环境会计外文文献及其翻译

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企业环境成本会计外文翻译word精品文档11页

企业环境成本会计外文翻译word精品文档11页

IMPLEMENTING 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 main groups 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. Conventionalaccounting 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 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 50m Management 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 flexibility Finance Personnel- family company -easy to survey number ofemployees- limited possibilities of financing -wide expertise-high satisfaction of employees Supply chain Innovation-closely involved in local -high potential ofinnovationeconomic 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 background knowledge 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 o n 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 the current 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. To 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 theyleave 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 surchargeson 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 a conventional 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-basedaccounting 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. To 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 and changes 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)。

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。

绿色会计理论与可持续发展外文文献翻译

绿色会计理论与可持续发展外文文献翻译

毕业设计附件外文文献翻译:原文+译文文献出处: Markus S. Green accounting theory and sustainable development [J]. Accounting, Auditing & Accountability Journal, 2016, 2(1): 29-46.原文Green accounting theory and sustainable developmentMarkus SAbstractGreen accounting, also known as environmental accounting, combining accounting and natural environment, the diversity of measurement methods and properties, on the basis of relevant environmental laws and regulations, and examined the relationship between economic development and environmental resources, and using the method of special, cause social resources and environment of the enterprise profit and loss revealed, recognition, measurement and analysis, in order to provide the environmental information of accounting theory and methods. The basic theories of green accounting are in the correction and criticism of the traditional accounting theory on the basis of the emergence and development. For a long time, the traditional accounting theory from the Angle of human economic activities, only reflect and supervision enterprise capital and its movement, according to the accrual basis, the historical cost and double-entry these three basic pillar of the economic accounting matters for accounting recognition, measurement, recording and reporting, caused by the environment of economic problems in this is not the answer. Green accounting for all the human activities and the whole ecological environment resources as the starting point, around how to compensate the cost of natural resources, efforts to fulfill the duties of the environmental management in all levels make the recognition, measurement and reporting, fundamentally changed the traditional accounting theory for the definition of accounting elements. Keywords: sustainable development; Green accounting; the basic theory1 IntroductionHuman industrial activities along with the rapid development of economic growth, people's living standard had the very significantly improved. But at the same time, the human scale of thedestruction of the earth's resources is also unprecedented. Due to the excessive open the calculation of environmental resources, ecological environment suffered serious damage, has appeared to make ends meet. Can say, is to rely on human to overdraw the future development. And, the environment problem has become a global problem, breakthrough the limitation of the country and region. The protection of environment, governance, the effective use of resources has become a global consensus. The emerging topic of green accounting is on the premise of this. Green accounting object of study is the content of environmental accounting in the accounting and supervision, is the enterprise production activities and environmental resources between consumption and supply process. Traditional accounting object itself contains only the enterprise production activities, capital contains only into three parts, operation and exit enterprises. Green accounting on the basis of the traditional accounting, increase the content of the environmental resources, the consumption and compensation of the natural environment of the enterprise up objectively reflect the role of, make its production activities impact on the environment are subject to supervision by the society and the country, so as to realize the virtuous circle of natural resource consumption and complement, make environment don't have to pay for economic growth, ultimately achieve sustainable development.2 Literature reviewIn the 1980 s, the western developed countries first proposed the term "sustainable development".1992, held in environment and development conference in governments and international institutions generally achieved consensus, recognized and accepted this view. These cases show that the theory has validity, universality, and urgent need. Sustainable development in macroscopic Angle of human survival and development, the protection of the environment and resources, and the logic of the dialectical relationship between economic activities, is the research content of macroeconomics in the aspect of environmental problems. Its role is to the coordinated development of the economic growth and environmental policies are discussed. The theory is the overall goal of the green accounting system and the basis, is a green accounting system began to expand and build theoretical basis. The starting point of green accounting, as well as the ultimate goal is to promote the sustainable development of economy and environment; this determines the starting point of the green accounting research and belonging. Sustainable development theory is the most important theoretical basis for green accounting; green accounting is one of the importantmeasures to promote the sustainable development, both in full accord. The implementation of sustainable development, the realization of the essence of which is environmental management; And environmental management responsibility, is held by government agencies. The implementation of environmental management responsibility, to identify by the independent audit department. Thus, as a social control mechanism of the green accounting is a top-down bear the responsibility of environmental protection and management, is also an important way of implementing sustainable development strategy.The connotation of sustainable development has two aspects: development and continuous. Development is the fundamental premise and foundation, only development, only necessary to discuss sustainability. Persistence is the key, there is no continuity, and it could have been. Development includes the following two aspects: first, the development is the accumulation of human material civilization, it directly reflects on the economic growth. Second, development is a national economic and social system construction of course, the ultimate goal is to increase the interests of all, is looking for social progress. Continuous meaning also contains two aspects: the first is that environmental resources storage and carrying capacity is limited. Because of the limitation, conflicts with the necessity of economically, have become the restriction conditions of economic development. Second, shouldn't overdraw the future economic development, considering their own interests at the same time, also for future generations to develop interests do consider. Sustainable development includes the resources and environment and the sustainable development of ecological planning, the sustainable development of the economic activities of production and social cultural sustainable development of three parts, is a long-term development strategy. You need to first on the basis of the sustainable use of resources and ecological environment, achieve economic production activities under the premise of sustainable development. Finally, the sustainable development center problem is, the ultimate goal is to seek the overall progress of society. Sustainable development strategy to achieve the ecological balance, the unification of the economic production and social development benefits, the extensive economic growth mode to intensive changes, keep the economic development and environment in harmony. Is beneficial to improve the level of people's whole life, promote the new industrialization, the adjustment of agricultural structure and the protection of the ecological environment, finally realizes the fast, stable, sustainable and healthy development of nationaleconomy.3 The basic theory of green accountingGreen accounting is the environment, environmental economics and development economics, the product of the combination of accounting. Green accounting theory problem should be to look at environmental issues stand in the perspective of accounting, with the thought of the accounting system and method system to think and analyze, in order to solve the contradiction between economic development and maintaining ecological environment. As a branch of modern accounting, green accounting should establish a goal, the basic theory of structural system composed of assumptions and principles.3.1 Green accounting targetAs the goal of green accounting behavior guidelines can be divided into two levels. One is the basic goal. Use accounting to measuring, reflect and control the social environment resources, improving social environment and resource problems, achieve economic benefit, ecological benefit and social benefit of synchronous optimization. Based on the requirements of environmental macro management, the enterprise in the production and business operation and obtain economic benefits at the same time, must attach great importance to the ecological environment and material circulation rule, reasonable development and utilization of natural resources, insist on sustainable development strategy, try to improve the environmental benefit and social benefit. Second, the specific objectives. For the corresponding accounting, the value of natural resources, the cost of natural resources, environmental protection, improve resource environment recognition and measurement, the benefits of environmental protection for the government departments and the competent department of industry, investors and social public enterprise environmental objectives, environmental policy and planning and other relevant information. Provide related object with the ultimate goal of environmental accounting information is control and coordinate the relationship between economic benefit and environmental resources, realize the environmental benefits, social benefits and economic benefits of synchronous optimization, to achieve economic development, social progress and environmental protection harmonious and unified.3.2 The basic hypothesis of green accountingThe sustainable development of assumptions. Hypothesis refers to the sustainabledevelopment of green accounting to accounting subject in natural resource depletion, ecological resources do not drop, on the basis of guarantee the social and economic sustainable development. Sustainable development contains a large amount for the contents of the ecological environment; the request must be coordinated development of economy and environment. Although the green accounting in the accounting entity's economic activities, there is a lot of uncertainty but accounting and supervision procedures and methods should be based on the sustainable development. Sustainable development is to establish the basic premise of green accounting, is the basis of constructing green accounting theory and method system conditions.Environmental value assumptions. In Marx's labor theory of value, only for the exchange of labor value. Only use environmental resources value, there is no exchange of value and price, do not belong to the scope of the traditional accounting, but must carry on the green accounting must first admit that environmental resources are valuable, although it does not apply to the labor theory of value, is applicable to the marginal value theory. Multiple measurement assumptions. Because of the complexity of the environmental factors and vagueness of the green benefit, if the only unit of measurement for money, will not be able to objectively reflect the environmental condition of the accounting entity and green benefit, therefore green accounting on the measurement should be multiple. Should be given priority by money value, supplemented by physical, percentage, or index, etc., sometimes even can use the graph and text notes, and should adopt combination of quantitative and qualitative, accuracy and fuzziness of compatible measurement method.4 The basic principles of green accounting4.1 Social principlesSocial principle refers to the green accounting requires enterprises must stand in the perspective of society, to stand in the Angle of the responsible for the environment and resources, consider the interests of the enterprise. For the evaluation of enterprises have to abandon a purely on the basis of enterprise operating profit idea, to enterprise profit created by green. At the same time, the enterprise to provide accounting information must also be conducive to the management and the macro control of the country.4.2 Principle of both economic and environmental benefitsGreen accounting should not only consider the economic interests of the enterprise itself, and should take the social ecological and environmental benefits, to comprehensively reflect andcontrol the enterprise's economic efficiency, resources and environment, waste and the ecological environment, the accounting main body in ecological environment, the whole social production, consumption and the corresponding ecological cycle are reflected in the accounting mode, the comprehensive measurement and reveal the enterprise production activities to the consequences of the ecological environment to the society, in order to standardize enterprise behavior, realize the sustainable development of economy.4.3 Principle of mandatory disclosure and voluntary disclosureIn green accounting system, the relevant government department or organization to deal with enterprise minimum levels of environmental resources, the mandatory provisions of the disclosure of information to make clear, at the same time, encourage enterprises to consciously to the public and the government related department or group provides environmental resources information as much as possible.译文绿色会计理论与可持续发展Markus S摘要绿色会计,又称环境会计,是将会计学和自然环境相结合,采用多元化的计量手段和属性,以有关环境法律、法规为依据,研究经济发展与环境资源之间关系,并运用专门的方法,对企业给社会资源环境造成的收益和损失进行确认、计量、揭示、分析,以便为决策者提供环境信息的会计理论和方法。

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。

环境会计之废物管理:澳大利亚地方政府的一项研究【外文翻译】

环境会计之废物管理:澳大利亚地方政府的一项研究【外文翻译】

本科毕业论文(设计)外文出处外文作者原文:IntroductionAlong withwaste is collectedEvidenceecosystem anddevelopment. Thisrecovery.needs of localdomestic andresponsibility ofcommercial andamount of environmental protection expenditure (e.g. local government expenditure on waste management has rose to 58 per cent of total environmental expenditure during 2000–01) (ABS, 2000–2001).Due to the increasing waste generation, increasing land prices and more stringent environmental regulation, waste management is becoming more expensive and more environmentally sensitive. Traditional management and accounting approaches have been criticized because they are incomplete in scope and overlook environmental benefit and cost information (US EPA, 1998). Changes from conventional accounting concepts and approaches to contemporary environmental accounting approaches emerged in the 1990s (see Senge, 1993; Epstein, 1996). Words such as ‘full’, ‘total’, ‘true’ and‘life cycle’ are often used in environmental accounting practices to emphasize the importance of a broader environmental information scope in management decision making. A number of studies have researched the development of full cost accounting and life cycle assessment for waste management in the US (e.g. US EPA, 1997; Weitzet al., 1999). However, the method these studies have used is limited to case studies.In Australia, while the significance of environmental accounting issues in local waste management has been noted, this new field is less studied. According to the principle of waste minimization made by the 1992 Australian National Strategy for Ecological Sustainable Development, whole life cycle methodologies should be developed to evaluate the full cost of landfill and waste disposal facilities. In 1998, Eco Land use Systems (ELS) (1998) conducted a survey about waste disposal charges in Australian major cities. They investigated current and prospective costs of landfill disposal, levels of charges and levies imposed by local authorities, and policies behind the establishment of the charges. It was found that waste disposal fees and charges had significantly increased in all Australian major cities since the 1990s. One third of the cities were planning for further changes of landfill charges to cover fuller costs. However, environmental information collection and reporting is still a challenge today. As noted by the Environment Australia (2001), data on waste generation in Australia is patchy, and waste data has been collected only relatively recently in somestates and territories. The relatively inexact nature of waste accounting and significant data gaps can make regional comparison difficult.This study aims to understand the extent to which Australian local governments have accounted for environmental costs and impacts of waste streams in response to the current environmental agenda. The purpose of this study is to contribute to our knowledge of environmental accounting for waste management regarding Australian practice and the results of the study will be of use for government regulators and environmental researchers to discover opportunities for and barriers to environmental accounting in local governments and to develop policies to encourage the development of environmental accounting approaches for local governments.Environmental accountingEnvironmental accounting has been defined in a variety of ways and contexts. This study uses Senge’s (1993) study as the basis for analysis because most recently developed definitions for environmental accounting are essentially similar to the environmental accounting challenges in Senge’s arguments. Senge proposed several main challenges environmental accounting presented. These include (1) capturing not only financial, but also non-financial information relating to environmental issues; (2) estimating potential future costs rather than adopting a historical cost orientation, and (3) recognizing transactions with the environment that currently lie outside the scope of conventional accounting concepts. The challenges highlight the following three essential features of environmental accounting.(i) Accounting for direct monetary and physical flow information.Environmental accounting has a multi-dimensional construct rather than a uni-dimensional form. It first sheds light on the responsibility of the organisation to capture both economic and ecological footprints and looks upon the entire operation of the organisation as an ecological activity with both economic and ecological impacts (UNDSD, 2001). As the United Nations Division for Sustainable Development (UNDSD) (2001) states, environmental accounting procedures for management decision-making include both physical procedures for material and energy consumption, flows and final disposal, and monetarised procedures for costs,savings and revenues related to activities with a potential environmental impact. Schaltegger and Burritt (2000) underscore that identifying significant and relevant environmental information in both dimensions can help organisations visualise and understand the total monetary and physical flow changes involved in their environmental management activities.(ii)Accounting for environmental information hidden in overheads and future periods.The second difference between conventional accounting and environmental accounting is that environmental accounting information extends beyond the scope of conventional costs to include potentially hidden, future and contingent costs. Hidden environmental costs are indirectly related to the operation of a process, system or facility, such as costs involved in administrative support, legal services and fines, auditing and so forth. Indirect environmental costs also involve those hidden costs in future periods. Accounting for future costs may require expenditure now in order to avoid much larger financial and environmental costs in the future. In the US EPA’s (1998) interpretation, future costs are generally contingent and intangible environmental liabilities that may influence the effective operations of the organization in the long run. But some prospective environmental costs may occur at more or less well-defined points in the future, such as future costs of closing landfills or complying with regulations that are not in effect but have been promulgated. Some future costs may or may not be incurred at some point in the future, such as uncertain future remediation or compensation costs, and risk posed by future regulatory changes. Accounting for these costs and impacts will encourage the identification of obligations resulting from current operations which will probably have to be paid in the future (Senge, 1993).(iii)Accounting for environmental externalities.External environmental costs are often referred to as ‘externalities’ that arise outside of the assumed, legitimate and ‘usual’ boundary of an organisation (Bebbington et al., 2001). While environmental impacts beyond the boundaries of an organisation may go unpriced or uncompensated, they do have an effect on the naturalenvironment and other parts of society. Examples of externalities include human health effects associated with air pollution, the depletion of natural resources, residual air and water emissions damaging the ecological system. Externalities are generally intangible and more difficult to directly measure in monetary terms than internal costs (direct or hidden), though external environmental costs can be the larger of the two cost components (IFAC, 1998). However, a ‘bargained’ equilibrium can be reached if the externalities are internalised. Gale and Stokoe (2001) postulate that it might be more pragmatic for organizations to take account of external costs as impending internal costs because each category of externalities will eventually be reflected in internal costs. Hence, externalities may be presented as costs to restore environmental impacts or costs borne to not cause the externalities.Environmental accounting for waste managementBased on the basic concepts and features of environmental accounting discussed above, environmental accounting for waste management has been explored in previous studies from three different perspectives corresponding to the three features of environmental accounting.(i) Accounting for monetary and physical flows in waste streams and activities.Local governments have a number of options to manage waste streams, from landfill disposal to material recovery and reduction. The US EPA’s study (1997) illustrates these options and activities associated with them. First, waste streams cover a number of physical flow paths reflected as the options local authorities choose to deliver their waste services. These paths include the landfill disposal path, the waste to energy path, the recycling path and the composting path. Second, each waste flow path covers a number of activities including collection of waste and recyclables, operation of transfer stations, waste processing and/or disposal at waste management facilities, and sale of by-products. The US EPA notes that basic activities through waste flows constitute a complicated process and considerable inventory data that local authorities cannot oversimplify. Understanding the costs of each waste activity and flow path is necessary for compiling costs of the entire system and helps to estimate the potential costs of changing service options from one to another.(ii) Accounting for hidden environmental costs of waste streams.The second issue is accounting for environmental information embedded in waste streams, which is specifically addressed in the US EPA’s (1997) full cost accounting project. Apart from direct activity related costs, waste streams involve a variety of indirect costs, such as costs for administration, waste education, reporting and auditing. These administrative expenditures for waste planning and management can be substantial. The US EPA implies that continuing or regular outlays of local community education and promotion activities can be essential management costs that account for most financial resources, but they are hardly ever separately recognised in administrative overheads. Moreover, costs incurred in one waste stream may lead to the benefits of another waste stream.In most cases, when waste reduction/recycling is regarded as an economically viable option, it is the avoided waste disposal costs that tip the economics (Laughlin and Varangu, 1991).With the increasing cost of garbage treatment/disposal, such avoided garbage disposal costs are now making recycling cheaper. Future costs and impacts are even harder for local governments to identify. First, at the end of the working life of a landfill, landfill occupiers bear a responsibility for sealing it and undertaking post-closure rehabilitation, monitoring and care (EPA NSW, 1996). Second, the US EPA’s study emphasises that potentially hidden long-term environmental information may also involve site replacement costs, the costs of environment legislation change and anticipated remediation costs. In Australia, such long-term costs are estimated to be $10 to $22 per tonne on top of operating costs for a well-engineered landfill (ACT Government, 2001). If these hidden costs are not fully recorded, it is difficult for local councils to assign sufficient resources to prevent or reduce them.(iii) Accounting for external environmental impacts of waste streams.External environmental outputs from waste streams were previously borne by the natural environment, but now are coming to attention. Landfill disposal, in particular, generates most adverse environmental impacts. Gandy (1994) points out that landfills have potential damage to human health through groundwatercontamination years after burial, contamination of surface water supply, leakage of toxic and hazardous air/water-borne pollution and acid deposition. Broader concerns now relate to emissions of greenhouse gases from waste disposal processes and the value of resources buried in landfills as well (EPA NSW, 1996; ACT Government, 2001). In environmental terms, recycling may be regarded as an environmentally benign option because of its environmental benefits of reducing pollution and decreasing general waste volume and the need for landfill space. Nevertheless, recycling also involves potential adverse environmental impacts from the location and operation of recycling facilities to the transportation of recovered materials. A number of studies challenge that communities should recycle only when it pays for itself through recyclable sales revenue and disposal cost saving (Alexander, 1993; Boerner and Chilton, 1994). Other studies claim that the substantial environmental advantages from waste recycling and composting go far beyond its adverse influence to the environment (Gandy, 1994; Craighill and Powell, 1996). It can be inferred that decisions may be different if different levels and scopes of environmental costs are identified and used.Source: Wei Qian, Roger Burritt. Environmental accounting for management: A study of local governments in Australia[J].Environmentalist,2007,(27):143-154.译文:环境会计之废物管理:澳大利亚地方政府的一项研究简介近年来随着澳大利亚城市人口的增长,废物的产生量也在迅速增长。

环境会计信息披露外文文献翻译中英文.pdf

环境会计信息披露外文文献翻译中英文.pdf

外文文献翻译原文及译文(本文档归max118 网hh2018 所有,仅供下载使用)中文标题:印度环境会计披露实践的影响因素:来自NIFTY 公司的经验证据文献出处:The IUP Journal of Accounting Research & Audit Practices, Vol. 15, No. 1, 2016译文字数:3900 多字原文Factors Influencing Environmental Accounting and Disclosure Practices in India: Empirical Evidence from NIFTY CompaniesB Omnamasivaya* and M S V PrasadThe study examines the factors determining the level of environmental disclosure information by taking a sample of NIFTY 50 companies from National Stock Exchange (NSE). The environmental information disclosure is measured by using an Environmental Accounting Disclosure Index (EADI) and the variables used in the study are profitability, corporate size, age, financial leverage, industry type, legal ownership and foreign operations. The relationship is tested using multiple regression analysis. The results show that there is a positive relationship between EADI and profitability, financial leverage, industry type and legal ownership, and a negative relationship between EADI and corporate size, age and foreign operations.IntroductionClimate change is one of the greatest challenges that the world is facing today. Climate change is the variation in the global climate over time. The climate change creates manifold problems like global warming, glacier meltdown, soil erosion, land degradation, deforestation, loss of biodiversity and all kinds of pollution. Human influence on the nature is one of the major causes of such problems. Indiscriminate use of resourcesand undue influence on nature in the name of development can be identified as the prime causes of climate change. As a result, in the last few decades, the adverse effect of environmental pollution on economic development has become a public concern all over the world (Goswami, 2014).The state of world‘s environment and the impact of mankind on the ecology of the world have led to increased public concern and scrutiny of the operations and performance of organizations. Globally, corporations are expected to include environmental concerns in business operations and interaction with stakeholders. As a result, firms can no longer ignore the problems of the society in which they operate. This has thus instituted a social contract between organizations and the environment, thereby making environmental responsibility a corporate dictate (Olayinka and Oluwamayowa, 2014).Every business has responsibility to use the resources at judiciously. Every enterprise needs to behave like a good corporate citizen, and the corporate behavior is judged by its actions related to the community, the steps taken to protect the environment or pollution control. In the context of the Indian corporate sector, companies are not performing as good citizens. Due to this reason many laws have been laid down by the government for making the companies good corporate citizens and fulfill their social responsibility (Chauhan, 2005).In India, the economic reforms initiated in the 1990s have unwittingly contributed to a rise in environmental problems. The awareness level of stakeholders and public regarding the environmental issues has increased the pressure on companies to disclose environmental information. As a result, the companies have started disclosing the environmental information in annual reports and sustainability reports to satisfy all their stakeholders.The Indian government has taken several steps to protect the environment. It has set up the Ministry of Environment, Forest and Climate Change (MoEFCC) with the aim to coordinate, among the states and the various ministries, the issues relating to environmental protection and antipollution measures. Necessary legislation has also been passed. In India, Central Pollution Control Board (CPCB) and State Pollution Control Board (SPCB) were established under the Water Act. The CPCB has identified 17 categories of industries which are highly polluting (Joshi et al., 2011).In India, specific environmental accounting rules or environmental disclosure guidelines for communication to different stakeholder groups are not available for Indian companies. There is no mandatory requirement for quantitative disclosure of (financial) environmental information in annual reports either under the Companies Act or as per the Indian Accounting Standards. Furthermore there are 23 stockexchanges in India which are controlled by the Securities Exchange Board of India (SEBI) Act, 1992. Each of these stock exchanges has different listing requirement for Indian companies to disclose environmental information. Therefore, any environmental disclosure by Indian companies is purely voluntary (Makori and Jagongo, 2013). Against this backdrop, the present study examines the factors determining the level of environmental disclosure information in India.Legitimacy TheoryIn order to explain the reasons for environmental disclosure, we use legitimacy theory. There are many theories which explain the various reasons for social and environmental accounting disclosures, but legitimacy theory is the most suitable theory to explain the environmental disclosure. Organizations cannot survive without meeting the societal expectations. The society expects that the organizations should be proactive in protecting the environment and minimizing the environmental hazards. In case organizations fail to meet the societal expectations, there is a severe threat to their existence. Nowadays Indian companies are legitimizing because of the awareness about environmental disclosure practices in the society. Therefore, Indian companies are taking several steps to protect the environment and are disclosing the relevant environmental information in their annual reports and company websites.Legitimacy relates to the environmental issues which are disclosedin the companies’ annual reports. This indicates the management concerns towards the community. Therefore, the management of different companies or managers have different ideas or thoughts about what the society expects and managers will adapt different strategies to show the society that the organization is meeting the expectations of the community (Zain, 2006).The theory of legitimacy is based on two fundamental ideas: companies need to legitimize their activities, and the process of legitimacy that confers benefits to businesses. Thus, the first element is compatible with the idea that environmental disclosure is related to the social pressure. In this context, the need for legitimacy is not the same for all companies due to the degree of social pressure the company is exposed to, and the level of response to this pressure. There are a number of factors which determine the degree of social pressure on companies and their responses to the pressure. These factors are potential determinants of corporate social disclosure. The second component is based on the idea that companies can expect to benefit by a legitimate behavior based on the social responsibility activity. In addition to that, the legitimacy theory provides a comprehensive framework to explain both the determinants and consequences of social disclosure (Mohamed et al., 2014).Literature ReviewKokubu et al. (2001) examined the annual reports of 1,203 companies to investigate the determinants of environmental disclosure. Environmental disclosure was measured by using an environmental disclosure index and the six independent variables used in the study were company size, financial performance, strength of consumer relations, dependence on debt, dependence on the capital market and type of industry. The study found that company size and industry type influence environmental disclosure.Elijido-Ten (2004) conducted a study on the determinants of environmental disclosures by using 40 Malaysian companies by applying stakeholder theory. The environmental disclosure was measured by using an environmental disclosure index. The study used three determinants: stakeholder power, strategic posture and economic performance. The study found that both top management and government power were the determinants of environmental disclosure, and it was also found that there was no relationship between economic performance and environmental disclosure.Yuen et al. (2009) examined 200 companies to investigate the relationship between firm characteristics and voluntary disclosure. Voluntary disclosure practices were measured by using a disclosure index and the independent variables used in the study were concentration of ownership, ownership by state, individual ownership, firm size, leverage,profitability and type of industry. The study found that individual ownership, audit committee, firm size, and leverage positively related to voluntary disclosure.Galani et al. (2011) examined the relationship between environmental disclosure and firm size by using 100 Greek companies. Environmental disclosure was measured by using environmental disclosure index and the independent variables tested in the study were profitability, size and listing status. The study found that there was a positive significant relationship between environmental disclosure and size of the firm and it was also found that there was no relationship between environmental disclosure and profitability listing requirements.Joshi et al. (2011) analyzed as ma ny as 45 Indian companies’ annual reports to investigate the factors influencing environmental disclosure. The environmental disclosure was measured using environmental disclosure index and the independent variables used in the study were profitability, size, accounting firm, industry, foreign operations, age, ownership and financial leverage. The study found that size and industry were significant determinants for environmental disclosure.Rouf (2011) examined the relationship between firm-specific characteristics and Corporate Social Responsibility Disclosure (CSRD) by taking 176 Bangladesh companies. CSRD was measured by using the CSRD index and the variables in the study were independent directorsand firm size. The study found that there was a positive relationship between CSRD and independent directors and firm size did not affect CSRD.Abdo and Al-Drugi (2012) studied whether any company characteristics influenced environmental disclosures by using 43 Libyan oil and gas companies. Environmental disclosures were measured using content analysis through word count and four characteristics were selected: company’s size, privatization, age, and nationality. The study found that there was a positive association between environmental disclosure and company’s size, company’s privatization, and company’s nationality; and it was also found that the age of the company was significant and negatively related to the level of environmental disclosure.Oba and Fodio (2012) examined the relationship between board characteristics and quality of environmental disclosure by taking 21 companies in Nigeria. Environmental disclosure was measured by using an environmental disclosure index and the independent variables used in the study were board size, foreign directors, gender mix, and board independence. The study found that there was no relationship between board size and environmental disclosure.Suttipun and Stanton (2012) conducted a study on the determinants of environmental disclosure by using 75 Thai companies. The environmental disclosure was measured by word count and the fiveindependent variables used in the study were size of the company, type of industry, ownership status, profitability and country of origin of the company. The study found that there was a positive relationship between environmental disclosure and size of the company.Development of HypothesesCorporate SizeMany of the researchers found a positive relationship between environmental disclosure and size, and many studies supported that large- sized firms disclose more on environment (e.g., Kokubu et al. 2001; Joshi et al., 2011; Suttipun and Stanton, 2012; Makori and Jagongo, 2013; Akbaş , 2014; and Sulaimana et al., 2014).There is a contrast between small enterprises and large enterprises. Large companies require more funds and for that they raise funds through external sources. For attracting the investors and to reduce the agency cost, large companies disclose more information and therefore get public support (Joshi et al., 2011).ProfitabilityThe profitability of a firm is an important factor in determining the environmental disclosure practices. As for whether environmental issues are important or not, it is argued that when the profit is low, the importance of environmental issues is low (Joshi et al., 2011). Many studies have reported that there is a positive relationship betweenprofitability and environmental disclosure (e.g., Nurhayati et al., 2015). A very few studies did not support that (e.g., Galani et al. 2011; Rouf, 2011; Akbaş , 2014; and Sulaimana et al., 2014).Many studies have used the profitability ratios like Return on Assets (ROA), Return on Investment (ROI), Return on Equity (ROE), Net Profit Margin and Dividend Per Share (DPS) to measure the firm profitability. This study uses ROE to measure profitability.Financial LeverageThe agency theory states that with the increase of debt proportion in capital structure, the greater is likely to be the conflict of interest between shareholders, creditors and managers; and the higher the agency cost, the greater is the incentive for managers to disclose more information. From the perspective of social and environmental responsibilities, companies with higher financial leverage are willing to disclose more environmental information to maintain good relationship with stakeholders (Joshi et al., 2011).Many studies have supported the association between financial leverage and environmental disclosure (Joshi et al., 2011; and Sulaimana et al., 2014). They reported that financial leverage has no impact on the disclosure level in India. Kokubu et al. (2001) stated that debt did not significantly influence the corporate environmental reports in Japan. However, this study uses debt-equity ratio for measuring financialleverage.Industry TypeMany studies have examined whether the industry influences the disclosure of environmental information, and many studies have supported strongly that environmental-sensitive companies disclose more environmental information than non-environmental-sensitive companies. Joshi et al. (2011) stated that environmental-sensitive companies in India are likely to disclose more environmental protection information than others. Akbaş (2014) reported that t here is a significant positive relationship between industry membership and the extent of environmental disclosure.ConclusionThe study examined the factors influencing EADI by taking a sample of 50 companies listed on NSE. The environmental accounting disclosure is measured by EADI, and the independent variables used in the study are corporate size, age, profitability, financial leverage, legal ownership, industry and foreign operations. The relationship is tested using multiple regression analysis. The R2 under the model is 0.6033, which indicates that the model is capable of explaining 60.33% of variability in the disclosure of environmental information in the sample companies. The adjusted R2 indicates that 53.72% of variation in the dependent variable is explained by the variations in the independentvariables. The results of multiple regression reveal that there is a positive relationship between EADI and profitability, financial leverage, industry type, and legal ownership, and a negative relationship between EADI and corporate size, age and foreign operations.Limitations: The main limitation of the study is that the data was selected only for one year. The sample size was also limited. Another limitation of the study is that there are many variables which may influence environmental disclosure like board of directors, CEO’s role, audit firm size, etc., but we have selected very few variables.Future Scope: There is huge scope for further research on environmental accounting disclosure in the Indian context, as there is less amount of research on this subject. Further research can focus on the relationship between environmental accounting disclosure practices and financial performance of the companies.译文印度环境会计披露实践的影响因素:来自NIFTY 公司的经验证据B Omnamasivaya,M S V Prasad该研究通过从国家证券交易所(NSE)获取NIFTY 50 公司的样本来分析环境披露信息水平的影响因素。

外文文献翻译译文

外文文献翻译译文

环境管理会计(EMA)是管理会计发展的趋势Christine Jasch摘要:组织机构和会计师们为什么应该关心环境问题?来自供应链、资金提供商、监管机构以及其他利益相关者对于环境绩效及其信息披露的压力,导致组织机构的与环境相关的成本不断增加。

但同时提高环境绩效能够带来潜在的货币利益这一观点也逐渐得到人们的认同,传统的会计实务不能充分提供对于环境管理和与之相关的战略决策所需要的信息。

由于联合国可持续发展事务署下的环境管理会计工作组的成立,以及由它主办的出版物的发行,环境管理会计得到了促进和提升。

最近,国际会计师联合会发行了一份关于环境管理会计的指导性文件,这将进一步推动环境管理会计在会计师中的应用。

这期《清洁生产》杂志的关于环境管理会计的这个特别问题,侧重于它的方法论背景,以及来自澳大利亚、奥地利、阿根廷、加拿大、日本和立陶宛的案例研究经验。

正文:环境问题伴随者相关费用,收入和利益,正被世界上大多数国家的公民,政府组织,合作型领导人给予越来越多的关注.但是,有一个越来越广泛的共识,那就是,传统的会计不能为合理的支持在环境管理责任方面的决策制定提供准确的信息.为了填补这个差距,目前,EMA的新兴领域已经受到持续增加的关注.在19世纪九十年代早期,美国环保署是第一个成立了正式的项目去促进EMA的采纳的国家机构.从那时起,在30个国家的组织已经开始推动和落实EMA的许多不同类型的与环保相关的管理措施. 对于EMA的广泛关注是由于联合国可持续发展事务司对EMA的提倡以及其对EMA书籍的委托出版。

国际会计师联合会决定授权在由联合国科学发展司EMA工作组发表的最早的关于EMA 两本出版物的基础上发展一个关于EMA的指导性文件以整合关于EMA的最好的信息并与此同时进行必要的更新和添加.这个文件既不是有规定的要求的标准,也不是个描述性研究报告.它意在成为一个提供指导性信息的文件,作为监管要求,标准和纯粹信息的中间地带.这样, 它的目标是提供了一个总体框架和EMA的定义是相当全面,这是一致的可能与其他现有的,广泛应用于环境会计框架与EMA必须通力合作,以减少一些就这一重要议题的国际混乱功能。

环境会计核算模式研究外文文献翻译最新译文字数3000多字

环境会计核算模式研究外文文献翻译最新译文字数3000多字

环境会计核算模式研究外文文献翻译最新译文字数3000多字文献出处:Mount R. Environmental reporting and accounting in Australia: Progress, prospects and research priorities [J]. Science of the T otal Environment, 2015, 7(3): 338-349.原文The Research of Environmental Accounting ModeMount RAbstractEnvironmental accounting research began in the 1970 s. Bemons wrote the social cost of pollution control research on conversion and marin's article 1973 accounting problems of pollution, has opened the prologue of environmental accounting research. Into the 80 s countries have serious consequences for the environmental pollution, more alert, intuitive understanding, many large multinational companies began to prepare the annual environmental special expense budgets, to solve the problem of environmental protection. In June 1992, the United Nations held a conference on environment and development in Brazil, through the convention on environmental protection, "21st century agenda", will determine the sustainable development as a guide to the common development of the global strategy and action. Was held in March 1995, the international accounting and reporting standard thirteenth session of the intergovernmental expert working group, the main issue is the environment accounting; it marks the environmental problems in the development of the world as a important subject has to depth development.Keywords: Environmental accounting; Measurement; The internalization of external costs. Information disclosure1 IntroductionWith the progress of science and technology, the development of productivity, the surge of population, more and more serious damage to natural, human caused global warming, acid rain, flood, abnormal climate phenomena, such as have constitute a serious threat to human survival and development. These widespread environmental problems derived from the social and economic activities of the whole world, and as the main economic activities of enterprises lack by accounting systemarrangement, etc, necessary constraints, did not effectively take responsibility to society, natural environment pollution. It caused the world attention to people of insight, hope to carry out international cooperation norms and constraints in enterprise production and business operation activities affect the environment resources. Then, in 1998 Geneva, Switzerland, the United Nations international accounting and reporting standard intergovernmental expert working group on the 15th meeting, discuss and passed about environmental accounting and reporting system, complete the international guide - the announcement of the position of environmental accounting and reporting. Out of this guide pointed out the direction for the research of environmental accounting. After that, to solve the problem of environmental accounting, many experts and scholars put forward the view of the environmental accounting system should be established.Environmental accounting system is generally divided into two aspects of macroscopic and microscopic. Macro environment accounting is a social perspective to look at the value of resources and environment and ecological environment balanceproblems. At the same time, the micro environmental accounting as a macro environment accounting support, reflected the enterprise as a member of the society, should assume due to the business activities on the environment pollution caused by the responsibility and obligation. This requires the micro field should reflect the enterprise environment accounting system, adopts appropriate recognition and measurement method, comprehensive, continuous, systematically reflect the enterprise's environmental expenditure and income, and the environmental behavior of enterprises to supervise and analysis of information relevant to the user to provide comprehensive enterprise information, meet the requirements of the public enterprise shall bear the obligation of environmental protection demands.2 The overview of current researchEnvironmental accounting as a new branch of accounting is a combination of environment, environmental economics and development economics, accounting concepts and knowledge. Accordingly, environmental accounting in addition to adhering to the basic principle and basic method of accounting, it at the same time toabsorb and reference to include the environment, environmental economics (and its branch disciplines such as economics and pollution hazards economics, resource economics, ecological economics), in the field of development economics and other disciplines and a series of concepts and methods, on this basis to form a set of environmental accounting theory and method system. Environmental accounting theory and method of system involves the environment accounting hypothesis, accounting target, environment accounting object,etc. Core at the same time, involved in the field of environmental accounting measurement problem, given the environment accounting measurement are different from the traditional accounting, environment accounting measurement basis has the characteristics of multiplicity: opportunity cost, marginal cost and replacement costs can act as environmental accounting measurement basis. In addition, in view of the fuzziness of environmental accounting measurement can be reference to the principle of environmental economics explained; About environmental accounting report, there are two main types: supplementary report mode and independent mode. In addition, about the content of the environmental cost accounting management involves both environmental financial accounting recognition, measurement, and embodies the environmental management accounting cost control, investment decision-making, and the requirements of performance evaluation. Environmental accounting is an important part of implementing sustainable development strategy. Under the concept of sustainable development, the enterprise should be the environmental protection work through to the whole process of production and operation of the enterprise. At the same time, the assessment on the operator's fiduciary duty, should not only consider the economic accountability, should also include the social and environmental accountability.2.1 Environmental accounting research in the United StatesThe research and application of the environmental accounting is in the leading level in the world. This is mainly due to the United States environmental protection agency (hereinafter referred to as the EPA) strong impetus. Under the impetus of the EPA, many research institutions and associationreleased the stakeholders actionagenda: studio of environmental cost accounting and capital budget of a report. The report, for the development of environmental accounting, needs to solve the problem of four centers: (1) the good understanding of related terms and concepts;(2) to create internal and external management incentives;(3) education, guidance and promotion;(4) the development and dissemination of analysis tools, methods and systems. Since then, the EPA environmental accounting project along the direction of theoretical research and practical experience summed up two. In the first, first expounds the significance of environmental accounting, define the basic concepts of environment accounting. Second, EPA within the enterprise environment cost can be divided into traditional costs, hidden costs, or costs, image and public relations costs four categories, in addition to the external social costs. Finally, analyzes how the environment accounting for cost allocation, capital budgeting, process or product design, etc. The EPA argues that successful environmental management system must carry on the measurement of all environmental costs, and applied to a variety of decision-making; In the second aspect, the EPA has obtained results can be further divided into three types: one is the individual case study, to summarize the successful experience of the world's leading enterprises. Two is case set, is mainly the study of some of the same industry company; it is through the field observation and interview, questionnaire survey form a benchmark study. The combination of theory with practice to make the environment more accurately find out the problems existing in the accounting job, determine the direction of further improvement.2.2 South Korea's environmental accountingSince the mid - 1990 - s, South Korean some company began to research environmental accounting. This is mainly originated from South Korea the increased cost of environmental pollution prevention. South Korean company’s pollution p revention and control of cost from 1993 to 1999 at double-digit rate has increased dramatically, which makes the enterprise product cost rising, seriously affected the market competitiveness. On the other hand, due to the government regulation force increasing environmental regulations make financial institutions such as the external creditors more focus on enterprise environmental risk and performance, underpressure to companies to look for cost effective optimization method to improve environmental performance. Based on this, many companies have begun to realize the advance of the importance of environmental management strategy and environmental performance report, but the practice is in its infancy. Environmental accounting practice in order to promote South Korea, South Korea's environment ministry (KMOE) issued a covering the scope of environmental accounting related about "the accounting standards of environmental costs and liabilities" report, the purpose is to provide theoretical basis and the introduction of environmental accounting in South Korea relevant methods, mainly includes the definition of environmental accounting, environmental accounting conceptual framework, and the field environment accounting practices and environmental accounting in South Korea, and other standard draft.3 Environmental accounting theory basisEnvironmental accounting is closely connected withaccounting, the accounting profession of the environmental accounting mainly embodied in environmental accounting as a branch of accounting, the recognition and measurement should be the product of the multi-discipline together, its basic value can be activities to the environment and related economic activity provides reflect and control. Mainly embodied in five aspects:3.1 Environmental accounting is a new branch of accountingHere involves three levels of content: first, the environmental accounting as a branch of enterprise accounting, on the whole reflects the existing enterprise accounting (including financial accounting, management accounting, etc.), the basic principle and basic methods, and only in special cases should be considered the influence of environmental factors; Second, the economic development, the more important accounting, this concept applies not only to environmental accounting, but also in the environmental accounting factors coordination, balance social interests, enterprise and play an important role in environmental effects; Third, environment accounting is aimed at companies, administrative institution of environmental effect and influence is relatively small, or only play the role of enterprises andenvironmental work, so in the future a period of administrative institutions to establish the necessity of environmental accounting is low. This from another Angle, interpretation of environmental accounting is a branch of accounting.3.2 Environmental accounting is the product of the combination of interdisciplinary developmentEnvironmental accounting is the environment, environmental economics and development economics, theproduct of the combination of accounting. Accordingly, environmental accounting in addition to adhering to the basic principle and basic method of accounting, it at the same time to absorb and reference to include the environment, environmental economics (and its branch disciplines such as economics and pollution hazards economics, resource economics, ecological economics), in the field of development economics and other disciplines and a series of concepts and methods, on this basis to form a set of environmental accounting theory and method system.3.3 Environmental accounting to make the scope of the accounting entity is broaderEnvironmental accounting and financial accounting is the same need to consider the concept of accounting entity. This due to the accounting entity concept as the main body of accounting in the enterprises, to undertake the rights and obligations of assets and liabilities. For environmental accounting, the body is not just a for-profit economic organization, and should be considered a social unit and link in the total system, need a certain amount of social responsibility, and environmental accounting entity concept is beyond the scope of general enterprise accounting entity and should as far as possible from the perspective of social and environmental control of the enterprise the management activities. Otherwise, environmental accounting will be established. At the same time, the accounting should not only on the enterprise's economic benefit, but also examine environmental benefits as well as the reflection of the enterprise the combination of two kinds of benefits, which is reflected in the environmental accounting measurement model selection. Concrete embodiment in should adopt the method ofmonetary measurement, and to use the real measurement. In the monetary measurement should not only use the strong historical cost, reliabilityand need to consider the adoption of other measurement model.译文环境会计核算模式研究作者:Mount R摘要环境会计的研究始于70 年代。

会计环境对会计确认与计量的影响 外文文献译文及原文精品文档18页

会计环境对会计确认与计量的影响 外文文献译文及原文精品文档18页

Contents Abstract..........................................................................................I Introduction (Ⅱ)Efficient Accounting Systems (1)Chapter 1 Accounting (1)1.1 The decision of accounting (2)1.2 The functions of accounting (4)Chapter 2 Accounting environment (7)2.1 The goal of accountant is the starting point in which accounting environment affects the accounting information system (9)2.2 Accounting assumed reveals close link between accounting and its interdependent external environment (10)2.3 Accounting standards disclose the request of accountingenvironment to accounting information (13)Chapter 3 Accounting system (15)Conclusion (30)References (31)Thanks (32)Efficient Accounting SystemsThe existence and development of everything are under certain environmental conditions. Accounting, as one of the most important practice of human activities is not a cases outside. Accounting environment have the base sense for the smooth conduct of the activities of accounting, while various accounting environmental factors will have isolated impact on total activity of the accounting system. The study of the structure of the accounting environment system and the relations between the various elements in this system made us to be much more realistic in this area ofaccounting theory and practice, to build a harmonious Environmental System for clear direction, so as to promote the accounting cause of sustainable development.Chapter 1 Accounting1.1 The decision of accountingAccounting is one of the fastest growing fields in the modern business world. Every new shore, school, restaurant, or filling station indeed, any new enterprise of any kind increases the demand for accountants. Consequently, the demand for accountants is generally much greater than the supply. Government official often have a legal background: similarly, the men and women in management often have a background in accounting. They are usually familiar with the methodology of finance and fundamentals of fiscal and business administration.Today’s accountants ar e as diverse as their job assignments. Accountants may be male or female, outgoing or conservative, but they are all analytical. They may have backgrounds in art history or computer programming. They come from every ethnic and cultural background.The accounting backgrounds can open doors to most lines of business. In short, accounting deals with all facets of anorganization —purchasing, manufacturing, marketing, and distribution. This is why accounting provides such an excellent basis for business experience. Accounting is an information system necessitated by the great complexity of modern business.1.2 The functions of accountingOne of the most important functions of accounting is to accumulate and report financial information that shows an organization’s financial position and the results of its operations to its interested users. These users include managers, stockholders, banks and other creditors, governmental agencies, investment advisors, and the general public. For example, stockholders must have an organization’s financial information in order to measure its management’s performance and to evaluate their own holdings. Banks and other creditors must consider the financial strength of a business before permitting it to borrow funds. Potential investors need financial data in order to compare prospective investments. Also many laws require that extensive financial information be reported to the various levels of government. Businesses usually publish such reports at least annually. To meet the needs of the external users, a framework of accounting standards, principles and procedures known as “generally accepted accounting principles” have been developedto insure the relevance and reliability of the accounting information contained in these external financial reports. The subdivision of the accounting process that produces these external reports is referred to as financial accounting.Another important function of accounting is to provide the management inside an organization with the accounting information needed in the organization’s internal decision-making, which relates to planning, control, and evaluation within an organization. For example, budgets are prepared under the directions of a company’s controller on an annual basis and express the desi res and goals of the company’s management. A performance report is supplied to help a manager focus his attention on problems or opportunities that might otherwise go unnoticed. Furthermore, cost-benefit data will be needed by a company’s management in deciding among the alternatives of reducing prices, increasing advertising, or doing both in attempt to maintain its market shares. The process of generating and analyzing such accounting information for internal decision –making is often referred to as managerial accounting and the related information reports being prepared are called internal management reports. As contrasted with financial accounting, a management accounting information system provides both historical and estimated information that is relevant to thespecific plans on more frequent basis. And managerial accounting is not governed by generally accepted accounting principles. Chapter 2 Accounting environmentThe growth of organizations, changes in technology, government regulation, and the globalization of economy during the twentieth century have spurred the development of accounting. As a result, a number of specialized fields of accounting have evolved in addition to financial accounting and managerial accounting, which include auditing, cost accounting, tax accounting, budgetary accounting, governmental and not –for-profit accounting, human resources accounting, environmental accounting, social accounting, international accounting, etc. For example, tax accounting encompasses the preparation of tax returns and the consideration of the tax consequences of proposed business transactions or alternative courses of action. Governmental and not-for-profit accounting specializes in recording and reporting the transactions of various governmental units and other not-for-profit organizations. International accounting is concerned with the special problems associated with the international trade of multinational business organizations. All forms of accounting, in the end, provide information to the related users and help them make decisions.Accountant the environment has, the development closely with accountant related, and decided that accountant the thought that the accounting theory, accountant organize, accountant the legal system as well as the accountancy level of development historic condition and the particular case.Studies accountant the environment the influence which develops to accountant, should take accountant the goal, accountant suppose, the accounting standards as the clue.2.1 The goal of accountant is the starting point in which accounting environment affects the accounting information system Each kind of accountant under the pattern accountant the goal concrete difference may sum up as accountant the environment different result. Looking from longitudinal, the different historical period, accountant the environment is different, accountant the goal is also different, from this causes the accounting information existence huge difference; Looking from crosswise, different national accountant the environment is different, accountant the goal content has the difference, its accounting information is also unique. About accountant the goal, the theorists have “the policy-making useful view” and “the management responsibility view” the s truggle. What policy-making useful view interdependence is the developed capital market, theresources request and is entrusted with something the relations are establishes through the capital market. Thus, the resources entrusting party and is entrusted with something the side responsibility relations intermediary becomes because of the capital market fuzzy. But the responsibility view to base the resources request which forms in the direct intercourse with is entrusted with something the relations. Western various countries and the international accounting standards committee approve the policy-making useful view. If the international accounting standards committee said that “must focus the attention to provide to the economic decision-making useful inform ation”. Comparatively speaking, the management responsibility view depends on each other accountant the environment and the Chinese present stage economic reform and the development actual situation even more tallies. The current our country financial inventory accounting's essential target, should locate, in approaches the trustee to report the fiduciary duty in the fulfillment situation. Because of from the time, the management responsibility view mainly faces the future, but faces in the past and the present. But in accountant confirmed that the standard and the measurement foundation's choices aspect, the foothold in the past and the present must be easier than in the future the foothold, provided the information quality even more drewclose to the goal the request.Because just accountant the goal affects the accounting information system's basic reason, therefore, the environment embarks from accountant to accountant the goal locates, can cause the accounting theory to move toward the accounting practice from Yu the accounting practice.2.2 accountants supposed has promulgated accountant between the external environment close relations which depended on each other with it.Accountant supposes is the accounting personnel the reasonable judgment which locates to the accounting the change which does not decide accountant who the environment makes, is the accounting basic premise Accountant supposes to financial inventory accounting has the overall importance influence, it is the behavior main body and the general situation embarks from accountant constructs the system info, American Accounting standards Committee Respective Accountant Research department's first memoir is “accountant's fundamental assumption”. Although theoretically speaking, the sound value information will have the guidance compared to the historical costs information regarding the user future economic decision-making, just like but US Chartered accountant the Association financial report Technical committee will publish thetopic will be "Improvement Enterprise Reported that - - Customer Guidance" said that the numerous users did not advocate by the sound value pattern substitution historical costs pattern, its reason will mainly be stems from the guarantee financial report information consistency, reliable and the cost - benefit principle consideration. However, they advocate many kinds of measurement attribute mix valuation.Accountant supposes is based on the external environment uncertainty proposed that therefore, may say that accountant supposes is the accounting theory and accountant the environment connected border meeting point, depends on each other accountant with it the environment to have the extremely close relationship. 2.3 The accounting standards disclose accountant the environment to the accounting information requestAccountant the environment to accounting standards' influence, may manifest in the accounting standards technical nature, the social two aspects.1. Technical nature. The accounting standards were considered that is one kind of pure objective restraint organization, one merely technical's standard method, its goal is enables accounting practice processing the science, to be reasonable, to be consistent. Since produces the behavior has universal restraint accountantafter accountant the standard system, accountant reforms mainly displays in accountant the standard system's reform, but accountant standard system's reform, displays for concrete accountant the computing technique innovation.2. Sociality. The different accounting standards will have the different accounting information, thus affects the different main body benefit, it will cause part of people to profit, but another part of people possibly suffer injury. The accounting standards produce the economic consequences prove its and impure objective. Accounting standards' sociality materially is the economic interest question, immediate influence to economic interest between related various aspects assignment. One of market economy's base elements is the fair competition;All market economy participants cannot different form the rank difference because of the right status. If the administrative right trades the behavior with the market economy to unify in together, will destroy the market mechanism, will be unable to realize the market economy effective disposition resources function. Therefore accounting standards' formulation organization must be the neutral organization, guarantees the accounting standards fairness and the rationality.Chapter 3 Accounting SystemAccounting system refers to establish accounting andaccounting supervision procedure and method of business activities. Effective accounting system should do:1. Confirmed and record all real business, timely and detailed description of economic business, so in the financial and accounting reports of economic business appropriately classified.2. Measurement value of economic business, so in the financial and accounting reports records in the appropriate monetary value.3. Determine the time, business to business records in the appropriate accounting period.4. In the financial and accounting reports, business and proper disclosure of expression related matters.有效会计体系任何事物都是在一定的环境条件下存在和发展的, 作为人类重要实践活动之一的会计活动也不例外。

英文文献翻译 绿色会计成本的措施

英文文献翻译 绿色会计成本的措施

绿色会计成本的措施摘要在过去,大型公司和中小企业的环境问题往往是被忽略的。

然而,在最近的几年,环境会计或简称“绿色会计”秉承着越来越多的关注。

许多企业,尤其是中小型企业(中小企业)现在对“绿色”感兴趣,许多投资者将环境责任看成是高价值的。

从业务和管理的变化看,许多环境成本能够显著减少或消除作为业务的决策,从而投资于更环保的工艺技术中,然后重新设计流程。

工业和绿色运动正朝着倾斜可持续发展的关键概念达成共识。

更好的自然资源和绿色帐目会为环境与经济之间的相互作用提供有价值的见解。

然而,在组织实施绿色会计,由于某种原因导致抵抗,如缺乏意识,缺乏道德教育,忽视等,如在马来西亚的中小企业。

本文重点围绕企业绿色会计在财务报告的问题进行研究。

本文的主要目的是勾勒出一套在环境管理会计事务所的制度和加以解决绿色会计的措施。

关键词:绿色会计;环境会计;绿色成本;马来西亚的中小企业1.引言绿色会计是有关环境信息和环境生态审计制度,并已被定义为“识别,跟踪,分析和重新移植的材料和成本与组织的环境因素有关的信息。

绿色会计是比较新的和发展的领域。

然而,马来西亚的绿色会计被认为是处于起步阶段,因为,绿色会计的组织,由于某种原因导致抵抗性,如缺乏认识,缺乏绿色和道德教育的忽视,等等,如中小企业在马来西亚的实施。

绿色会计处理有关的环境和社会影响的会计和管理问题,规定和限制,安全,环保和经济上可行的能源生产和供应。

绿色会计的首要任务是解决社会环境问题,并可能对实现在任何国家的可持续发展和环境,影响了公司在面对社会和环境责任问题行为的因素。

国际会计师联合会将绿色会计环境定义为“通过适当的环境相关的会计制度和办法的制定和实施管理的经济绩效,虽然这可能包括报告和审计的一些企业,绿色交流计数通常会涉及到生命周期成本,全成本核算,效益评估和环境管理战略规划”。

此外,联合国可持续发展司强调,绿色会计系统产生的信息用于内部决策,这种信息可以是物质的或货币的焦点。

环境会计信息披露外文文献翻译中英文.pdf

环境会计信息披露外文文献翻译中英文.pdf

外文文献翻译原文及译文(本文档归max118 网hh2018 所有,仅供下载使用)中文标题:印度环境会计披露实践的影响因素:来自NIFTY 公司的经验证据文献出处:The IUP Journal of Accounting Research & Audit Practices, Vol. 15, No. 1, 2016译文字数:3900 多字原文Factors Influencing Environmental Accounting and Disclosure Practices in India: Empirical Evidence from NIFTY CompaniesB Omnamasivaya* and M S V PrasadThe study examines the factors determining the level of environmental disclosure information by taking a sample of NIFTY 50 companies from National Stock Exchange (NSE). The environmental information disclosure is measured by using an Environmental Accounting Disclosure Index (EADI) and the variables used in the study are profitability, corporate size, age, financial leverage, industry type, legal ownership and foreign operations. The relationship is tested using multiple regression analysis. The results show that there is a positive relationship between EADI and profitability, financial leverage, industry type and legal ownership, and a negative relationship between EADI and corporate size, age and foreign operations.IntroductionClimate change is one of the greatest challenges that the world is facing today. Climate change is the variation in the global climate over time. The climate change creates manifold problems like global warming, glacier meltdown, soil erosion, land degradation, deforestation, loss of biodiversity and all kinds of pollution. Human influence on the nature is one of the major causes of such problems. Indiscriminate use of resourcesand undue influence on nature in the name of development can be identified as the prime causes of climate change. As a result, in the last few decades, the adverse effect of environmental pollution on economic development has become a public concern all over the world (Goswami, 2014).The state of world‘s environment and the impact of mankind on the ecology of the world have led to increased public concern and scrutiny of the operations and performance of organizations. Globally, corporations are expected to include environmental concerns in business operations and interaction with stakeholders. As a result, firms can no longer ignore the problems of the society in which they operate. This has thus instituted a social contract between organizations and the environment, thereby making environmental responsibility a corporate dictate (Olayinka and Oluwamayowa, 2014).Every business has responsibility to use the resources at judiciously. Every enterprise needs to behave like a good corporate citizen, and the corporate behavior is judged by its actions related to the community, the steps taken to protect the environment or pollution control. In the context of the Indian corporate sector, companies are not performing as good citizens. Due to this reason many laws have been laid down by the government for making the companies good corporate citizens and fulfill their social responsibility (Chauhan, 2005).In India, the economic reforms initiated in the 1990s have unwittingly contributed to a rise in environmental problems. The awareness level of stakeholders and public regarding the environmental issues has increased the pressure on companies to disclose environmental information. As a result, the companies have started disclosing the environmental information in annual reports and sustainability reports to satisfy all their stakeholders.The Indian government has taken several steps to protect the environment. It has set up the Ministry of Environment, Forest and Climate Change (MoEFCC) with the aim to coordinate, among the states and the various ministries, the issues relating to environmental protection and antipollution measures. Necessary legislation has also been passed. In India, Central Pollution Control Board (CPCB) and State Pollution Control Board (SPCB) were established under the Water Act. The CPCB has identified 17 categories of industries which are highly polluting (Joshi et al., 2011).In India, specific environmental accounting rules or environmental disclosure guidelines for communication to different stakeholder groups are not available for Indian companies. There is no mandatory requirement for quantitative disclosure of (financial) environmental information in annual reports either under the Companies Act or as per the Indian Accounting Standards. Furthermore there are 23 stockexchanges in India which are controlled by the Securities Exchange Board of India (SEBI) Act, 1992. Each of these stock exchanges has different listing requirement for Indian companies to disclose environmental information. Therefore, any environmental disclosure by Indian companies is purely voluntary (Makori and Jagongo, 2013). Against this backdrop, the present study examines the factors determining the level of environmental disclosure information in India.Legitimacy TheoryIn order to explain the reasons for environmental disclosure, we use legitimacy theory. There are many theories which explain the various reasons for social and environmental accounting disclosures, but legitimacy theory is the most suitable theory to explain the environmental disclosure. Organizations cannot survive without meeting the societal expectations. The society expects that the organizations should be proactive in protecting the environment and minimizing the environmental hazards. In case organizations fail to meet the societal expectations, there is a severe threat to their existence. Nowadays Indian companies are legitimizing because of the awareness about environmental disclosure practices in the society. Therefore, Indian companies are taking several steps to protect the environment and are disclosing the relevant environmental information in their annual reports and company websites.Legitimacy relates to the environmental issues which are disclosedin the companies’ annual reports. This indicates the management concerns towards the community. Therefore, the management of different companies or managers have different ideas or thoughts about what the society expects and managers will adapt different strategies to show the society that the organization is meeting the expectations of the community (Zain, 2006).The theory of legitimacy is based on two fundamental ideas: companies need to legitimize their activities, and the process of legitimacy that confers benefits to businesses. Thus, the first element is compatible with the idea that environmental disclosure is related to the social pressure. In this context, the need for legitimacy is not the same for all companies due to the degree of social pressure the company is exposed to, and the level of response to this pressure. There are a number of factors which determine the degree of social pressure on companies and their responses to the pressure. These factors are potential determinants of corporate social disclosure. The second component is based on the idea that companies can expect to benefit by a legitimate behavior based on the social responsibility activity. In addition to that, the legitimacy theory provides a comprehensive framework to explain both the determinants and consequences of social disclosure (Mohamed et al., 2014).Literature ReviewKokubu et al. (2001) examined the annual reports of 1,203 companies to investigate the determinants of environmental disclosure. Environmental disclosure was measured by using an environmental disclosure index and the six independent variables used in the study were company size, financial performance, strength of consumer relations, dependence on debt, dependence on the capital market and type of industry. The study found that company size and industry type influence environmental disclosure.Elijido-Ten (2004) conducted a study on the determinants of environmental disclosures by using 40 Malaysian companies by applying stakeholder theory. The environmental disclosure was measured by using an environmental disclosure index. The study used three determinants: stakeholder power, strategic posture and economic performance. The study found that both top management and government power were the determinants of environmental disclosure, and it was also found that there was no relationship between economic performance and environmental disclosure.Yuen et al. (2009) examined 200 companies to investigate the relationship between firm characteristics and voluntary disclosure. Voluntary disclosure practices were measured by using a disclosure index and the independent variables used in the study were concentration of ownership, ownership by state, individual ownership, firm size, leverage,profitability and type of industry. The study found that individual ownership, audit committee, firm size, and leverage positively related to voluntary disclosure.Galani et al. (2011) examined the relationship between environmental disclosure and firm size by using 100 Greek companies. Environmental disclosure was measured by using environmental disclosure index and the independent variables tested in the study were profitability, size and listing status. The study found that there was a positive significant relationship between environmental disclosure and size of the firm and it was also found that there was no relationship between environmental disclosure and profitability listing requirements.Joshi et al. (2011) analyzed as ma ny as 45 Indian companies’ annual reports to investigate the factors influencing environmental disclosure. The environmental disclosure was measured using environmental disclosure index and the independent variables used in the study were profitability, size, accounting firm, industry, foreign operations, age, ownership and financial leverage. The study found that size and industry were significant determinants for environmental disclosure.Rouf (2011) examined the relationship between firm-specific characteristics and Corporate Social Responsibility Disclosure (CSRD) by taking 176 Bangladesh companies. CSRD was measured by using the CSRD index and the variables in the study were independent directorsand firm size. The study found that there was a positive relationship between CSRD and independent directors and firm size did not affect CSRD.Abdo and Al-Drugi (2012) studied whether any company characteristics influenced environmental disclosures by using 43 Libyan oil and gas companies. Environmental disclosures were measured using content analysis through word count and four characteristics were selected: company’s size, privatization, age, and nationality. The study found that there was a positive association between environmental disclosure and company’s size, company’s privatization, and company’s nationality; and it was also found that the age of the company was significant and negatively related to the level of environmental disclosure.Oba and Fodio (2012) examined the relationship between board characteristics and quality of environmental disclosure by taking 21 companies in Nigeria. Environmental disclosure was measured by using an environmental disclosure index and the independent variables used in the study were board size, foreign directors, gender mix, and board independence. The study found that there was no relationship between board size and environmental disclosure.Suttipun and Stanton (2012) conducted a study on the determinants of environmental disclosure by using 75 Thai companies. The environmental disclosure was measured by word count and the fiveindependent variables used in the study were size of the company, type of industry, ownership status, profitability and country of origin of the company. The study found that there was a positive relationship between environmental disclosure and size of the company.Development of HypothesesCorporate SizeMany of the researchers found a positive relationship between environmental disclosure and size, and many studies supported that large- sized firms disclose more on environment (e.g., Kokubu et al. 2001; Joshi et al., 2011; Suttipun and Stanton, 2012; Makori and Jagongo, 2013; Akbaş , 2014; and Sulaimana et al., 2014).There is a contrast between small enterprises and large enterprises. Large companies require more funds and for that they raise funds through external sources. For attracting the investors and to reduce the agency cost, large companies disclose more information and therefore get public support (Joshi et al., 2011).ProfitabilityThe profitability of a firm is an important factor in determining the environmental disclosure practices. As for whether environmental issues are important or not, it is argued that when the profit is low, the importance of environmental issues is low (Joshi et al., 2011). Many studies have reported that there is a positive relationship betweenprofitability and environmental disclosure (e.g., Nurhayati et al., 2015). A very few studies did not support that (e.g., Galani et al. 2011; Rouf, 2011; Akbaş , 2014; and Sulaimana et al., 2014).Many studies have used the profitability ratios like Return on Assets (ROA), Return on Investment (ROI), Return on Equity (ROE), Net Profit Margin and Dividend Per Share (DPS) to measure the firm profitability. This study uses ROE to measure profitability.Financial LeverageThe agency theory states that with the increase of debt proportion in capital structure, the greater is likely to be the conflict of interest between shareholders, creditors and managers; and the higher the agency cost, the greater is the incentive for managers to disclose more information. From the perspective of social and environmental responsibilities, companies with higher financial leverage are willing to disclose more environmental information to maintain good relationship with stakeholders (Joshi et al., 2011).Many studies have supported the association between financial leverage and environmental disclosure (Joshi et al., 2011; and Sulaimana et al., 2014). They reported that financial leverage has no impact on the disclosure level in India. Kokubu et al. (2001) stated that debt did not significantly influence the corporate environmental reports in Japan. However, this study uses debt-equity ratio for measuring financialleverage.Industry TypeMany studies have examined whether the industry influences the disclosure of environmental information, and many studies have supported strongly that environmental-sensitive companies disclose more environmental information than non-environmental-sensitive companies. Joshi et al. (2011) stated that environmental-sensitive companies in India are likely to disclose more environmental protection information than others. Akbaş (2014) reported that t here is a significant positive relationship between industry membership and the extent of environmental disclosure.ConclusionThe study examined the factors influencing EADI by taking a sample of 50 companies listed on NSE. The environmental accounting disclosure is measured by EADI, and the independent variables used in the study are corporate size, age, profitability, financial leverage, legal ownership, industry and foreign operations. The relationship is tested using multiple regression analysis. The R2 under the model is 0.6033, which indicates that the model is capable of explaining 60.33% of variability in the disclosure of environmental information in the sample companies. The adjusted R2 indicates that 53.72% of variation in the dependent variable is explained by the variations in the independentvariables. The results of multiple regression reveal that there is a positive relationship between EADI and profitability, financial leverage, industry type, and legal ownership, and a negative relationship between EADI and corporate size, age and foreign operations.Limitations: The main limitation of the study is that the data was selected only for one year. The sample size was also limited. Another limitation of the study is that there are many variables which may influence environmental disclosure like board of directors, CEO’s role, audit firm size, etc., but we have selected very few variables.Future Scope: There is huge scope for further research on environmental accounting disclosure in the Indian context, as there is less amount of research on this subject. Further research can focus on the relationship between environmental accounting disclosure practices and financial performance of the companies.译文印度环境会计披露实践的影响因素:来自NIFTY 公司的经验证据B Omnamasivaya,M S V Prasad该研究通过从国家证券交易所(NSE)获取NIFTY 50 公司的样本来分析环境披露信息水平的影响因素。

会计英文文献及翻译

会计英文文献及翻译

IMPLEMENTING 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 main groups 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. To arrive at a practical solution to the implementation of E CA 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 andmedium-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 500employees Turnover up to EUR 50m Management Organization- Owner-cum-entrepreneur -Divisional organization is rare- Varies from a patriarchal management -Short flow of information style in 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 of employees- limited possibilities of financing -wide expertise-high satisfaction of employeesSupply chain Innovation-closely involved in local -high potential of innovation economic 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 background knowledge 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 the current 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. To 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, standardizedstand-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 a conventional 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 softwaremodule 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 andenvironmental/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. To 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 and changes 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。

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. . 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.。

环境会计外文文献及其翻译(可编辑修改word版)

环境会计外文文献及其翻译(可编辑修改word版)

河南科技学院新科学院2013 届本科毕业论文(设计)外文文献及翻译Environmental Accounting学生姓名:叶乃润所在系别:经济系所学专业:国际经济与贸易导师姓名:郭晓明(助教)完成时间:2013 年 4 月 18 日Environmental Accountingby 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 the difficulties and 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.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 building routine 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 study “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. Once adjusted to account 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 decision makers 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 tocapture 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 non marketed goods and services of the environment. Thus Filipinos estimate monetary values for such items as gathered fuel wood 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 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 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 u se.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, 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.Green GDP. Developing a gross domestic product that includes the environment is also a matter of controversy. Most people actively involved in building environmental accounts minimize 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. 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.Environmental 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, theUN published the System for Integrated Economic and Environmental Accounting (SEEA) as an annex to the 1993 revisions 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,” comprised primarily of national income accountants and statisticians from OECD countries. The group’s work will be an important step toward con sensus on accounting methods, but the process will be lengthy: Development of the conventional SNA took some forty years.A 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 time series 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.环境会计by Joy E. Hecht由利益增长改变国民收入核算制度以促进了解经济和环境之间的联系。

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河南科技学院新科学院2013届本科毕业论文(设计)外文文献及翻译Environmental Accounting学生姓名:***所在系别:经济系所学专业:国际经济与贸易导师姓名:郭晓明(助教)完成时间:2013年4月18日Environmental Accountingby 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 the difficulties and 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.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 building routine 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 study “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. Once adjusted to account for that depreciation, Indonesia’s GDP and growth rates both sank significantly below conventional figures. While “Wasting Assets” called many to action, it also op erated as a brake, leading many economists and statisticians to warn against a focus on green GDP, because it tells decision makers 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 tocapture 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 non marketed goods and services of the environment. Thus Filipinos estimate monetary values for such items as gathered fuel wood 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 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 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, 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.Green GDP. Developing a gross domestic product that includes the environment is also a matter of controversy. Most people actively involved in building environmental accounts minimize 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. 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.Environmental accounting would receive a substantial boost if an international consensus could be reached on methodology. The UN Statistics Department hascoordinated 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 revisions 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,” comprised 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 years.A 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 time series 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.环境会计by Joy E. Hecht由利益增长改变国民收入核算制度以促进了解经济和环境之间的联系。

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