this approach as part of its environmental accounting program. The physical data in the NAMEA system are used to assess the impact of different growth strategies on environmental quality. Data can also be separated by type of pollutant emission to understand the impact on domestic, transborder, or global environments. If emissions are valued in monetary terms, these values can be used to determine the economic cost of avoiding environmental degradation in the first place, as well as to compare costs and benefits of environmental protection.Disaggregation of conventional national accounts.Sometimes data in the conventional accounts are taken apart to identify expenditures specifically related to the environment, such as those incurred to prevent or mitigate harm, to buy and install protection equipment, or to pay for charges and subsidies. Over time, revelation of these data makes it possible to observe links between changes in environmental policy and costs of environmental protection, as well as to track the evolution of the environmental protection industry.While these data are of obvious interest, some people argue that looking at them in isolation can be misleading. For example, while end-of-pipe pollution control equipment is easily observed, new factories and vehicles increasingly are lowering their pollutant emissions through product redesign or process change rather than relying on special equipment. In such cases, no pollution control expenditures would show up in the accounts, yet environmental performance might be better than in a case where expenditures do show up.Value of nonmarketed environmental goods and services. Considerable controversy exists over whether to include the imputed value of nonmarketed environmental goods and services in environmental accounts, such as the benefits of an unpolluted lake or a scenic vista. On the one hand, the value of these items is crucial if the accounts are to be used to assess tradeoffs between economic and environmental goals. Otherwise, the accounts can end up reflecting the costs of protecting the environment without in any way reflecting the benefits. On the other hand, some people feel that valuation is a modeling activity that goes beyond conventional accounting and should not be directly linked to the SNA .The concern underlying their view is that it is difficult to standardize valuation methods, so the resulting accounts may not be comparable across countries or economic sectors within a country.Green GDP.Developing a gross domestic product that includes the environment is also a matter of controversy. Most people actively involved in building environmental accountsminimize its importance .Because environmental accounting methods are not standardized, a green GDP can have a different meaning in each project that calculates it, so values are not comparable across countries. GDP Moreover, while a green GDP can draw attention to policy problems, it is not useful for figuring out how to resolve them. Nevertheless, most accounting projects that include monetary values do calculate this indicator .Great interest in it exists despite its limitations.Toward Consensus on MethodEnvironmental accounting would receive a substantial boost if an international consensus could be reached on methodology .The UN Statistics Department has coordinated some of the ongoing efforts toward this end since the 1980s. In 1993, the UN published the System for Integrated Economic and Environmental Accounting (SEEA) as an annex to the 1993 revision of the SNA.SEEA is structured as a series of methodological options, which include most of the different accounting activities described above; users choose the options most appropriate to their needs.No consensus exists on the various methods that the UN recommended. In fact, SEEA is now undergoing revision by the so-called “London Group,” co mprised primarily of national income accountants and statisticians from OECD countries. The group's work will be an important step toward consensus on accounting methods, but the process will be lengthy: Development of the conventional SNA took some forty yearsToward Widespread UseA number of steps can be taken now toward the goal of ensuring that environmental accounting is as well established as the SNA. First, information must circulate freely about existing environmental accounts and how they are contributing to economic and environmental policy. Ongoing work needs to be identified and systematically reviewed and analyzed to learn lessons, which may inform the design and implementation of future accounting activities. The Green Accounting Initiative of the World Conservation Union has embarked on this effort, and a number of other organizations are calling for similar activities. Use of the World Wide Web may facilitate access to unpublished work, although it will require a concerted effort to obtain accounting reports and seek permission to load them on the Internet.Second, development of a core of internationally standardized methods will contribute to willingness to adopt environmental accounting. Experts in the—field--including economists, environmentalists, academics, and others outside of the national statistical offices—should take a proactive role in tracking the work of the London Group and insist that the standard-setting process involve participants representing a spectrum of viewpoints, countries, and interested stakeholders. An opportunity exists for research institutes to take a lead in identifying the financial resources needed to facilitate a broader standard setting process, and to elicit a full range of voices to build a consensus on methodology.Finally, and perhaps most importantly, the more countries institutionalize construction of environmental accounts, the greater the momentum for more of the same.Still, building accounts--like developing any timeseries statistics—will not happen overnight. Their construction will require sustained institutional and financial commitment to ensure that the investment lasts long enough to yield results. But the experiences of Norway, Namibia, and the Philippines show that such a commitment can pay off; it is a commitment that more countries around the world need to make.Joy E. Hecht coordinates the Green Accounting Initiative at the International Union for the Conservation of Nature. /greenacct.html. While on the RFF staff in 1980–81, she began working on environmental accounting. This article is based on a talk she gave last fall as part of RFF's Wednesday Seminar Series.。

精编【财务会计管理】企业环境成本会计外文翻译

精编【财务会计管理】企业环境成本会计外文翻译

【财务会计管理】企业环境成本会计外文翻译xxxx年xx月xx日xxxxxxxx集团企业有限公司Please enter your company's name and contentvIMPLEMENTING ENVIRONMENTAL COSTACCOUNTING IN SMALL AND MEDIUM-SIZEDCOMPANIES1.ENVIRONMENTAL COST ACCOUNTING IN SMESSince its inception some 30 years ago, Environmental Cost Accounting (ECA) has reached a stage of development where individual ECA systems are separated from the core accounting system based an assessment of environmental costs with (see Fichter et al., 1997, Letmathe and Wagner , 2002).As environmental costs are commonly assessed as overhead costs, neither the older concepts of full costs accounting nor the relatively recent one of direct costing appear to represent an appropriate basis for the implementation of ECA. Similar to developments in conventional accounting, the theoretical and conceptual sphere of ECA has focused on process-based accounting since the 1990s (see Hallay and Pfriem, 1992, Fischer and Blasius, 1995, BMU/UBA, 1996, Heller et al., 1995, Letmathe, 1998, Spengler and H.hre, 1998).Taking available concepts of ECA into consideration, process-based concepts seem the best option regarding the establishment of ECA (see Heupel and Wendisch , 2002). These concepts, however, have to be continuously revised to ensure that they work well when applied in small and medium-sized companies.Based on the framework for Environmental Management Accounting presented in Burritt et al. (2002), our concept of ECA focuses on two maingroups of environmentally related impacts. These are environmentally induced financial effects and company-related effects on environmental systems (see Burritt and Schaltegger, 2000, p.58). Each of these impacts relate to specific categories of financial and environmental information. The environmentally induced financial effects are represented by monetary environmental information and the effects on environmental systems are represented by physical environmental information. Conventional accounting deals with both –monetary as well as physical units –but does not focus on environmental impact as such. T o arrive at a practical solution to the implementation of ECA in a company’s existing accounting system, and to comply with the problem of distinguishing between monetary and physical aspects, an integrated concept is required. As physical information is often the basis for the monetary information (e.g. kilograms of a raw material are the basis for the monetary valuation of raw material consumption), the integration of this information into the accounting system database is essential. From there, the generation of physical environmental and monetary (environmental) information would in many cases be feasible. For many companies, the priority would be monetary (environmental) information for use in for instance decisions regarding resource consumptions and investments. The use of ECA in small and medium-sized enterprises (SME) is still relatively rare, so practical examples available in the literature are few and far between. One problem is that the definitions of SMEs vary between countries (see Kosmider, 1993 and Reinemann,1999). In our work the criteria shown in Table 1 are used to describe small and medium-sized enterprises.Table 1. Criteria of small and medium-sized enterprisesNumber of employees TurnoverUp to 500 employees Turnover up to EUR 50mManagement Organization- Owner-cum-entrepreneur -Divisional organization is rare- Varies from a patriarchal management -Short flow of information stylein traditional companies and teamwork -Strong personal commitmentin start-up companies -Instruction and controlling with- Top-down planning in old companies direct personal contact- Delegation is rare- Low level of formality- High flexibilityFinance Personnel- family company -easy to survey number ofemployees- limited possibilities of financing -wide expertise-high satisfaction of employeesSupply chain Innovation-closely involved in local -high potential of innovationeconomic cycles in special fields- intense relationship with customersand suppliersKeeping these characteristics in mind, the chosen ECA approach should be easy to apply, should facilitate the handling of complex structures and at the same time be suited to the special needs of SMEs.Despite their size SMEs are increasingly implementing Enterprise Resource Planning (ERP) systems like SAP R/3, Oracle and Peoplesoft. ERP systems support business processes across organizational, temporal and geographical boundaries using one integrated database. The primary use of ERP systems is for planning and controlling production and administration processes of an enterprise. In SMEs however, they are often individually designed and thus not standardized making the integration of for instance software that supports ECA implementation problematic. Examples could be tools like the “eco-efficiency” approach of IMU (2003) or Umberto (2003) because these solutions work with the database of more comprehensive software solutions like SAP, Oracle, Navision or others. Umberto software for example (see Umberto, 2003) would require large investments and great backgroundknowledge of ECA – which is not available in most SMEs.The ECA approach suggested in this chapter is based on an integrative solution –meaning that an individually developed database is used, and the ECA solution adopted draws on the existing cost accounting procedures in the company. In contrast to other ECA approaches, the aim was to create an accounting system that enables the companies to individually obtain the relevant cost information. The aim of the research was thus to find out what cost information is relevant for the company’s decision on environmental issues and how to obtain it.2.METHOD FOR IMPLEMENTING ECASetting up an ECA system requires a systematic procedure. The project thus developed a method for implementing ECA in the companies that participated in the project; this is shown in Figure 1. During the implementation of the project it proved convenient to form a core team assigned with corresponding tasks drawing on employees in various departments. Such a team should consist of one or two persons from the production department as well as two from accounting and corporate environmental issues, if available. Depending on the stage of the project and kind of inquiry being considered, additional corporate members may be added to the project team to respond to issues such as IT, logistics, warehousing etc.Phase 1: Production Process VisualizationAt the beginning, the project team must be briefed thoroughly on thecurrent corporate situation and on the accounting situation. To this end, the existing corporate accounting structure and the related corporate information transfer should be analyzed thoroughly. Following the concept of an input/output analysis, how materials find their ways into and out of the company is assessed. The next step is to present the flow of material and goods discovered and assessed in a flow model. T o ensure the completeness and integrity of such a systematic analysis, any input and output is to be taken into consideration. Only a detailed analysis of material and energy flows from the point they enter the company until they leave it as products, waste, waste water or emissions enables the company to detect cost-saving potentials that at later stages of the project may involve more efficient material use, advanced process reliability and overview, improved capacity loads, reduced waste disposal costs, better transparency of costs and more reliable assessment of legal issues. As a first approach, simplified corporate flow models, standardized stand-alone models for supplier(s), warehouse and isolated production segments were established and only combined after completion. With such standard elements and prototypes defined, a company can readily develop an integrated flow model with production process(es), production lines or a production process as a whole. From the view of later adoption of the existing corporate accounting to ECA, such visualization helps detect, determine, assess and then separate primary from secondary processes.Phase 2: Modification of AccountingIn addition to the visualization of material and energy flows, modeling principal and peripheral corporate processes helps prevent problems involving too high shares of overhead costs on the net product result. The flow model allows processes to be determined directly or at least partially identified as cost drivers. This allows identifying and separating repetitive processing activity with comparably few options from those with more likely ones for potential improvement.By focusing on principal issues of corporate cost priorities and on those costs that have been assessed and assigned to their causes least appropriately so far, corporate procedures such as preparing bids, setting up production machinery, ordering (raw) material and related process parameters such as order positions, setting up cycles of machinery, and order items can be defined accurately. Putting several partial processes with their isolated costs into context allows principal processes to emerge; these form the basis of process-oriented accounting. Ultimately, the cost drivers of the processes assessed are the actual reference points for assigning and accounting overhead costs. The percentage surcharges on costs such as labor costs are replaced by process parameters measuring efficiency (see Foster and Gupta, 1990).Some corporate processes such as management, controlling and personnel remain inadequately assessed with cost drivers assigned to product-related cost accounting. Therefore, costs of the processes mentioned, irrelevant to the measure of production activity, have to be assessed and surcharged with aconventional percentage.At manufacturing companies participating in the project, computer-integrated manufacturing systems allow a more flexible and scope-oriented production (eco-monies of scope), whereas before only homogenous quantities (of products) could be produced under reasonable economic conditions (economies of scale). ECA inevitably prevents effects of allocation, complexity and digression and becomes a valuable controlling instrument where classical/conventional accounting arrangements systematically fail to facilitate proper decisions.Thus, individually adopted process-based accounting produces potentially valuable information for any kind of decision about internal processing or external sourcing (e.g. make-or-buy decisions).Phase 3: Harmonization of Corporate Data – Compiling and Acquisition On the way to a transparent and systematic information system, it is convenient to check core corporate information systems of procurement and logistics, production planning, and waste disposal with reference to their capability to provide the necessary precise figures for the determined material/energy flow model and for previously identified principal and peripheral processes. During the course of the project, a few modifications within existing information systems were, in most cases, sufficient to comply with these requirements; otherwise, a completely new software module would have had to be installed without prior analysis to satisfy the data requirements.Phase 4: Database conceptsWithin the concept of a transparent accounting system, process-based accounting can provide comprehensive and systematic information both on corporate material/ energy flows and so-called overhead costs. To deliver reliable figures over time, it is essential to integrate a permanent integration of the algorithms discussed above into the corporate information system(s). Such permanent integration and its practical use may be achieved by applying one of three software solutions (see Figure 2).For small companies with specific production processes, an integrated concept is best suited, i.e. conventional and environmental/process-oriented accounting merge together in one common system solution.For medium-sized companies, with already existing integrated production/ accounting platforms, an interface solution to such a system might be suitable. ECA, then, is set up as an independent software module outside the existing corporate ERP system and needs to be fed data continuously. By using identical conventions for inventory-data definitions within the ECA software, misinterpretation of data can be avoided.Phase 5: Training and CoachingFor the permanent use of ECA, continuous training of employees on all matters discussed remains essential. T o achieve a long-term potential of improved efficiency, the users of ECA applications and systems must be able to continuously detect and integrate corporate process modifications andchanges in order to integrate them into ECA and, later, to process them properly.中小企业环境成本会计的实施一、中小企业的环境成本会计自从成立三十年以来,环境成本会计已经发展到一定阶段,环境会计成本体系已经从以环境成本评估为基础的会计制度核心中分离出来(参考Fichter et al., 1997, Letmathe 和Wagner , 2002)。

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外文出处Business & Economic Review,2006(4):21-27外文作者布莱恩.斯坦科,艾琳.布罗根,艾琳,亚历山大,约瑟芬.蔡.梅齐原文:Environmental AccountingHere's why projected cleanup costs from hazardous waste sites will be findingtheir way onto the balance sheets of Corporate America.Monitoring the production and disposal of hazardous waste has been a top priority of the United States government and the Environmental Protection Agency (EPA) since the mid-1970s, largely as a result of the Love Canal environmental disaster. Unfortunately, the remediation of hazardous waste sites is not finished, and cleanup cost estimates range anywhere between $500 billion and $1 trillion. American corporations will ultimately be held accountable for these costs. What remains to be seen, however, is exactly who, when, and how much.In terms of corporate responsibilities, this article discusses requirements regarding the financial reporting of environmental liabilities and current initiativesthat should improve the measurement and disclosure of these liabilities. Investors and business professionals alike must understand the significance of these obligations asthey relate to current and future corporate financial statements.Financial ReportingFinancial reporting requirements have evolved over time under several governing bodies. The Securities Act of 1934 created the Securities and Exchange Commission (SEC) and gave it the authority to administer federal securities laws and prescribe accounting principles and reporting practices. Companies that are considered under the jurisdiction of the SEC include any company whose stock is publicly traded. As a result, these companies are required to follow SEC disclosure requirements in their filings.The Financial Accounting Standards Board (FASB) is responsible for establishing the current standards of financial accounting and reporting. The standardsor pronouncements that the FASB issues, "Statements of Financial Accounting Standards" (SFASs), are officially recognized as authoritative by the Securities and Exchange Commission and the American Institute of Certified Public Accountants (AICPA), the national professional organization of CPAs.Until recently, the AICPA played a prominent role in the accounting and reporting environment. But as a result of the Sarbanes-Oxley Act of 2002, the AlCPA's Auditing Standards Board (ASB) was limited in its role of establishing Generally Accepted Auditing Standards. Auditing and related professional practice standards as they pertain to public companies are now established by the Public Company Accounting Oversight Board (PCAOB), a private-sector, nonprofit corporation created to oversee the auditors of public companies in order to protect the interests of investors and further the public interest in the preparation of informative, fair, and independent audit reports.Evolution of Environmental Accounting StandardsThe common definition of "environmental accounting" is "the identification, measurement, and allocation of environmental costs, the integration of these environmental costs into business decisions, and the subsequent communication of the information to a company's stakeholders" (AICPA).Typical environmental costs include off-site waste disposal costs, cleanup costs, litigation costs, and other related costs.The first accounting standards or interpretation of standards that could be applied to environmental liabilities were enacted by the FASB in 1975 and 1976. These rules covered a generic grouping of contingent liabilities (including environmental liabilities). Initially the FASB stated that contingent liabilities arising from environmental cleanup costs should be accounted for and disclosed according to Statement of Financial Accounting Standards (SFAS) No. 5, "Accounting for Contingencies" (FASB 1975). One year later, the FASB issued Interpretation (FIN) No. 14, "Reasonable Estimation of the Amount of a Loss" (FASB 1976), offering additional guidance regarding loss contingencies. Essentially, the standard required losses to be accrued for when they became "probable and reasonably estimable."SFAS No. 5 is still followed today by accountants who are considering the measurement and disclosure of environmental liabilities.SuperfundPrior to Congress passing legislation granting the EPA authority to identify and sanction Potentially Responsible Parties (PRPs), most reported environmental liabilities were minimal. That changed in 1980 when Congress passed the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (CERCLA), commonly known as the Superfund Act. CERCLA established strict regulatory requirements regarding the release of hazardous substances from existing or future waste sites.Six years later, Congress amended CERCLA with the Superfund Amendment and Reauthorization Act (SARA).This strengthened the EPA’s authority and increased the agency’s fund balance. Under the new Superfund Act, the EPA became responsible for identifying and listing those locations throughout the United States where hazardous substances or waste either have caused or may cause damage to the environment. The EPA, through administrative or legal action, seeks to require PRPs to accept responsibility for the remediation of contaminated sites.Under CERCLA, a PRP is defined as any individual or company that is potentially responsible for, or contributed to, the contamination problems at a Superfund site. According to Paul D. Hutchinson, this can include:• Current owners or operators of facilities where hazardous substances have been deposited• Owners or operators of facilities at the time hazardous substances were deposited• Generators of hazardous substances deposited at facilities• Transporters of hazardous substances to facilities• Per sons who arranged for disposal or treatment of hazardous substances at facilitiesOnce the EPA identifies a PRP, a liability-based program is used to address the cleanup of the site. Under the liability-based program, a potentially responsible partyis classified into one of three categories:• Strict Liability - the PRP is liable for cleanup costs even when there was no negligence• Joint and Several Liability – any one party can be forced to bear the full cost of the remedy, even if several parties contributed to the waste at a site• Retroactive Liability - the provisions apply to actions that took place before CERCLA was passedAfter the EPA identifies the PRPs and their respective liability, it sends notification to the SEC and the respective companies or individuals.Regulation S-K and FRR 36With the increased environmental regulation, the accounting regulatory bodies began to issue standards regarding the reporting and disclosure of environmental liabilities. In 1982, the SEC integrated all of its environmental disclosure requirements into Regulation S-K, requiring disclosure if pollution expenditures had a material effect on the company's earnings. Regulation S-K Item 101, known as the Description of Business, requires registrants to disclose, among other things, the material effects of complying or failing to comply with environmental requirements on the capital expenditures, earnings, and competitive position of the registrant and its subsidiaries. S-K Item 103 requires registrants to describe any material concerning pending legal proceedings unless the legal proceedings involve ordinary routine litigation incidental to the business. S-K Item 303, often referred to as Management Discussion and Analysis of Financial Condition and Results of Operations, requires the disclosure of environmental contingencies that may reasonably have a material impact on net sales, revenue, or income from continuing operations.In 1989, the SEC provided further guidance by issuing Financial Reporting Release (FRR) 36. FRR 36 discusses and illustrates various disclosure requirements for the Management's Discussion and Analysis (MD&A) component of the SEC annual report 10-K filing and the shareholder annual report.Staff Accounting Bulletin (SAB) 92Even with this increase in regulation, companies were still finding it difficult toestimate liabilities that needed to be disclosed. In response, the SEC issued Staff Accounting Bulletin No.92 (SAB 92) to further clarify its disclosure requirements. SAB 92 specifically discussed the disclosure of environmental liabilities in the balance sheet. The SEC's position on the disclosure of environmental liabilities was strengthened through an agreement with the EPA in 1990. Essentially, the EPA would provide the SEC with certain quarterly information, including names of PRPs, a list of all cases filed under CERCLA, and a list of civil and criminal cases under federal environmental laws. In exchange for this information, the SEC agreed to target the enforcement of environmental disclosures.AICPA Statement of Position 96-1By 1996, the EPA had identified more than 36,000 hazardous waste sites in the United States. The EPA then took what they considered to be the most severe of the contaminated sites and developed the National Priorities List (NPL). This list contained 1,405 sites, each referred to as a Superfund site. From these Superfund sites alone, the EPA proceeded to identify 15,000 PRPs connected to these sites. These PRPs would eventually be responsible for cleanup costs that would range from $35 million to $1 billion per site. The release of this information revealed to the accounting profession that the remedial liabilities of the PRPs were significant and, therefore, required better accounting and disclosure. As a result, the AICPA issued Statement of Position (SOP) 96-1, "Environmental Remediation Liabilities," which provided specific guidance on estimation and the financial reporting of environmental accruals and contingencies.Analysis of the Standards (Past and Present)(A) Recognition of Environmental LiabilitiesRecognition pertains to when a liability should be reported in the financial statements. Contingent liabilities are obligations that are dependent upon the occurrence or nonoccurrence of one or more future events to confirm the amount payable, the payee, the date payable or its existence. The most significant liability that a firm faces in relation to environmental accounting comprises the remediation costs. Remediation costs typically include cleanup costs, litigation costs, and other costsassociated with legal compliance.FAS No. 5,mentioned earlier,requires that a provision for a loss contingency be recorded and a liability recognized in financial statements when both of the following conditions are met:• It is probable that an asset has been impaired or a liability has been incurred at the date of the financial statements• The amount of the loss can be reasonably estimatedFASB Interpretation (FIN) No. 14 provides additional guidance on how to recognize a loss contingency when the estimated loss is within a specified range. It recommends that the minimum amount of the range be accrued, unless some amount within the range appears at the time to be a better estimate than any other amount within the range.The AICPA SOP 96-1 expands the types of costs that may be appropriately accrued and the ability to consider technologies under development in order to help assess the ultimate cost of remediation efforts more accurately. PRPs must now use a more conservative approach (increase the probability of loss recognition) than under the prior provisions of SFAS No. 5 to ascertain if they should accrue such liabilities. According to the SOP 96-1, the probability criterion of SFAS No. 5 is met if the EPA has decided (or probably will) that the company must participate in remediation. Liabilities must now be recognized when litigation has commenced or an assertion of a claim is probable whenever the PRP is associated with that site. In addition, PRPs must now accrue potential environmental remediation liabilities "up front," all at once, rather than recognize the expenses when they are actually paid.(B) Accounting for Recognized Environmental LiabilitiesWhen a company has determined that an environmental obligation exists, it must be measured and accounted for based on available information. Key accounting issues related to the recognition of environmental liabilities are highlighted below: Estimates of the Environmental LiabilityAccording to AlCPA's SOP 96-1, once a liability is determined, its magnitude must be estimated. In developing the estimates, according to Kathleen BlackburnHethcox, Richard Riley, and Jan R. Williams writing in National Public Accountant, the factors below should be considered:• The extent and type of haz ardous substances at the site, and the costs to be included in the estimate• The effect of expected future events or developments• The range of technologies that can be used in remediation• The number and financial condition of other PRPs• The effect o f potential recoveriesEarly estimates of loss can be revised later if new information gives cause for a change. The revisions should be accounted for as a change in accounting estimate, thereby only affecting current and future financial reporting. No retroactive restatement of prior year financial statements is allowed under SOP 96-1. The SOP 96-1 also recommends that for various stages of remediation, benchmarks be used to evaluate the extent of the amount that can be estimated. At a minimum, the estimate should be evaluated as each benchmark occurs; which includes identification of the company as a PRP, receipt of a unilateral administrative order requiring a removal action, participation in a remedial investigation (Rl) or feasibility study (FS) as a PRP, completion of a feasibility study, and issuance of a record of decision.Source: Brian B Stanko, Erin Brogan, Erin Alexander, and Josephine Choy-Mee Chay.Environmental Accounting[J]. Buinese & Economic Review, 2006,(4):21-27.。

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