外文翻译 -面对绿色贸易壁垒升级
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本科毕业论文外文翻译Undergraduate Thesis External Translation (700 Words)Title: The Impact of Social Media on Consumer Behavior Abstract:With the rapid development of social media, its influence on consumer behavior has drawn increasing attention from scholars and marketers. This paper aims to explore the impact of social media on consumer behavior from the perspective of information acquisition, interpersonal communication, and brand evaluation. Through a literature review and analysis, it is found that social media has a significant impact on consumer behavior by providing easy access to information, facilitating communication between consumers, and influencing brand perception. This research provides valuable insights for marketers in understanding and utilizing social media platforms to effectively engage with consumers and influence their purchasing decisions.1. IntroductionSocial media has become an integral part of people's daily lives, and its impact on consumer behavior cannot be ignored. This paper aims to investigate the impact of social media on consumer behavior and provide practical implications for marketers. The research question is: How does social media influence consumer behavior in terms of information acquisition, interpersonal communication, and brand evaluation?2. Information Acquisition2.1 Social media provides a platform for consumers to easilyaccess information about products and services. Through social media platforms such as Facebook, Instagram, and Twitter, consumers can obtain product reviews, comparisons, and recommendations from peers. This information influences consumers' purchasing decisions and enhances their knowledge about products.2.2 Social media also serves as a source of entertainment and inspiration, enabling users to discover new trends and products. Influencers and celebrities, who gain popularity through social media, often endorse products and create consumer desire for these items. This form of indirect advertising through social media has a significant impact on consumer behavior.3. Interpersonal CommunicationSocial media platforms enable users to interact with friends, family, and even strangers. This communication aspect of social media hasa direct influence on consumer behavior.3.1 Word-of-mouth (WOM) communication through social media is prevalent. Consumers often share their positive or negative experiences with products on social media platforms, which influence others' opinions and purchasing decisions. These online conversations have a wide reach and can greatly impact brand perception.3.2 Social media facilitates communication between consumers and brands. Consumers can directly communicate with brands through social media channels, providing feedback, asking questions, and seeking assistance. This two-way communicationimproves customer satisfaction and loyalty.4. Brand Evaluation4.1 Social media plays a crucial role in brand evaluation. Consumers often seek information about brands, their values, and their reputation on social media platforms. Positive or negative brand mentions and reviews on social media greatly influence consumers' perceptions of brands, leading to either increased or decreased brand trust and loyalty.4.2 Social media influencers and celebrities endorsing particular brands also impact brand evaluation. These individuals' recommendations and opinions can greatly influence consumers' perceptions and preferences for specific brands.5. ConclusionIn conclusion, social media has a significant impact on consumer behavior by influencing information acquisition, interpersonal communication, and brand evaluation. Marketers should utilize and engage with social media platforms to effectively reach and influence their target customers. This research provides insights for marketers to enhance their social media strategies and create effective brand-consumer interactions.。
本科毕业论文外文参考文献译文及原文学院经济与贸易学院专业经济学(贸易方向)年级班别2007级 1 班学号3207004154学生姓名欧阳倩指导教师童雪晖2010 年 6 月 3 日目录1 外文文献译文(一)中国银行业的改革和盈利能力(第1、2、4部分) (1)2 外文文献原文(一)CHINA’S BANKING REFORM AND PROFITABILITY(Part 1、2、4) (9)1概述世界银行(1997年)曾声称,中国的金融业是其经济的软肋。
当一国的经济增长的可持续性岌岌可危的时候,金融业的改革一直被认为是提高资金使用效率和消费型经济增长重新走向平衡的必要(Lardy,1998年,Prasad,2007年)。
事实上,不久前,中国的国有银行被视为“技术上破产”,它们的生存需要依靠充裕的国家流动资金。
但是,在银行改革开展以来,最近,强劲的盈利能力已恢复到国有商业银行的水平。
但自从中国的国有银行在不久之前已经走上了改革的道路,它可能过早宣布银行业的改革尚未取得完全的胜利。
此外,其坚实的财务表现虽然强劲,但不可持续增长。
随着经济增长在2008年全球经济衰退得带动下已经开始软化,银行预计将在一个比以前更加困难的经济形势下探索。
本文的目的不是要评价银行业改革对银行业绩的影响,这在一个完整的信贷周期后更好解决。
相反,我们的目标是通过审查改革的进展和银行改革战略,并分析其近期改革后的强劲的财务表现,但是这不能完全从迄今所进行的改革努力分离。
本文有三个部分。
在第二节中,我们回顾了中国的大型国有银行改革的战略,以及其执行情况,这是中国银行业改革的主要目标。
第三节中分析了2007年的财务表现集中在那些在市场上拥有浮动股份的四大国有商业银行:中国工商银行(工商银行),中国建设银行(建行),对中国银行(中银)和交通银行(交通银行)。
引人注目的是中国农业银行,它仍然处于重组上市过程中得适当时候的后期。
第四节总结一个对银行绩效评估。
毕业论文外文翻译格式毕业论文外文翻译格式在撰写毕业论文时,外文翻译是一个重要的环节。
无论是引用外文文献还是翻译相关内容,都需要遵循一定的格式和规范。
本文将介绍一些常见的外文翻译格式,并探讨其重要性和应用。
首先,对于引用外文文献的格式,最常见的是使用APA(American Psychological Association)格式。
这种格式要求在引用外文文献时,先列出作者的姓氏和名字的首字母,然后是出版年份、文章标题、期刊名称、卷号和页码。
例如:Smith, J. D. (2010). The impact of climate change on biodiversity. Environmental Science, 15(2), 145-156.在翻译外文文献时,需要注意保持原文的准确性和完整性。
尽量避免意译或添加自己的解释,以免歪曲原文的意思。
同时,还需要在翻译后的文献后面加上“译者”和“翻译日期”的信息,以便读者可以追溯翻译的来源和时间。
其次,对于翻译相关内容的格式,可以参考国际标准组织ISO(International Organization for Standardization)的格式。
这种格式要求在翻译相关内容时,先列出原文,然后是翻译后的文本。
例如:原文:The importance of effective communication in the workplace cannot be overstated.翻译:工作场所有效沟通的重要性不容忽视。
在翻译相关内容时,需要注意保持原文的意思和语气。
尽量使用准确的词汇和语法结构,以便读者能够理解和接受翻译后的内容。
同时,还需要在翻译后的文本后面加上“翻译者”和“翻译日期”的信息,以便读者可以追溯翻译的来源和时间。
此外,对于长篇外文文献的翻译,可以考虑将其分成若干章节,并在每个章节前面加上章节标题。
这样可以使读者更容易理解和阅读翻译后的内容。
毕业论文外文翻译硕士毕业论文外文翻译硕士近年来,随着全球化的加速和信息交流的便利,外文翻译行业迎来了空前的发展机遇。
尤其是在中国,随着国际交流的不断深化,外文翻译的需求日益增长。
毕业论文外文翻译硕士专业应运而生,成为了许多热衷于翻译事业的学子们的首选。
毕业论文外文翻译硕士专业的课程设置涵盖了翻译理论、翻译技巧、专业知识和实践能力等方面。
学生们将通过学习和研究,掌握翻译的基本原理和方法,培养独立思考和解决问题的能力。
此外,毕业论文外文翻译硕士专业还注重培养学生的跨文化交际能力和语言表达能力,以适应多元化的翻译需求。
在毕业论文外文翻译硕士专业的学习过程中,学生们将进行大量的实践训练。
他们将翻译各类专业文献、学术论文、商务文件等,以提高自己的翻译水平和专业素养。
同时,学生们还将参与翻译项目的实践,与真实的翻译需求接轨,锻炼自己的实际操作能力。
毕业论文外文翻译硕士专业的学习不仅仅是对翻译技巧和知识的掌握,更是对跨文化交流和理解的深入思考。
在全球化的时代背景下,了解不同文化的差异和共同点,是一位优秀的翻译人员必备的素质。
因此,毕业论文外文翻译硕士专业注重培养学生的跨文化意识和跨文化沟通能力,使他们能够更好地理解和传达不同文化的信息。
毕业论文外文翻译硕士专业的学生毕业后,将有广阔的就业前景。
他们可以选择从事翻译工作,为各类机构和企业提供专业的翻译服务。
他们也可以选择从事教学和研究工作,为培养更多的翻译人才做出贡献。
此外,随着互联网和科技的发展,新兴的翻译领域也将为毕业论文外文翻译硕士专业的学生提供更多的就业机会。
然而,毕业论文外文翻译硕士专业也面临一些挑战和问题。
首先,随着机器翻译技术的不断发展,传统的人工翻译是否会受到冲击,成为了人们关注的焦点。
其次,由于翻译行业的特殊性,翻译人员的工作强度和压力较大,需要具备良好的心理素质和抗压能力。
此外,翻译人员的专业素养和语言表达能力也需要不断提升和更新,以适应不断变化的翻译需求。
外文翻译器外文翻译器外文翻译器(Machine Translation)是指使用计算机等技术对外文进行自动翻译的工具。
它利用计算机语言处理、人工智能和语言学等多个领域的知识和技术,将源语言(外文)自动转化为目标语言(母语)的过程。
外文翻译器可以帮助人们快速准确地将外文内容转化为自己熟悉的语言,提高工作效率和信息获取能力。
外文翻译器的研究和发展始于上世纪40年代,最早采用的是基于规则的翻译方法,即根据语法规则和词汇库对源语言进行分析和转换。
然而,这种方法存在很多限制,因为语法和词汇库可能无法覆盖所有的语言特点和用法,导致翻译结果不准确和不流畅。
随着计算机技术和人工智能的发展,神经网络机器翻译(Neural Network Translation)成为外文翻译器的主流方法。
这种方法利用大规模平行语料库训练神经网络模型,通过模仿人类学习语言的方式自动学习源语言和目标语言之间的映射关系。
神经网络机器翻译能够更好地处理语法结构和上下文信息,翻译结果更加准确和自然。
除了神经网络机器翻译,外文翻译器还可以采用统计机器翻译(Statistical Machine Translation)等其他方法。
统计机器翻译利用大量的双语语料进行统计分析,找到最佳的翻译候选,然后根据概率模型对其进行排序和选择。
虽然统计机器翻译在一定程度上改善了翻译质量,但由于依赖于大量的语料库,对于某些语言和领域的翻译效果仍然不理想。
当前外文翻译器的发展已经进入了深度学习时代,融合了自然语言处理、深度学习和人工智能的多种技术手段。
深度学习通过建立多层神经网络模型,能够从大规模语料中自动学习和提取特征,进一步提升了翻译质量和效率。
此外,人工智能的发展还带来了一系列辅助工具,如术语提取、句子结构分析和语音识别等,能够进一步提高翻译的准确性和流畅度。
虽然外文翻译器在很大程度上改善了翻译效率和准确性,但由于语言本身的复杂性和多义性,完全依靠机器翻译仍然存在一些局限性。
毕业设计(论文)外文文献翻译院系:财务与会计学院年级专业:201*级财务管理姓名:学号:132148***附件: 财务风险管理【Abstract】Although financial risk has increased significantly in recent years risk and risk management are not contemporary issues。
The result of increasingly global markets is that risk may originate with events thousands of miles away that have nothing to do with the domestic market。
Information is available instantaneously which means that change and subsequent market reactions occur very quickly。
The economic climate and markets can be affected very quickly by changes in exchange rates interest rates and commodity prices。
Counterparties can rapidly become problematic。
As a result it is important to ensure financial risks are identified and managed appropriately. Preparation is a key component of risk management。
【Key Words】Financial risk,Risk management,YieldsI. Financial risks arising1.1What Is Risk1.1.1The concept of riskRisk provides the basis for opportunity. The terms risk and exposure have subtle differences in their meaning. Risk refers to the probability of loss while exposure is the possibility of loss although they are often used interchangeably。
Agricultural Land and Regulation in the Transition Economy of Russia Ekaterina Gnedenko1 & Michael Kazmin2Published online: 7 July 2015# International Atlantic Economic Society 2015JEL Classification C10 . L33 . O57 . Q00This research note explores the link between farmland conversion and existing land regulation in Russia. We conclude that land regulation is lagging the new market trends in the transition economy of Russia. As market forces continue to penetrate the economy, apparent managerial and statutory problems with regard to local land-use planning and regulation preclude more effective use of land. Responding to the need for attracting investment in agriculture, the Russian Ministry of Science and Education provided funds for our research project that involves primary data collection and econometric analysis of the interdependencies between governmental policies and farmland loss. Our unique dataset contains socioeconomic, demographic and spatialgeographic 2010 data for 39 municipal districts in the Moscow metropolitan region.The econometric analysis of this data set is used to explore the relationship among farmland quantity, its assessed value, the share of privatized farmland, farmland tax,and land-use zoning in the simultaneous equations framework.While the Russian market for real estate has developed quickly, the market for agricultural land is still thin. Farmland deals are limited, partly because of the lingering uncertainty about farmland property rights. The state-owned farmland is still significant. Our Moscow regional data suggest a strong positive relationship between the fraction of privatized farmland and farmland acreage, although the fraction of individually and collectively privatized farmland is only 57 %. The direct sale of farmland to foreigners is prohibited decreasing potential foreign investment as well. As a result, the area occupied by agricultural lands has been steadily decreasing and deteriorating in quality. During the period 1990 to 2005, tillable lands in Russia have shrunk by 10.5 million hectares (7.9 % of tillable lands).Lacking experience and adequate knowledge, local governments are stuck with the land conservation policies available to the former USSR. In particular, in an attempt to contain the loss of prime farmland, the regulators retain old land-use zoning laws prohibiting the change of land status. However, strong development pressures and widespread corruption often annihilate the desirable effect of zoning. The results ofour econometric analysis indicate that the proximity to Moscow city and population growth both have a significant negative effect on the amount of farmland, even in the strictlyzoned-for agriculture districts, suggesting strong urban pressure in the capital region of Moscow. The estimated elasticity of farmland acreage with respect to population growth is −0.3. A corrupt practice of illegal changes in land status is reflected in the fact that the lands still classified as farmland in the Federal Register of Land are turned into residential or industrial areas. This signals a management problem which could be perhaps resolved by the introduction of more flexible zoning and an increase in the range of responsibilities of local governments and their property rights to land.The other economic instrument indispensable in land policy, land assessment, is also based on the former practices of the Communist period following a federally mandated general formula that takes into account soil productivity criteria, topographic features of the landscape, and the presence of irrigation, but still has little in common with the market price of farmland. When the agricultural land tax is calculated as the percentage of the assessed value of farmland, which is often below its real market value, local authorities are not interested in developing local agricultural infrastructure or increasing agricultural land base because they will not be able to reap any significant tax benefits from it. Coupled with the low federally mandated upper limits on tax rates (0.3 % of the assessed value of agricultural and residential lands) this leads to insufficient local tax revenues and overreliance on intergovernmental transfers. According to our data for the Moscow region, although localities tend to impose the maximum allowable tax rate, the average share of land tax revenues in local budgets is a mere 5 %. It is not surprising as the average assessed value of farmland across municipalities is 1000 times less than the ongoing average sales price, according to data we collected.The insignificant local land tax revenues caused by the underestimated land value lead to insufficient local infrastructure investment, which further suppresses the value of farmland and hastens its conversion. The results of the econometric analysis indicate lack of statistical significance between the assessed value of farmland and farmland quantity in the Moscow region, making the farmland tax rate an ineffective instrument in land policy. This missing link between the farmland quantity and existing land policies may render these policies not just ineffective but even wasteful. Innovative approaches such as the retention of development rights by the governmentmight represent a temporary solution. The increasing reliance on local governance in solvinglocal problems would imply improved land-use and public finance planning and,perhaps, a slower farmland conversion trend.俄罗斯经济转型中的农业用地与监管Ekaterina Gnedenko1 & Michael Kazmin2。
外文翻译范例在全球化日益加深的今天,外文翻译的重要性愈发凸显。
无论是学术研究、商务交流,还是文化传播,准确而流畅的外文翻译都起着至关重要的桥梁作用。
下面为大家呈现几个不同领域的外文翻译范例,以帮助大家更好地理解和掌握外文翻译的技巧与要点。
一、科技文献翻译原文:The development of artificial intelligence has brought about revolutionary changes in various fields, such as healthcare, finance, and transportation译文:人工智能的发展给医疗保健、金融和交通运输等各个领域带来了革命性的变化。
在这个范例中,翻译准确地传达了原文的意思。
“artificial intelligence”被准确地翻译为“人工智能”,“revolutionary changes”翻译为“革命性的变化”,“various fields”翻译为“各个领域”,用词准确、贴切,符合科技文献严谨、客观的语言风格。
二、商务合同翻译原文:This Agreement shall commence on the effective date and shall continue in force for a period of five years, unless earlier terminated in accordance with the provisions herein译文:本协议自生效日起生效,并将持续有效五年,除非根据本协议的规定提前终止。
商务合同的翻译需要格外注重准确性和专业性。
上述译文中,“commence”翻译为“生效”,“in force”翻译为“有效”,“terminated”翻译为“终止”,清晰准确地表达了合同条款的含义,避免了可能的歧义。
三、文学作品翻译原文:The sun was setting, painting the sky with hues of orange and pink, as if nature were a master artist at work译文:太阳正在西沉,把天空涂成了橙色和粉色,仿佛大自然是一位正在创作的艺术大师。
毕业论文的外文翻译在完成毕业论文时,外文翻译是一个重要的环节。
通过对外文文献的翻译,我们可以获取更多的研究信息和视野,为毕业论文的写作提供有力的支持。
然而,外文翻译可能面临一些困难和挑战。
本文将探讨毕业论文的外文翻译问题,并提供一些建议和技巧,以便更好地完成这项任务。
一、外文翻译的挑战与困难1. 语言障碍:毕业论文常涉及专业性较强的知识领域,外文文献中常包含大量专业术语和复杂句式,语言难度较高。
对于非英语专业的学生来说,面对外文文献的翻译可能会遇到一些困难。
2. 文化差异:不同国家和地区的学术界对于问题的研究角度、方法以及表达方式可能存在差异,翻译时需要了解并妥善处理这些文化差异。
3. 原文表达问题:外文文献中可能存在语义模糊、句意混乱或篇章结构复杂等问题,译者需要理解原文的意思并找到合适的翻译方式。
二、毕业论文外文翻译的方法与技巧1. 熟悉背景知识:在进行外文翻译之前,要先对所研究的领域进行充分了解和阅读,熟悉常见的术语和理论框架,提高翻译的准确性和连贯性。
2. 通过多种途径获取资料:除了查阅相关的外文文献,还可以通过学术数据库、专业期刊和学术社区等获取更多的翻译参考资料。
3. 注意审视文本:在翻译过程中,要仔细审视原文,并理解作者的意图和表达方式。
对于一些存在歧义的句子或术语,可以通过查阅其他资料或与同行交流来进行准确的翻译。
4. 日常积累与翻译软件的使用:通过积累英文词汇量和阅读经验,增强对外文翻译的灵活运用。
同时,在需要的时候可以借助翻译软件进行辅助翻译,但需要注意避免直接将翻译软件的结果作为最终翻译。
5. 注意文化差异:在进行外文翻译时,要注意不同文化背景下的表达差异。
对于无法准确翻译的文化特定词汇或短语,可以使用括号注释或提供解释等方式进行说明。
三、毕业论文外文翻译的注意事项1. 保持准确性:翻译过程中要保持准确性,尽可能地忠实表达原文的意思,不要随意增加或删除信息。
另外,要根据具体的学术规范和格式要求进行文献引用和注释。
外文资料原文涂敏之会计学 8051208076Title:Future of SME finance(c)Background – the environment for SME finance has changedFuture economic recovery will depend on the possibility of Crafts, Trades and SMEs to exploit their potential for growth and employment creation.SMEs make a major contribution to growth and employment in the EU and are at the heart of the Lisbon Strategy, whose main objective is to turn Europe into the most competitive and dynamic knowledge-based economy in the world. However, the ability of SMEs to grow depends highly on their potential to invest in restructuring, innovation and qualification. All of these investments need capital and therefore access to finance.Against this background the consistently repeated complaint of SMEs about their problems regarding access to finance is a highly relevant constraint that endangers the economic recovery of Europe.Changes in the finance sector influence the behavior of credit institutes towards Crafts, Trades and SMEs. Recent and ongoing developments in the banking sector add to the concerns of SMEs and will further endanger their access to finance. The main changes in the banking sector which influence SME finance are:•Globalization and internationalization have increased the competition and the profit orientation in the sector;•worsening of the economic situations in some institutes (burst of the ITC bubble, insolvencies) strengthen the focus on profitability further;•Mergers and restructuring created larger structures and many local branches, which had direct and personalized contacts with small enterprises, were closed;•up-coming implementation of new capital adequacy rules (Basel II) will also change SME business of the credit sector and will increase its administrative costs;•Stricter interpretation of State-Aide Rules by the European Commission eliminates the support of banks by public guarantees; many of the effected banks are very active in SME finance.All these changes result in a higher sensitivity for risks and profits in the financesector.The changes in the finance sector affect the accessibility of SMEs to finance.Higher risk awareness in the credit sector, a stronger focus on profitability and the ongoing restructuring in the finance sector change the framework for SME finance and influence the accessibility of SMEs to finance. The most important changes are: •In order to make the higher risk awareness operational, the credit sector introduces new rating systems and instruments for credit scoring;•Risk assessment of SMEs by banks will force the enterprises to present more and better quality information on their businesses;•Banks will try to pass through their additional costs for implementing and running the new capital regulations (Basel II) to their business clients;•due to the increase of competition on interest rates, the bank sector demands more and higher fees for its services (administration of accounts, payments systems, etc.), which are not only additional costs for SMEs but also limit their liquidity;•Small enterprises will lose their personal relationship with decision-makers in local branches –the credit application process will become more formal and anonymous and will probably lose longer;•the credit sector will lose more and more i ts “public function” to provide access to finance for a wide range of economic actors, which it has in a number of countries, in order to support and facilitate economic growth; the profitability of lending becomes the main focus of private credit institutions.All of these developments will make access to finance for SMEs even more difficult and / or will increase the cost of external finance. Business start-ups and SMEs, which want to enter new markets, may especially suffer from shortages regarding finance. A European Code of Conduct between Banks and SMEs would have allowed at least more transparency in the relations between Banks and SMEs and UEAPME regrets that the bank sector was not able to agree on such a commitment.Towards an encompassing policy approach to improve the access of Crafts, Trades and SMEs to financeAll analyses show that credits and loans will stay the main source of finance for the SME sector in Europe. Access to finance was always a main concern for SMEs, but the recent developments in the finance sector worsen the situation even more.Shortage of finance is already a relevant factor, which hinders economic recovery in Europe. Many SMEs are not able to finance their needs for investment.Therefore, UEAPME expects the new European Commission and the new European Parliament to strengthen their efforts to improve the framework conditions for SME finance. Europe’s Crafts, Trades and SMEs ask for an encompassing policy approach, which includes not only the conditions for SMEs’ access to l ending, but will also strengthen their capacity for internal finance and their access to external risk capital.From UEAPME’s point of view such an encompassing approach should be based on three guiding principles:•Risk-sharing between private investors, financial institutes, SMEs and public sector;•Increase of transparency of SMEs towards their external investors and lenders;•improving the regulatory environment for SME finance.Based on these principles and against the background of the changing environment for SME finance, UEAPME proposes policy measures in the following areas:1. New Capital Requirement Directive: SME friendly implementation of Basel IIDue to intensive lobbying activities, UEAPME, together with other Business Associations in Europe, has achieved some improvements in favour of SMEs regarding the new Basel Agreement on regulatory capital (Basel II). The final agreement from the Basel Committee contains a much more realistic approach toward the real risk situation of SME lending for the finance market and will allow the necessary room for adaptations, which respect the different regional traditions and institutional structures.However, the new regulatory system will influence the relations between Banks and SMEs and it will depend very much on the way it will be implemented into European law, whether Basel II becomes burdensome for SMEs and if it will reduce access to finance for them.The new Capital Accord form the Basel Committee gives the financial market authorities and herewith the European Institutions, a lot of flexibility. In about 70 areas they have room to adapt the Accord to their specific needs when implementing itinto EU law. Some of them will have important effects on the costs and the accessibility of finance for SMEs.UEAPME expects therefore from the new European Commission and the new European Parliament:•The implementation of the new Capital Requirement Directive will be costly for the Finance Sector (up to 30 Billion Euro till 2006) and its clients will have to pay for it. Therefore, the implementation – especially for smaller banks, which are often very active in SME finance –has to be carried out with as little administrative burdensome as possible (reporting obligations, statistics, etc.).•The European Regulators must recognize traditional instruments for collaterals (guarantees, etc.) as far as possible.•The European Commission and later the Member States should take over the recommendations from the European Parliament with regard to granularity, access to retail portfolio, maturity, partial use, adaptation of thresholds, etc., which will ease the burden on SME finance.2. SMEs need transparent rating proceduresDue to higher risk awareness of the finance sector and the needs of Basel II, many SMEs will be confronted for the first time with internal rating procedures or credit scoring systems by their banks. The bank will require more and better quality information from their clients and will assess them in a new way. Both up-coming developments are already causing increasing uncertainty amongst SMEs.In order to reduce this uncertainty and to allow SMEs to understand the principles of the new risk assessment, UEAPME demands transparent rating procedures –rating procedures may not become a “Black Box” for SMEs: •The bank should communicate the relevant criteria affecting the rating of SMEs.•The bank should inform SMEs about its assessment in order to allow SMEs to improve.The negotiations on a European Code of Conduct between Banks and SMEs , which would have included a self-commitment for transparent rating procedures by Banks, failed. Therefore, UEAPME expects from the new European Commission and the new European Parliament support for:•binding rules in the framework of the new Capital Adequacy Directive,which ensure the transparency of rating procedures and credit scoring systems for SMEs;•Elaboration of national Codes of Conduct in order to improve the relations between Banks and SMEs and to support the adaptation of SMEs to the new financial environment.3. SMEs need an extension of credit guarantee systems with a special focus on Micro-LendingBusiness start-ups, the transfer of businesses and innovative fast growth SMEs also depended in the past very often on public support to get access to finance. Increasing risk awareness by banks and the stricter interpretation of State Aid Rules will further increase the need for public support.Already now, there are credit guarantee schemes in many countries on the limit of their capacity and too many investment projects cannot be realized by SMEs.Experiences show that Public money, spent for supporting credit guarantees systems, is a very efficient instrument and has a much higher multiplying effect than other instruments. One Euro form the European Investment Funds can stimulate 30 Euro investments in SMEs (for venture capital funds the relation is only 1:2).Therefore, UEAPME expects the new European Commission and the new European Parliament to support:•The extension of funds for national credit guarantees schemes in the framework of the new Multi-Annual Programmed for Enterprises;•The development of new instruments for securitizations of SME portfolios;•The recognition of existing and well functioning credit guarantees schemes as collateral;•More flexibility within the European Instruments, because of national differences in the situation of SME finance;•The development of credit guarantees schemes in the new Member States;•The development of an SBIC-like scheme in the Member States to close the equity gap (0.2 – 2.5 Mio Euro, according to the expert meeting on PACE on April 27 in Luxemburg).•the development of a financial support scheme to encourage the internalizations of SMEs (currently there is no scheme available at EU level: termination of JOP, fading out of JEV).4. SMEs need company and income taxation systems, whichstrengthen their capacity for self-financingMany EU Member States have company and income taxation systems with negative incentives to build-up capital within the company by re-investing their profits. This is especially true for companies, which have to pay income taxes. Already in the past tax-regimes was one of the reasons for the higher dependence of Europe’s SMEs on bank lending. In future, the result of rating w ill also depend on the amount of capital in the company; the high dependence on lending will influence the access to lending. This is a vicious cycle, which has to be broken.Even though company and income taxation falls under the competence of Member States, UEAPME asks the new European Commission and the new European Parliament to publicly support tax-reforms, which will strengthen the capacity of Crafts, Trades and SME for self-financing. Thereby, a special focus on non-corporate companies is needed.5. Risk Capital – equity financingExternal equity financing does not have a real tradition in the SME sector. On the one hand, small enterprises and family business in general have traditionally not been very open towards external equity financing and are not used to informing transparently about their business.On the other hand, many investors of venture capital and similar forms of equity finance are very reluctant regarding investing their funds in smaller companies, which is more costly than investing bigger amounts in larger companies. Furthermore it is much more difficult to set out of such investments in smaller companies.Even though equity financing will never become the main source of financing for SMEs, it is an important instrument for highly innovative start-ups and fast growing companies and it has therefore to be further developed. UEAPME sees three pillars for such an approach where policy support is needed:Availability of venture capital•The Member States should review their taxation systems in order to create incentives to invest private money in all forms of venture capital.•Guarantee instruments for equity financing should be further developed.Improve the conditions for investing venture capital into SMEs•The development of secondary markets for venture capital investments in SMEs should be supported.•Accounting Standards for SMEs should be revised in order to easetransparent exchange of information between investor and owner-manager.Owner-managers must become more aware about the need for transparency towards investors•SME owners will have to realise that in future access to external finance (venture capital or lending) will depend much more on a transparent and open exchange of information about the situation and the perspectives of their companies.•In order to fulfil the new needs for transparency, SMEs will have to use new information instruments (business plans, financial reporting, etc.) and new management instruments (risk-management, financial management, etc.).外文资料翻译涂敏之会计学 8051208076题目:未来的中小企业融资背景:中小企业融资已经改变未来的经济复苏将取决于能否工艺品,贸易和中小企业利用其潜在的增长和创造就业。
IntroductionLatvian legislation for forest protection belts Latvian legislation demands that forest protection belts are established around all cities and towns. The concept of protection belts originates from the Soviet Era and is maintained in Latvian legislation despite the radical changes to the political system after regaining indepen-dence in 1991. The legal background for the establish-ment of protection belts is as follows:•Law on Protection Belts (1997, 2002)•Forest Law (2000)•Law on Planning of Territorial Development (1998).Designating a greenbelt around the city of Riga, LatviaJanis DonisLatvian State Forestry Research Institute ‘Silava’, Salaspils, LatviaAbstract: Latvian legislation demands that forest protection belts are established around all cities and towns. The main goal of a protection belt is to provide suitable opportuni-ties for recreation to urban dwellers and to minimise any negative impacts caused by urban areas on the surrounding environment. Legislation states the main principles to be adopted, which include the maximum area of protection belts, their integration in terri-torial development plans and restrictions placed on forest management activities. The largest part of the forest area around Riga is owned by the municipality of Riga, which, as a result, has two competing interests: to satisfy the recreational needs of the inhabitants of Riga, and to maximise the income from its property. In order to compile sufficient background information to solve this problem, the Board of Forests of Riga Municipality initiated the preparation of a proposal for the designation of a new protection belt.The proposal was based on the development and application of a theoretical framework developed during the 1980s. The analysis of the recreational value of the forest (5 class-es of attractiveness) was carried out based on categories of forest type, dominant tree species, dominant age, stand density, distance from urban areas and the presence of at-tractive objects. Information was derived from forest inventory databases, digital forest maps and topographic maps. Additional information was digitised and processed using ArcView GIS 3.2. Local foresters were asked about the recreation factors unique to differ-ent locations, such as the number of visitors and the main recreation activities. From a recreational point of view and taking into account legal restrictions and development plans for the Riga region, it was proposed to create three types of zones in the forest: a protection belt, visually sensitive areas and non-restricted areas.Key words:greenbelt forest, recreational value, GIS, zoningThe Law on Protection Belts states that protection belts around cities (with forests as part of a green zone)have to be established (a) to provide suitable conditions for recreation and the improvement of the health of urban dwellers, and (b) to minimise the negative im-pact of urban areas on the surrounding environment.Urban For.Urban Green.2 (2003):031–0391618-8667/03/02/01-031 $ 15.00/0Address for correspondence:Latvian State Forestry Re-search Institute ‘Silava’, Rı¯gas iela 111, Salaspils, LV-2169,Latvia. E-mail: donis@silava.lv© Urban & Fischer Verlaghttp://www.urbanfischer.de/journals/ufugRegulation nr 263 (19.06.2001) on the ‘Methodology for the establishment of forest protection belts around towns’issued by the Cabinet of Ministers (CM) states: (a) The area of a protection belt depends on the numberof inhabitants in the town: towns with up to 10,000 inhabitants should have a maximum of 100 ha of protection belt, those with between 10,000 and 100,000 inhabitants a maximum of 1,500 ha, and towns with more than 100,000 inhabitants a maxi-mum of 15,000 ha;(b) the borders of protection belts have to be able to beidentifiable on the ground, using features such as roads, ditches, power lines, and so forth;(c) protection belts have to be recorded in the territorialplans of regions adjacent to the town or city; and (d) establishment of protection belts has to be agreedupon by local municipalities.According to law, protection belts should be man-aged using adapted silvicultural measures. Clear-cut-ting, for example, is prohibited in a protection belt to mitigate any negative impacts of the city on the sur-rounding environment. The Forest Law of 2000 and subsequent regulations including the Regulation on Cutting of Trees, and the Regulation on Nature Conser-vation in Forestry define clear-cuts as felled areas larg-er than 0.1 ha where the basal area is reduced below a critical level in one year. These regulations also state the permitted intensity and periodicity of selective cut-ting (30–50%, at least 5 years between entries).The third element of the legal framework relevant for protection belts in Latvia is the Law on Planning of Territorial Development (1998). It defines:(a) Principles and responsibilities of the different or-ganisations involved;(b) the contents of territorial plans;(c) the procedures for public hearing; and(d) the procedures for the acceptance of plans.The law also states that protection belts around towns have to be designated in territorial plans. Thus, the legislation gives very detailed descriptions of the restrictions to maximum area, activities and guidelines for delineation and so forth, while there are no ‘rules’for the choice of what areas are to be included in pro-tection belts. It is up to territorial planners to propose what areas to include and for negotiation among mu-nicipalities to approve the selection.Protection belt for the city of RigaRiga and the Riga region are situated in the Coastal Lowland of Latvia within the Gulf of Riga. The main landform types are the Baltic Ice Lake plain, the Litto-rina Sea plain and the Limnoglacial plain and bog plain. The total area of the administrative area of the City of Riga covers 307.2 km2, and that of the Riga re-gion 3,059 km2. In 2000 the city of Riga had 815,000 inhabitants, while an additional 145,000 people resided in the greater Riga region. During the last decade the number of inhabitants in Riga decreased by 10.5%and in Riga region by 5.3%. In the mid-1990s the main types of industry in Riga were food processing, timber and wood processing, metal fabricating and engineer-ing, while in the region agriculture and forestry, wood processing, pharmaceuticals, and the power industry were the main activities. Due to reduced industrial ac-tivities today, the main sources of pollution in Riga re-gion are road transport and households.The greater part of the Riga region is covered by for-est, i.e. 1,642 km2or 53%. About 26% of the land is used for agriculture, 4% is covered by bogs, and 4% by water. The Riga region also has a coastal dune zone of some 30 km along the Gulf of Riga. The main tree species to be found in the Riga region are Scots pine (Pinus sylvestris L.),birch (Betula spp.) and Norway spruce (Picea abies (L.) Karsten) (see Table 1). In the administrative area of the city of Riga, 57 km2 or about 19% of the land area is forest. Scots pine is the domi-nant species, covering approx. 46.9 km2(i.e. 88% of the total forest area).According to the legislation described before, a pro-tection belt around Riga city, with a maximum size of 15,000 ha, could be designated. Moreover, any propos-al has to be agreed upon among 24 local municipalities. The Riga region is divided into 24 administrative units: 7 towns and 17 pagasts or ‘parishes’.Riga municipality currently owns more than 55,600 ha of forests. Most are situated in the vicinity of Riga. Four forest administrative districts lie completely with-in Riga region and close to Riga city (see Fig. 1). The total area of these districts is 44,158 ha out of which forest stands cover 36,064 ha (82%). Thus the Riga municipality forests of those 4 districts cover only 17% of the total forest area of the Region. The dominant tree species in the municipally owned forests are Scots32J.Donis:Designating a greenbelt around the city of Riga,LatviaUrban For.Urban Green.2 (2003)Table 1.Tree species composition in the Riga region Dominant tree Area covered, ha Average age, years species––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––Total Municipa-Total Municipa-lity*lity* Scots pine95,27627,3718581 Norway spruce20,8493,0175139Birch30,5585,1246056 Other10,438552––Total157,12136,0647369*Data only for the 4 forest districts of the Riga city munici-pality that are entirely situated within the Riga region.pine, birch and Norway spruce. These cover 76%, re-spectively 14% and 8% of the forest area. Other species cover less than 2% of the area.Until the re-establishment of Latvian independence almost all forestland was owned by the state but since then many areas have been returned to their former owners and are now privately owned. Current regula-tions state that until the designation of new boundaries for protection belts has been agreed upon, all forests of the previously existing and protected green zone have to remain protected whatever their functional role or ownership status. Consequently almost all forests of the Riga municipality located in the Riga region have management restrictions placed on them, and the same can be said for forests of other owners within the previ-ously existing green zone. Currently, therefore, on the one hand significant recreation opportunities for urban dwellers are provided, while on the other hand forest owners’rights to obtain income from timber harvest in the suburban areas continue to be restricted. Suburban municipalities also lose income because of reduced land taxes from land with management restrictions.The board of Forests of the Municipality of Riga there-fore initiated the preparation of a proposal to designate a new protection belt.Study to support protection belt designation The main objective of the study presented here has been to obtain background information in preparation for further discussions with local municipalities. Stud-ies in Latvia as well as elsewhere have revealed that recreational values of forests depend mainly on forest characteristics, location and level of pollution (Emsis et al. 1979; Emsis 1989; Holgen et al. 2000; Lindhagen & Hörnsten 2000; Rieps ˇas 1994; Su ¯na 1973, 1979). A very important aspect is the distance to the forest from places where people live (e.g. Rieps ˇas 1994). The abil-ity of a forest stand to purify the air by filtering or ab-sorbing dust, micro-organisms, and noxious gases de-pends on tree and shrub species composition, age, tree size and stand density (Emsis 1989). Stands purify the air most effectively at the time of maximum current an-nual volume increment, usually between 30 to 60 years of age in Latvian conditions, depending on species.Recreational value, on the other hand, increases with age (and tree size) and reaches its maximum consider-ably later. Taking into account the peculiarities of the dispersal of pollution as described by Laivin ‚s ˇ et al.(1993) and Za ¯lı¯tis (1993), selective cutting is prefer-able in the vicinity of a pollution source, especially ifJ.Donis:Designating a greenbelt around the city of Riga,Latvia 33Urban For.Urban Green.2 (2003)Fig. 1.Location ofthe Riga municipali-ty forests in the Riga region.the forest consists of a narrow strip between the pollu-tion source and housing. If the distance between a pol-lution source and housing exceeds several kilometres, a patch clear-cut system with stands of different ages is sufficient to provide a reduction in the negative impact of urban areas. Taking into account the fact that closer to residential areas it is more important to consider the visual qualities of the forest (e.g. Tyrväinen et al. 2003), this purification ability can generally be ignored when planning protection belts.MethodsThis study to support the designating of the Riga pro-tection belt used the following data sources for analysis (see Fig. 2): forest inventory databases, digital forest maps of the Riga municipal forests which are situated outside the administrative borders of the city (55,600 ha of which 44,158 ha located in the Riga region) (see Fig. 1), and corresponding topographic maps.The study and its developed proposal are based on an application of a theoretical approach developed during the 1980s by the Latvian State Forestry Research Insti-tute ‘Silava’(Emsis 1989) and the Lithuanian Forestry Research Institute (Riepsˇas 1994). According to the methodology developed by Emsis (1989), the first step in the process is to evaluate the recreational potential of the forest stands. This is carried out by analysing the following factors:• The tolerance of the forest ecosystem to different lev-els of anthropogenic (recreation) loading;• the status of forest ecosystems in terms of the damage or degradation as a result of recreational use;•the suitability of the landscape for non-utilitarian recreation (recreational value); and• the existing and potential levels of recreational loads.The second step involves evaluating the existing andexpected functional roles of the forest.The tolerance of the forest ecosystem to different levels of anthropogenic impact or loading is evaluated using a framework based on a combination of forest type, dominant tree species, dominant age group, soil type and relief, according to the stability of ecosystem. All stands are classified into one of five tolerance classes. The highest score is given to mature deciduous forests on mesotrophic and mesic soils on flat topogra-phy, while the lowest score is given to young pine stands on oligotrophic soils on steep slopes (forests on dunes).In this study ecosystem tolerance could not be evalu-ated, as it was primarily a desk using existing databas-es, and topographic relief maps were not available in digital form. The status of the forest ecosystem in rela-tion to damage or degradation was evaluated in terms of the degree of change in vegetation cover, under-growth, tree root exposure of the and level of littering, classified into three classes.Assessment of the recreational value of the forest stands was calculated using a formula developed by Riepsˇas (1994):Recreational value VR= (VS*kW*kS+VA)*kPWhere VSis stand suitability based on key internal at-tributes of the stand, such as species, age, stand densityand forest type. VSvalues range from 0 for young, high-density grey alder (Alnus incana L.) on wet peat soils, to 100 for average density mature pine stands ondry mineral soils. kwis a coefficient depending on the distance of the stand from watercourses, ranging from0.1 for stands further than 2 km from watercourses to1.0 for stands up to 500 m from watercourses. kSis a coefficient depending on the distance of the stand from urban areas, ranging from 0.1 for stands further than34J.Donis:Designating a greenbelt around the city of Riga,LatviaUrban For.Urban Green.2 (2003)Fig. 2.Structure of data sources used in data ana-lysis.80 km from Riga to 1.0 for stands within 30 km ofRiga. VA is an additional value depending on the pres-ence of attractive features, for example, 25 for forest stands up to 500 m from settlements, including summer cottages, or for areas intensively used for recreation ac-cording to information of local foresters. kP is a coeffi-cient depending on the level of environmental pollu-tion. Its value is 0 if the actual pollution level exceeds limit values, 0.5 if the level of environment pollution is between 50% and 100% of limit values, and 1 if the level of actual pollution is less than 50% of the limit values. In this study a coefficient of 1.0 was used, be-cause SO2and O3concentrations measured by Rigabackground measuring stations did not exceed 50% of the limit values (Fammler et al. 2000).The division of stands into classes of stand suitabili-ty is based on studies of visitors’preferences. Coeffi-cients kw, ksand VAare based on visitors’spatial distri-bution and show the ratio of the number of visitors in different zones. The evaluation of existing and expect-ed recreational loads was carried out by local foresters. They marked existing and potential recreation places on forest maps, including:•Small areas or sites for activities such as swimming, barbecuing, and so forth.•Recreation territories, defined as areas of 20 ha or more where people stay longer periods for walking, jogging, skiing or other forms of both active and pas-sive recreation.•Traditionally popular places for the collection of berries and mushrooms.•Recreational routes, including routes from public transport stops to recreation sites or recreation terri-tories, and between recreation sites and territories. For each recreation site and recreation territory data on the main seasons of use, the periods of use (week-days, weekends), and the average number of people in ‘rush-hours’during good weather conditions was col-lected or estimated.Data processing was carried out using ArcView GIS3.2a, Visual Fox pro and Microsoft Excel. VS values foreach stand were calculated from information in the for-est database using Visual Fox pro. Information collect-ed at a later stage from local foresters was digitised using separate themes (layers) in ArcView GIS 3.2a. Buffer zones along watercourses and water bodies, as well as residential areas, recreation sites and territoriesand recreation routes were created to get kW ,kSand VAvalues for each stand. Then VR values were calculatedfor each stand.A selection of recreation sites and territories was vis-ited by members of the project team in order to evalu-ate the state of the ecosystem with respect to wear and tear arising from different levels of recreational use. An evaluation of the existing functional role of each forest stand was carried out using the existing categories offorest protection. The anticipated future functional role was evaluated by annalysing the recreational value of stands, known expectations in terms of territorial de-velopment, and existing legal restrictions in order to find a compromise between recreation possibilities and other services of the forest. Next, a first draft of the protection belt was drawn according to experts’judge-ment. This draft included forests with high recreational value adjacent to residential areas and summer cot-tages, and larger tracts intensively used for recreation with medium to high recreational value.ResultsAccording to the original forest classification 65% of the total forest land area was designated as a commer-cial greenbelt forest, for which the main management goals are timber production and environmental consid-erations. The remaining 35% were designated as pro-tected (see Table 2). With regards to protected areas in Latvia: the main management goals of nature parks are nature conservation and recreation, including some ed-ucation. The goal for nature reserves is nature conser-vation, while that of the protected greenbelt forests is recreation.While interviewing local foresters it was revealed that they find it difficult to evaluate dispersed recreation loads (for example collection of berries, mushrooms). The assessments of foresters varied greatly and were considered to be unreliable. It was therefore decided to map only the places important for recreation, but not to use the inaccurate estimates of visitor numbers.In Latvia, special investigations have to be carried out in order to develop management objectives and principles for protected forests as part of the preparation of management plans. Pilot studies and visits to some of the recreation areas have revealed that the evaluation of the state of the forest ecosystem is useful only when de-veloping the detailed management plan. Even then, this is only the case for places identified by local foresters as recreation sites or territories, because otherwise it is too time consuming to carry out fieldwork which provides little useful additional information.Calculated VSvalues show that on average the forests studied have a medium suitability value for recreation (average score 47) (see Table 2). There are considerable differences between districts, with aver-age value ranging from 32 points in Olaine to 66 points in the Garkalne district. This indicates that the average stands in the Garkalne district are more suitable for recreation than those in other districts. If other aspects are taken into account, such as distance from wherepeople live, and VRvalues are calculated it can be seenJ.Donis:Designating a greenbelt around the city of Riga,Latvia35Urban For.Urban Green.2 (2003)that the districts are still ranked as follows: Garkalne,Jugla, Tireli and Olaine.Only 10% of the forest owned by Riga municipality within the Riga region were evaluated as having a high or very high recreational value. 12% had medium recreational value, while large areas used for the col-lection of berries and mushrooms were evaluated as having low or very low recreational value (60% of the total forest area) (see Table 3).More than 16% of the area is covered by bogs, for which according to the used methodology, recreational value was not evaluated at all. Some areas were recorded by the local foresters as important places for the collec-tion of berries. However, more valuable from a recre-ational point of view were those forests situated east and north-east of the city (Garkalne and Jugla districts),while the forests to the south (Olaine and Tireli districts)were found to have a lower recreational value (V R ).36J.Donis:Designating a greenbelt around the city of Riga,LatviaUrban For.Urban Green.2 (2003)Table 2.Distribution of forest by forest categories according to the original functional role Forest districtDataFormer forest category Total–––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––Commercial Nature Nature Protected greenbelt forests parks reserves greenbelt forestsGarkalneArea, ha521.27,698.78,219.9Average of V S *61.966.566.2Average of V R **59.350.751.4JuglaArea, ha 8,376.74,098.812,475.4Average of V S 45.656.949.1Average of V R 22.034.025.7OlaineArea, ha 11,765.4707.512,473.0Average of V S 31.941.032.6Average of V R 8.527.410.0TireliArea, ha 8,689.5257.91,025.01,016.910,989.3Average of V S 40.666.710.059.342.3Average of V R 17.055.3 1.044.920.6TotalArea, ha 28,831.6779.11,025.013,522.044,157.6Average of V S 39.863.510.061.647.1Average of V R16.357.91.043.725.9* V S Suitability value – based on stand parameters (0–100 points).** V R Recreation value (0–125 points) based on stand parameters, distance to the residential areas, water and other attractive objects.Table 3.Distribution of forest areas by classes of attractiveness and by designated functional role Designated zoneDataClass of attractiveness Total –––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––n.a.Very low Low Medium High Very high 0<2525,1–5051–7575–100100<Protection belt Area, ha76.7560.12,266.42,222.7850.5743.66719.9Average of V R *0.012.036.063.390.0125.053.4Visually sensitive Area, ha 447.64,150.54,157.7853.4847.1179.810636.1Average of V R 0.07.837.460.996.7125.028.5Non-restricted Area, ha 6,664.715,389.12,548.61,090.5874.8234.026801.7Average of V R 0.0 5.234.761.197.2125.015.8TotalArea, ha 7,189.020,099.88,972.74,166.52,572.31,157.344157.6Average of V R0.06.236.362.294.6125.025.9*V R Recreation value (0–125 points) based on stand parameters, distance to the residential areas, water and other attractive objects.Areas along main roads and railways are known to be visually sensitive, because of the large number of peo-ple who can see them during travel. The same is true for forest in the vicinity of small villages. Taking into ac-count the fact that legislation prohibits clear-cuts in pro-tection belts – which is not always necessary in order to maintain the visual quality of the landscape – it was proposed, as part of the zoning strategy, to create so called visually sensitive areas. In these areas the forest owner (Riga municipality) is recommended to use more detailed landscape-planning techniques and to pay more attention to visual aspects during management.As a result of the study, seen from a recreational point of view and taking into account legal restrictions and so forth, it has been proposed to create three zoning categories: (1) protection belts, (2) visually-sensitive areas, and (3) non-restricted areas (see Fig. 3). The protection belt should include:• Forest with high recreational value adjacent to residen-tial areas and summer cottages, to form a 200–500 m wide belt.• Larger tracts of forestland intensively used for recre-ation.The zone of visually-sensitive areas should include:• Forests within the administrative borders of Riga mu-nicipality and in the vicinity of villages (up to 200–500 m distance).• Forests along roads of national and regional impor-tance, railways, watercourses and streams as a protec-tion belt of 100–300 m wide.• Places used for mushroom and berry collection in the original restricted protection belt.• Places that could become important for recreation in the near future.J.Donis:Designating a greenbelt around the city of Riga,Latvia 37Urban For.Urban Green.2 (2003)Table 4.Proposed distribution of forest categories in designated zones (in hectares)Designated zoneFormer forest category Grand Total––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––––Commercial Nature Nature Protected greenbelt forests parks reserves greenbelt forests Protection belt355.2779.15,585.76,719.9Visually sensitive areas 3,503.97,132.110,636.1Non-restricted areas 24,972.51,025.0*804.226,801.7Total 28,831.6779.11,025.013,522.044,157.6*Forests within nature reserves are not intended for recreation; their primary management goal is nature conservation.Fig. 3.Proposal for zon-ing of the Riga municipalforests in Riga region.The remaining areas should consequently be classi-fied as non-restricted areas.A revision of the first draft plan was made taking into account the known prospective development plans of Riga and Riga region. As a result, for forests owned by Riga municipality and located in Riga region the pro-posal is to include 6,720 ha in the protection belt (see Table 3). Moreover, it has been suggested to designate 10,636 ha as visually-sensitive areas, but to omit the re-maining 26,802 ha from zoning, as these do not need special management from a recreation point of view. Average recreational values of stands in this area range from 53 (medium), through 28 (low) to 15 points (very low) respectively.As a result, the major part of the forest remains in the same functional category as in the original allocation (see Table 4). As was mentioned above, the classifica-tion described here is only based on recreational as-pects, thus forests in nature reserves are misleadingly shown as non-restricted forests. Only 5,586 ha out of the 13,500 thousand ha of the originally protected greenbelt forests are proposed to be included in the protection belt, while 355 ha of the previous commer-cial greenbelt forests are proposed to be placed under stronger protection.DiscussionForests owned by Riga municipality within the Riga re-gion are divided over 13 rural municipalities. Accord-ing to legislation, revised draft proposals for zoning Riga city forests have to be accepted by Riga munici-pality, while the final decision is up to Riga and the sur-rounding municipalities. The study presented here has provided a tentative estimate of the recreational value and suitability of the forests for recreation and can be used as a starting point for political discussions. At the very beginning the intention was to divide the forests in two categories: the protection belt and the remainder of the forest. During the study it was concluded, however, that a third category would be needed, that of visually sensitive areas. Within this category more attention would have to be paid to the amenity of the landscape, but there would be no need to drastically restrict com-mercial forest management. As nature parks are also designated for recreation, it has been proposed to in-clude all forests of nature parks in the protection belt. It has to be noted that all the forests within the adminis-trative borders of cities, and as such not included in this study, are designated as protected. As a consequence, the forest area available for recreation to the inhabi-tants of Riga would increase to 12,500 ha.Unlike many other European cities, where timber ex-traction is of small importance (Konijnendijk 1999),Riga municipal forests have a considerable economic role. It is estimated that the allowable annual cut in suburban forests amounts to 169,800 m3or 81% of the annual increment (Dubrovskis et al. 2002). It should be kept in mind that income from logging is used for for-est regeneration and tending, forest fire protection and maintenance of recreation facilities.The objective of this study was not to evaluate the precision of the method nor possible errors occurring when applying it. This study revealed, however, the in-completeness of the methodology used. Bogs, which are very sensitive to recreation loads, are ascribed quite a high level of attractiveness from a recreation point of view (for the collection of wild berries), but according to the methodology they are not evaluated at all. All watercourses were assumed to be attractive sites, while the preliminary evaluation of recreation loads showed this not to be true. The use of watercourses is very vari-able and obviously depends on water quality and vege-tation structure of the edges or banks. Another aspect which was not taken into account was that amenity of a forest is not simply the sum of the amenity values of forest stands (Pukkala et al. 1995).It seems that the evaluation based on dominant species is appropriate for screening areas, but for more detailed management plans, species mixture, the number of forest layers, and principles of landscape architecture also have to be taken into account (Bell 1999; Bell & Nikodemus 2000). Various studies have shown that people prefer uneven-aged forests (e.g. Melluma et al. 1982) and uneven-aged stands (e.g. Riepsˇas 1994). The impacts of the screening effect show that there are, even in the visually-sensitive and commercial zones, considerable areas with high and very high recreational value. This is mainly because delineation of zonal boundaries is carried out using easily distinguishable natural lines, and often it is not worth including single stands of high recreational value in the protection belt if, as a consequence, re-strictions on management would be placed over whole compartments of 50 ha.For the preparation of specific management guide-lines detailed field inventories have to be carried out. This has not been done in this study, where more re-liance was placed on the experience of local foresters and existing databases. Detailed economical calcula-tions have yet to be carried out in order to evaluate the direct and indirect value of the forest. These will also assist in obtaining more background information to be used as part of a holistic approach and for development of a decision support system to resolve contradictions between different interest groups.After acceptance of the draft plan by the municipali-ty of Riga, the process of negotiation between Riga and its surrounding municipalities is currently ongoing.38J.Donis:Designating a greenbelt around the city of Riga,Latvia Urban For.Urban Green.2 (2003)。
外文期刊翻译Translation of a Foreign Journal Article (700 words)Title: The Impact of Climate Change on Biodiversity ConservationIntroduction:Climate change is often considered one of the greatest threats to biodiversity worldwide. As the global temperature rises, the natural habitats of many species are being disrupted, which can lead to the loss of biodiversity. In this article, we will explore the various ways in which climate change impacts biodiversity conservation and discuss potential strategies to mitigate these effects.Impact of Climate Change on Species:One of the key impacts of climate change on biodiversity is the shifting of species' ranges. As temperatures increase, species are forced to migrate to new locations in search of suitable habitats. This can disrupt the delicate balance of ecosystems, leading to the decline or extinction of certain species. Additionally, the timing of seasonal activities, such as breeding and migration, can also be affected by climate change, further impacting population dynamics.Furthermore, climate change can also exacerbate existing threats to biodiversity. For example, rising temperatures can increase the severity and frequency of wildfires, making it difficult for certain species to recover. Similarly, extreme weather events such as hurricanes and droughts can lead to the destruction of habitats, resulting in a significant loss of biodiversity.Implications for Conservation:The impacts of climate change on biodiversity conservation pose significant challenges for conservation efforts. Traditional conservation strategies, such as protected areas and species-specific management plans, may no longer be effective in the face of changing climates. Conservationists need to consider adapting their approaches to ensure the long-term survival of species and ecosystems.Adaptive Management:Adaptive management is one approach that can help address the challenges posed by climate change. This approach involves continuously monitoring and assessing the impacts of climate change on species and ecosystems, and adjusting conservation strategies accordingly. For example, if a previously protected area is no longer suitable for certain species due to changing climates, conservationists may need to consider creating new protected areas that provide suitable habitats.Assisted Migration:Assisted migration, or translocation, is another strategy that may be necessary in some cases. This involves manually moving species to new locations that offer more favorable conditions for their survival. However, this approach comes with its own set of risks and ethical considerations, as it can disrupt native ecosystems and potentially introduce invasive species. Therefore, careful research and planning must be undertaken before implementing assisted migration programs.Habitat Restoration:Another important strategy for biodiversity conservation in achanging climate is habitat restoration. Restoring degraded habitats can help create more resilient ecosystems that are better able to withstand the impacts of climate change. This may involve replanting native vegetation, restoring wetlands, or implementing sustainable land management practices.Conclusion:Climate change poses significant challenges to biodiversity conservation worldwide. However, by adopting strategies such as adaptive management, assisted migration, and habitat restoration, conservationists can help mitigate the impacts of climate change and promote the long-term survival of species and ecosystems. It is crucial for governments, organizations, and individuals to work together to implement these strategies and preserve the incredible diversity of life on our planet.。
引言概述:正文内容:一、外文翻译的重要性1.外文翻译在学术领域的作用外文翻译可以帮助我们了解和掌握国外学术前沿,扩大我们的学术视野,促进思维的创新与交流。
2.外文翻译在商业领域的意义外文翻译在商业领域中,特别是跨国公司的经营中起到了至关重要的作用,能够帮助企业了解竞争对手的动态,并进行市场调研和产品开发。
3.外文翻译在文化交流中的作用外文翻译是促进国与国之间文化交流的重要手段,能够传播本国文化,增进两国人民的友谊。
二、外文翻译的技巧1.语言能力的培养外文翻译的首要条件是具备扎实的外语基础,需要加强对词汇、语法和表达方式的学习。
2.翻译技巧与方法翻译技巧包括对上下文的理解、逐词逐句的翻译和准确传达原意等。
同时,还可以运用翻译工具进行辅助翻译。
3.灵活运用翻译策略根据翻译的目的和要求,可以选择直译、意译或文化转换等不同的翻译策略。
三、外文翻译的难点1.语言和文化差异不同语言和文化之间的差异可能导致翻译难度增加,需要对原文进行深入理解,并灵活运用翻译技巧。
2.专业术语的翻译外文翻译中遇到的专业术语需要准确传达,这需要对相关领域的专业知识有一定的了解,可以借助词典和其他资源进行查询。
3.语义和语境的理解在翻译过程中,对原文的语义和语境理解不准确可能导致误译,需要细致入微地理解每个句子和词语的意义。
四、外文翻译中常见的问题1.语法和表达问题外文翻译中经常会涉及到语法和表达问题,需要对原文和翻译文本进行仔细对比和校正,确保语法和表达的准确性。
2.遗漏和加词问题翻译过程中可能会出现遗漏或者加词的情况,需要细心排查,保持原文和翻译文本的一致性。
3.歧义和模糊问题外文翻译中可能会存在歧义和模糊的词语或句子,需要根据上下文进行准确的判断和翻译。
五、外文翻译的应用1.学术研究和论文撰写外文翻译能够帮助学者了解国外学术动态,并为自己的研究提供参考资料,从而提升论文的质量和水平。
2.商业与经济领域外文翻译对于跨国公司的运营和市场开拓至关重要,可以帮助企业了解竞争对手和市场需求,为企业决策提供依据。
论文写作中的外文翻译一、引言在如今全球化的时代,全球各个领域的学术研究都离不开海量的国际文献阅读。
然而,对于非英语母语的研究者来说,理解和运用外文文献成为了一个常见的挑战。
本文将探讨论文写作中外文翻译的重要性、技巧和对于学术研究的影响。
二、外文翻译的重要性1. 探索全球化的学术前沿外文翻译是获得国际学术研究成果的主要途径之一。
通过阅读和翻译外文文献,研究者可以了解全球学术前沿,并在自己的研究中借鉴和应用国际领先的研究成果,从而提高论文的质量和学术水平。
2. 拓宽研究视野翻译外文文献能够帮助研究者拓宽自己的研究视野。
不同国家和地区的学术界存在着不同的研究思路和方法,通过翻译外文文献,研究者可以深入了解其他学术领域的研究思想,为自己的研究提供新的思路和视角。
三、外文翻译的技巧1. 字典和翻译工具的运用在进行外文翻译时,合理利用字典和翻译工具是提高翻译效率和准确性的重要手段。
目前,市面上存在着众多的在线翻译工具和专业字典,研究者可以结合使用这些工具来更好地理解和翻译外文文献。
2. 上下文理解的重要性在进行外文翻译时,不仅需要理解每个词语的字面意思,更需要理解其在上下文中的含义。
上下文的语言环境会影响某个词的具体意思,因此,在进行翻译的过程中,研究者要通过上下文的分析来准确理解和翻译外文文献。
3. 注意语法和语义的转换不同语言之间存在着语法和语义的差异,研究者在进行外文翻译时需要注意将原文的语法和语义转换成适合目标语言的表达方式。
例如,英语中的被动语态在中文中要转换为主动语态,翻译时需要灵活运用语言表达的规则。
四、外文翻译对学术研究的影响1. 提高学术研究的质量外文翻译能够使研究者更深入地理解和掌握国际学术研究成果,为自己的学术研究提供新的思路和方法。
通过引用国际文献,研究者能够提高论文的可信度和学术价值,从而提高自己的研究质量。
2. 增强跨文化的交流和合作外文翻译能够促进国际学术界的跨文化交流和合作。
附录C:外文翻译资料Article Source:Business & Commercial Aviation, Nov 20, 2000. 5-87-88 Interactive Electronic Technical Manuals Electronic publications can increase the efficiency of your digital aircraft and analogtechnicians.Benoff, DaveComputerized technical manuals are silently revolutionizing the aircraft maintenance industry by helping the technician isolate problems quickly, and in the process reduce downtime and costs by more than 10 percent.These electronic publications can reduce the numerous volumes of maintenance manuals, microfiche and work cards that are used to maintain engines, airframes, avionics and their associated components."As compared with the paper manuals, electronic publications give us greater detail and reduced research times," said Chuck Fredrickson, general manager of Mercury Air Center in Fort Wayne, Ind.With all the advances in computer hardware and software technologies, such as high quality digital multimedia, hypertext and the capability to store and transmit digital multimedia via CD-ROMs/ networks, technical publication companies have found an effective, cost-efficient method to disseminate data to technicians.The solution for many operators and OEMs is to take advantage of today's technology in the form of Electronic Technical Manuals (ETM) or Interactive Technical Manuals (IETM). An ETM is any technical manual prepared in digital format that has the ability to be displayed using any electronic hardware media. The difference between the types of ETM/IETMs is the embedded functionality and implementation of the data."The only drawback we had to using ETMs was getting enough computers to meet our technicians' demand," said Walter Berchtold, vice president of maintenance at Jet Aviation's West Palm Beach, Fla., facility.A growing concern is the cost to print paper publications. In an effort to reduce costs, some aircraft manufacturers are offering incentives for owners to switch from paper to electronic publications. With an average printing cost of around 10 cents per page, a typical volume of a paper technical manual can cost the manufacturer over $800 for each copy. When producing a publication electronically, average production costs for a complete set of aircraft manuals are approximately $20 per copy. It is not hard to see the cost advantages of electronic publications.Another advantage of ETMs is the ease of updating information. With a paper copy, the manufacturer has to reprint the revised pages and mail copies to all the owners. When updates are necessary for an electronic manual, changes can either be e-mailed to theowners or downloaded from the manufacturer's Web site.So why haven't more flight departments converted their publications to ETM/IETMs? The answer lies in convincing technicians that electronic publications can increase their efficiency."We had an initial learning curve when the technicians switched over, but now that they are familiar with the software they never want to go back to paper," said Fredrickson.A large majority of corporate technicians also said that while they like the concept of having a tool that aids the troubleshooting process, they are fearful to give up all of their marked-up paper manuals.In 1987, a human factors study was conducted by the U.S. government to compare technician troubleshooting effectiveness, between paper and electronic methodology, and included expert troubleshooting procedures with guidance through the events. Results of the project indicated that technicians using electronic media took less than half the time to complete their tasks than those using the paper method, and technicians using the electronic method accomplished 65 percent more in that reduced time.The report also noted that new technicians using the electronic technical manuals were 12-percent more efficient than the older, more experienced technicians. (Novices using paper took 15 percent longer than the experts.)It is interesting that 90 percent of the technicians who used the electronic manuals said they preferred them to the paper versions. This proved to the industry that with proper training, the older technicians could easily transition from paper to electronic media.Electronic publications are not a new concept, although how they are applied today is. "Research over the last 20 years has provided a solid foundation for today's IETM implementation," said Joseph Fuller of the U.S. Naval Surface Warfare Center. "IETMs such as those for the Apache, Comanche, F-22, JSTAR and V-22 have progressed from concept to military and commercial implementation."In the late 1970s, the U.S. military investigated the feasibility of converting existing paper and microfilm. The Navy Technical Information Presentation System (NTIPS) and the Air Force Computer- based Maintenance Aid System (CMAS) were implemented with significant cost savings.The report stated that transition to electronic publications resulted in reductions in corrective maintenance time, fewer false removals of good components, more accurate and complete maintenance data collection reports, reduction in training requirements and reduced system downtime.The problem that the military encountered was ETMs were created in multiple levels of complexity with little to no standardization. Options for publications range from simple page-turning programs to full-functioning automated databases.This resulted in the classification of ETMs so that the best type of electronic publication could be selected for the proper application.Choosing a LevelWith all of the OEM and second- and third-party electronic publications that are available it is important that you choose the application level that is appropriate for your operation.John J. Miller, BAE Systems' manager of electronic publications, told B/CAthat "When choosing the level of an ETM/IETM, things like complexity of the aircraft and its systems, ease of use, currency of data and commonality of data should be the deciding factors; and, of course, price. If operational and support costs are reduced when you purchase a full-functioning IETM, then you should purchase the better system."Miller is an expert on the production, sustainment and emerging technologies associated with electronic publications, and was the manager of publications for Boeing in Philadelphia.Electronic publications are classified in one of five categories. A Class 1 publication is a basic electronic "page turner" that allows you to view the maintenance manual as it was printed. With a Class 2 publication all the original text of the manual is viewed as one continuous page with no page breaks. In Class 3, 4 and 5 publications the maintenance manual is viewed on a computer in a frame-based environment with increasing options as the class changes. (See sidebar.)Choosing the appropriate ETM for your operation is typically limited to whatever is being offered on the market, but since 1991 human factors reports state the demand has increased and, therefore, options are expected to follow.ETM/IETM ProvidersCompanies that create ETM/IETMs are classified as either OEM or second party provider. Class 1, 3 and 4 ETM/IETMs are the most commonly used electronic publications for business and commercial operators and costs can range anywhere from $100 to $3,000 for each ETM/ IETM. The following are just a few examples ofETM/IETMs that are available on the market.Dassault Falcon Jet offers operatorsof the Falcon 50/50EX, 900/900EX and 2000 a Class 4 IETM called the Falcon Integrated Electronic Library by Dassault (FIELD). Produced in conjunction with Sogitec Industries in Suresnes Cedex, France, the electronic publication contains service documentation, basic wiring, recommended maintenance and TBO schedules, maintenance manual, tools manual, service bulletins, maintenance and repair manual, and avionics manual.The FIELD software allows the user to view the procedures and hot- link directly to the Illustrated parts catalog. The software also enables the user to generate discrepancy forms, quotation sheets, annotations in the manual and specific preferences for each user.BAE's Miller said most of the IETM presentation systems have features called "Technical Notes." If a user of the electronic publication notices a discrepancy or needs to annotate the manual for future troubleshooting, the user can add a Tech Note (an electronic mark-up) to the step or procedure and save it to the base document. The next time that or another user is in the procedure, clicking on the tech note icon launches a pop-up screen displaying the previous technician's comments. The same electronic transfer of tech notes can be sent to other devices by using either a docking station or through a network server. In addition, systems also can use "personal notes" similar to technical notes that are assigned ID codes that only the authoring technician can access.Requirements for the FIELD software include the minimum of a 16X CD-ROM drive,Pentium II 200 MHz computer, Windows 95, Internet Explorer 4 SP 1 and Database Access V3.5 or higher.Raytheon offers owners of Beech and Hawker aircraft a Class 4 IETM called Raytheon Electronic Publication Systems (REPS). The REPS software links the frame-based procedures with the parts catalog using a single CD-ROM.Raytheon Aircraft Technical Publications said other in- production Raytheon aircraft manual sets will be converted to the REPS format, with the goal of having all of them available by 2001. In addition Raytheon offers select Component Maintenance Manuals (CMM). The Class 1 ETM is a stand-alone "page-turner" electronic manual that utilizes the PDF format of Adobe Acrobat.Other manufacturers including Bombardier, Cessna and Gulfstream offer operators similar online and PDF documentation using a customer- accessed Web account.Boeing is one manufacturer that has developed an onboard Class 5 IETM. Called the Computerized Fault Reporting System (CFRS), it has replaced the F-15 U.S. Air Force Fault Reporting Manuals. Technologies that are currently being applied to Boeing's military system are expected to eventually become a part of the corporate environment.The CFRS system determines re-portable faults by analyzing information entered during a comprehensive aircrew debrief along with electronically recovered maintenance data from the Data Transfer Module (DTM). After debrief the technicians can review aircraft faults and schedule maintenance work to be performed. The maintenance task is assigned a Job Control Number (JCN) and is forwarded electronically to the correct work center or shop. Appropriate information is provided to the Air Force's Core Automated Maintenance System (CAMS).When a fault is reported by pilot debrief, certain aircraft systems have the fault isolation procedural data on a Portable Maintenance Aid (PMA). The JCN is selected on a hardened laptop with a wireless Local Area Network (LAN) connection to the CFRS LAN infrastructure. The Digital Wiring Data System (DWDS) displays aircraft wiring diagrams to the maintenance technician for wiring fault isolation. On completion of maintenance, the data collected is provided to the Air Force, Boeing and vendors for system analysis.Third party IETM developers such as BAE Systems and Dayton T. Brown offer OEMs the ability to subcontract out the development of Class 1 through 5 ETM/IETMs. For example, Advantext, Inc. offers PDF and IPDF Class 1 ETMs for manufacturers such as Piper and Bell Helicopters. Technical publications that are available include maintenance manuals, parts catalogs, service bulletins, wiring diagrams, service letters and interactive parts ordering forms.The difference between the PDF and IPDF version is that the IPDF version has the ability to search for text and include hyperlinks. A Class 1 ETM, when printed, is an exact reproduction of the OEM manuals, including any misspellings or errors. Minimum requirements for the Advantext technical publications is a 486 processor, 16 MB RAM with 14 MB of free hard disk space and a 4X CD-ROM or better.Aircraft Technical Publishers (ATP) offers Class 1, 2 and 3 ETM/ IETMsfor the Beechjet 400/400A; King Air 300/ 350, 200 and 90; Learjet 23/24/25/28/29/35/36/55; Socata TB9/10/20/21 and TBM 700A; Sabreliner 265-65, -70 and -80; andBeech 1900. The libraries can include maintenance manuals, Illustrated parts bulletins, wiring manuals, Airworthiness Directives, Service Bulletins, component maintenance manuals and structural maintenance manuals. System minimum requirements are Pentium 133 MHz, Windows 95 with 16 MB RAM, 25 MB free hard disk space and a 4X CD-ROM or better.Additional providers such as Galaxy Scientific are providing ETM/ IETMs to the FAA. This Class 2, 3 and 4 publication browser is used to store, display and edit documentation for the Human Factors Section of the administration."Clearly IETMs have moved from research to reality," said Fuller, and the future looks to hold more promise.The Future of Tech PubsThe use of ETM/IETMs on laptop and desktop computers has led research and development corporations to investigate the human interface options to the computer. Elements that affect how a technician can interface with a computer are the work environment, economics and ease of use. Organizations such as the Office of Naval Research have focused their efforts on the following needs of technicians: -- Adaptability to the environment.-- Ease of use.-- Improved presentation of complex system relationship.-- Maximum reuse and distribution of engineering data.-- Intelligent data access.With these factors in mind, exploratory development has begun in the areas of computer vision, augmented reality display and speech recognition.Computer vision can be created using visual feedback from a head- mounted camera. The camera identifies the relative position and orientation of an object in an observed scene, and the object is used to correlate the object with a three-dimensional model. In order for a computer vision scenario to work, engineering data has to be provided through visually compatible software.When systems such as Sogitech's View Tech electronic publication browser and Dassault Systemes SA's Enovia are combined, a virtual 3D model is generated.The digital mockup allows the engineering information to directly update the technical publication information. If a system such as CATIA could be integrated into a Video Reference System (VRS), then it could be possible that a technician would point the camera to the aircraft component, the digital model identifies the component and the IETM automatically displays the appropriate information.This example of artificial intelligence is already under development at companies like Boeing and Dassault. An augmented reality display is a concept where visual cues are presented to users on a head-mounted, see-through display system.The cues are presented to the technician based on the identification of components on a 3D model and correlation with the observed screen. The cues are then presented as stereoscopic images projected onto the object in the observed scene.In addition a "Private Eye" system could provide a miniature display of the maintenance procedure that is provided from a palm- size computer. Limited success hascurrently been seen in similar systems for the disabled. The user of a Private Eye system can look at the object selected and navigate without ever having to touch the computer. Drawbacks from this type of system are mental and eye fatigue, and spatial disorientation.Out of all the technologies, speech recognition has developed into an almost usable and effective system. The progression through maintenance procedures is driven by speaker-independent recognition. A state engine controls navigation, and launches audio responses and visual cues to the user. Voice recognition software is available, although set up and use has not been extremely successful.Looking at other industries, industrial manufacturing has already started using "Palm Pilot" personal digital assistants (PDAs) to aid technicians in troubleshooting. These devices allow the technician to have the complete publication beside them when they are in tight spaces. "It would be nice to take the electronic publications into the aircraft, so we are not constantly going back to the work station to print out additional information," said Jet Aviation's Berchtold.With all the advantages that a ETM/ IETM offers it should be noted that electronic publications are not the right solution all of the time, just as CBT is not the right solution for training in every situation. Only you can determine if electronic publications meet your needs, and most technical publication providers offer demo copies for your review. B/CA IllustrationPhoto: Photograph: BAE Systems' Christine Gill prepares a maintenance manual for SGML conversion BAE Systems; Photograph: Galaxy Scientific provides the FAA's human factors group with online IETM support.; Photograph: Raytheon's Class 4 IETM "REPS" allows a user to see text and diagrams simultaneously with hotlinks to illustrated parts catalogs.外文翻译资料译文部分文章出处:民航商业杂志,2000-11-20,5-87-88交互式电子技术手册的电子出版物可以提高数字飞机和模拟技术的效率。
e c o l o g i c a l e n g i n e e r i n g 28(2006124–130a v a i l ab l e a t w w w.sc i e n c ed i re c t.c omj o u r n a l h o m e p a g e :w w w.e l s e v i e r.c o m /l o c a t e /e c o l e n gPlant-biofilm oxidation ditch for in situ treatm ent of polluted watersQi-Tang Wu a ,∗,Ting Gao a ,Shucai Zeng a ,Hong Chua ba College of Natural Resources and Environment,South China Agricultural University,Guangzhou 510642,ChinabDepartment of Civil and Structural Engineering,Hong Kong Polytechnic University,Hung Hom,Kowloon,Hong Kong SAR,Chinaa r t i c l ei n f o Article history:Received 17December 2005Received in revised form 16May 2006Accepted 18May 2006Keywords:Plant-biofilm oxidation ditch (PBFODIn situWastewater treatmenta b s t r a c tEutrophication of surface water bodies is a problem of increasing environmental and ecolog-ical concern worldwide and is particularly serious in China.In the present study,oxidation ditches were connected to a lake receiving municipal sewage sludges.T wo 24m 2(width 2m,length 12mparallel plastic oxidation ditches material were installed on a lake near the inlet of the municipal sewage.Zizania caduciflora and Canna generalis were grown in the ditches with plastic floating supporters for the removal of N and P from the sewage.The experiment was conducted firstly with municipal sewage in autumn–winter seasons for about 150daysunder the following conditions:2m 3/h influent flow,0.75kW jet-flow aerator(air/water of 5,18h HRT (hydrological retention timeand a return ratio of 10.Then it was run with the polluted lake water in summer–autumn for about 160days with an aerator of 1.25kW and an influent of 6m 3/h (air/water 3.3,HRT 6h.The performance was quite stable during the experimental period for the municipal sewage treatment.The average removal rates of COD (chemical oxygen demand,SS (suspended solids,TP (total phosphorus,NH 4+-N and inorganic-N were 70.6,75.8,72.6,52.1and50.3%,respectively.For the polluted lake water treatment,the average concentrations of COD,NH 4+-N and TP were 42.7,13.1and 1.09mg/L,respectively,in the influent and were 25.1,6.4and 0.38mg/L,respectively,in the effluent.The capacity of the plants to remove N and P by direct uptake was limited,but the indi-rect mechanisms also occurred.The proposed process,transforming the natural lake into a wastewater treatment plant,could evidently reduce the costs of the sewage collection,the land space requirement and the construction compared with conventional sewage treat-ment plants,and is especially suited to conditions in south China and south-east Asia.©2006Elsevier B.V .All rights reserved.1.IntroductionMany water bodies are subject to eutrophication due to eco-nomic constraints in reducing point sources of nutrients and/or to a high proportion of diffuse sources,and the prob-lem is particularly common in China because the proportion of treated municipal sewage is still low due to the relatively high capital investmentrequired.Accordingly,43.5%of 130investi-gated major lakes in China were found to be highly eutrophied∗Corresponding author .Tel.:+862085280296;fax:+862085288326.E-mail address:qitangwu@ (Q.-T.Wu.and 45%were of intermediate status (Li et al.,2000.These pol-luted lakes were mainly located in economically developed regions and especially around cities where large amounts of municipal sewage are discharged without appropriate treat-ment.Increasingly,natural or constructed wetlands,including buffer zones(Correll,2005,are being used for removal of pol-lutants from wastewater or for treatment of stormwater runoff from agricultural land and other non-point sources (Mitsch ete c o l o g i c a l e n g i n e e r i n g28(2006124–130125Table1–COD and BOD5of the study lake sampled at three points for5days inMay2003COD(mg/LBOD5(mg/LBOD5/COD13May89.5135.700.4083.3334.500.4189.5136.600.4114May55.5624.800.4589.5135.200.3949.3820.900.4227May105.1141.300.3981.0832.300.40111.1141.000.3728May60.0026.830.4563.3327.700.4463.3327.000.4329May90.0035.700.4093.3337.000.40117.9949.400.42al.,2000;Coveney et al.,2002;Belmont et al.,2004.However, this method requires a large land area in addition to the lake in question.For in situ treatment of hypereutrophic water bodies where the transparency of the water does not allow regrowth of submerged macrophytes,phosphorus precipitation in eutrophic lakes by iron application(Deppe and Benndorf, 2002or by additions of lime(Walpersdorf et al.,2004has been reported.Aeration of river water has been employed to remediate polluted rivers since the1970s(Wang et al.,1999. Increasing oxygen transfer inflow by stones placed in rivers was studied by Cokgor and Kucukali(2004.Growingfloating aquatic macrophytes(Sooknah and Wilkie,2004or terrestrial green plants usingfloating supports(Li and Wu,1997,physical ecological engineering(PEEN(Pu et al.,1998,and biotic addi-tives have also been applied(Chen,2003.However,these sim-ple designs do not constitute a real water treatment system and the efficiencies of these treatments are unsatisfactory.Activated sludge systems have been proved efficient treat-ing municipal sewage since the1960s(Ray,1995.However, this type of system has not been used for in situ remediation of polluted lakes or rivers.In the present study,the oxidation ditch technique was adopted on a lake receiving municipal sewage sludge.Floating green plants and the biofilms com-prisingfloating materials and plant roots were also added to enhance N and P removal.A pilot scale experiment was set up to test the feasibility and performance of the plant-enhanced oxidation ditch for in situ treatment ofboth the municipal sewage and the polluted lake water.2.Experimental2.1.Site descriptionThe study lake was situated at South China Agricultural Uni-versity,Guangzhou,China.The area of the lake was about 10000m2and the depth0.5–3m.This lake received the munic-ipal sewage from the residential area around the university.Fig.1–Surface arrangement of the plant-biofilm oxidation ditch and the waterflows.(1Wall of nylon tissue;(2nets of5mm;(3nets of0.25mm;(4oxidation ditch;(5jet-flow aerator;(6water pump;(7floating green plants;(8sewage entry.2.2.Establishment of the plant-biofilm oxidationditchesT wo24m2(width2m,length12mparallel oxidation ditches made of plastic materials were installed along the lake bank near the sewage inlet.The inner ditch was made of cement and the outer ditch was isolated with nylon tissues andfix-ing PVC(polyvinyl chloridetubes.Fig.1showsthe surface arrangement and the waterflow path.The coarse suspended solids in the influent werefiltered by two pl astic nets,one with a pore size of5mm and the other with a pore size of0.25mm,whereas the suspended solids in the effluent werefiltered by a plastic net with a pore size of 0.25mm.Zizania caduciflora and Canna generalis were grown in the ditch with theplast icfloating supporters which held the plants in position.Thefloating supporters were made of closed126e c o l o g i c a l e n g i n e e r i n g28(2006124–130PVC tubes and nylon nets and each was3.6m2.Zizania caduci-flora was grown on twofloating supporters an d Canna gener-alis on another two supporters.The plants were planted in four columns andfive lines.The twofloating supporters with Canna generalis were near the influent and the two with Zizania caduciflora were near the effluent.The entire disposal system is shown in Photo1.2.3.Conduct of the experimentsAn experiment was conductedfirstly on municipal sewage in autumn–winter seasons of2003–2004for about150days. The aeration of the oxidation ditch was achieved using a jet-flow aerator of0.75kW(Aqua Co.,Italy;air generation10m3/h, water jet rate22–28m3/h.The water sampling started on18 September2003and endedon12February2004.The influent was2m3/h created by a water pump of0.37kW.With the jet-flow aerator of0.75kW the theoretical air/water ratio was5, HRT was18h and the return ratio was10–13.The system was then run with the polluted lake water in summer and autumn2004for about160days with an aerator of1.25kW and with an influent of6m3/h(air/water3.3,HRT 6h.The influent was not created by water pump but by the driving fo rce of the jet-flow aerator.The water sampling for the second run started on15May2004and endedon15October 2004.2.4.Sampling and analysisThe influent and effluent were sampled every3–5days at 08:00–09:00a.m.andat17:00–18:00p.m.,each with three sam-pling re plicates for thefirst run.For the second run,the influ-ent and effluent were sampled1day a week.The water sam-pler took0–30cm surface water.The samples were analyzed for COD Cr,BOD5,SS,TP,NO3−-N,NH4+-N and pH according to standard methods(APHA,1995.The plant s were transplanted ontofloating supporters two weeks before water sampling and thefirst harvest was carried out60days later and at the termination of thefirst run for the municipal sewage.The plant biomass and N and P con-tents were measured according to the methods proposed by the Soil and Agro-Chemical Analysis Committee of China(Lu, 2000.The total uptakes of N and P were calculated and com-pared with the total removal of these elements calculated by the cumulative removal each day following measurement of a water sample.Total N removal=(average N in influent−average N in effluent×48×D iwhere48was the treated water volume per day in m3/day;D i was the number of days following the water sampling and before the next sampling.3.Results and discussionTable2shows the removal of COD Cr and SS by plant-biofilm oxidation ditch for the treatment of the municipal sewage in autumn–winter seasons of2003–2004.The removal of COD Cr varied from60to79%with an average of70%for the influent COD Cr ranging from100to200mg/L,a nd resulted in effluent COD Cr valuesfrom30to55mg/L(Table2,Fig.2.The average removal percentage was about75%for SS and variedfrom68to82%(Table2.The effluent SS was about 30mg/L which is the effluent limit value of the second grade for the sewage treatment plants in China(GB18918,2002 (Fig.3,for the influents varying from60to240mg/L.The average NH4+-N removal from influent was52%,which was lower in winter than in autumn(Table3.This may be due to lower bacterial activity in winter,but theinfluent NH4+-NTable2–Removal of COD and SS by the plant-biofilm oxidation ditch for the in situ treatment of municipal sewage each month in autumn–winter seasons of2003–2004Period Sampled days Water temperature(◦CInfluent(mg/LEffluent(mg/LRemoval(%COD Cr18–30September528.0118.54(3.01a34.34(7.8367.74 3–28October826.1123.91(4.0333.51(4.2672.661–7November326.0153.94(2.7337.60(3.8175.4918–28November423.1170.22(4.2835.45(5.3778.711–15December419.3180.36(8.2039.24(7.0677.6511–31January314.5128.46(3.6652.04(5.2359.504–12February216.8178.35(4.1662.86(5.8362.47Average150.54(4.3042.15(5.6370.60SS18–30September528.0160.4041.6074.18 3–28October826.1144.3826.2581.171–7November326.0116.0033.3370.7918–28November423.1111.7521.5080.981–15December419.390.5028.5068.4211–31January314.5104.0017.3382.384–12February216.8120.5033.0072.57Average121.0828.7975.78e c o l o g i c a l e n g i n e e r i n g28(2006124–130127Fig.2–COD in the influent and effluent of the plant-biofilm oxidation ditch for the in situ treatment of municipal sewage in autumn–winter seasons of2003–2004.was also higher in winter(Fig.4probably because of lower water consumption in the cold season.The total inorganic-N removal was similar to that for NH4+-N(Table3.NO3−-N concentrations were rather similar in the influent and the effluent.The total P removal varied from63to78%and was higher and more regular than N removal(Table3.The P concentra-tion in treated effluent was about1mg/L(Fig.5and conformed to the Chinese municipal sewage treatment standard which is set to3mg/L for second grade regions and1.5forfirst grade regions(GB18918,2002.Fig.6shows typical changes in the water quality param-eters for the sampling points from inlet to outlet.Thisindi-Fig.3–Suspended solids concentration in the influent and effluent of the p lant-biofilm oxidation ditch for the in situ treatment of municipal sewage in autumn–winter seasons of2003–2004.cates that COD and SS decreased gradually,but NH4+-N and TP dropped substantially following the mixing with the return water by the aerator and then decreased slowly,while NO3−-N and pH of the water remained virtually unchanged.The water DO increased dramatically following the aeration,decreased slowly thereafter and remained rather high even in the efflu-ent(about5.5mg/L.For the second run treating the polluted lake water on-site,the average influent COD Cr was42.7mg/L and the effluent 25.1mg/L for about160days during summer–autumn seasons (Fig.7.The removal of NH4+-N was about50%from about13.1 to6.4mg/L.Total-P in the effluents was rather stable,bei ngTable3–The removal of N and P by the plant-biofilm oxidation ditch for the in situ treatment of municipal sewage for each month in autumn–winter seasons of2003–2004Period Sampled days Water temperature(◦CInfluent(mg/LEffluent(mg/LRemoval(%NH4+-N18–30September528.020.60(0.30a7.16(0.2264.72 3–28October826.126.55(0.2310.15(0.2061.671–7November326.030.00(0.4113.67(0.2254.5118–28November423.135.15(0.7915.95(0.2653.991–15December419.335.89(0.3515.93(0.2755.1511–31January314.530.57(0.6918.59(0.2236.634–12February216.835.23(0.0521.61(0.0637.72Average30.57(0.4014.72(0.2152.06NH4+-N+NO3−-N18–30September528.023.06(0.159.24(0.1159.94 3–28October826.128.31(0.1212.01(0.1457.571–7November326.031.42(0.2114.58(0.1153.5918–28November423.136.32(0.4016.81(0.1353.721–15December419.337.41(0.1917.54(0.1453.1111–31January314.531.96(0.3720.07(0.1337.204–12February216.837.11(0.0323.35(0.0337.08Average32.23(0.2116.23(0.1150.32TP18–30September528.0 3.56(0.070.81(0.0475.56 3–28October826.1 4.01(0.140.87(0.0478.241–7November326.0 4.37(0.13 1.20(0.0472.5618–28November423.1 4.89(0.16 1.13(0.0776.661–15December319.5 4.86(0.80 1.38(0.2371.07 11–31January314.5 3.75(0.45 1.35(0.0363.32 4–12February216.8 4.75(0.10 1.51(0.0566.20 Average 4.31(0.16 1.16(0.0471.89128e c o l o g i c a l e n g i n e e r i n g 28(2006 124–130Fig.4–NH 4+-N concentration in the influent and effluent of the plant-biofilm oxidation ditch for the in situ treatment of municipal sewage in autumn–winter seasons of2003–2004.Fig.5–Total-P concentration in the influent and effluent of the plant-biofilm oxidation ditch for the in situ treatment of municipal sewage in autumn–winter seasons of2003–2004.Fig.6–T ypical changes in the pollutants in theplant-biofilm oxidation ditch during the in situ treatment ofFig.7–The influent and effluent concentrations of COD (up,NH 4+-N (medianand total-P (bottomin theplant-biofilm oxidation ditch treating polluted lake water.about 0.38mg/L from an average of 1.09mg/L in the influents.The removal of COD Cr ,NH 4+-N and Total-P was then quite sat-isfactory both for the municipal sewage and the polluted lake water.The removal of N and P was somewhat higher than con-ventional oxidation ditches,perhaps due to the existence of the plant-biofilm in the studiedsystem.However,the direct uptake rates of N and P by green plants were almost negligi-ble compared to the total removal of these elements by the whole system (Table4.However,the plants may have cre-ated localized anaerobic conditions by their root exudates and dead biomass and enhance the denitrification of N by micro-organisms as occurs in constructed wetlands (Hone,2000.Besides the green plants,the proposed system also con-tains biofilm coated to the plastic materials.The high velocity of return-fluent was different to the conventional oxidation ditch.Kugaprasatham et al.(1982showed that the increase of the fluent velocity could increase the density of the biofilm if the nutrient conditions were suitable for bacteria growth.Simultaneous nitrification/denitrification (SND(Van Mun ch etal.,1996may also occur in the system.Concerning the P removal of the system,biological phos-phate removal processes may occur but were not significant because there was no sludge removal and very little sludge precipitation after the run for treatment of municipal sewage.This may partly due to the existence of some ferric chains which were added to precipitate and fix the nylon tissue to the lake bottom,with formation of precipitates of ferric phos-e c o l o g i c a l e n g i n e e r i n g 2 8 ( 2 0 0 6 124–130 129 Table 4 – Proportions of N and P uptake by plants and total removal in the plant-biofilm oxidation ditch treating municipal sewage Date Days ZCa Harvested fresh biomass (g CG ZC 5 September–4 November 5 November–6 January Total or average a Plant uptake (g N CG 5.30 13.03 System removal (kg N CG P Percent of plant uptake N (% P (% P ZC 0.88 0.24 2.79 60 63 123 2200 625 9725 2750 4150 4.85 1.20 24.38 0.72 0.95 37.63 65.45 103.1 7.13 12.78 19.91 0.03 0.02 0.02 0.02 0.01 0.01 ZC: Zizania caduciflo ra; CG: Canna generalis. tained for at least 1 year. The actual mechanisms still remain to be identified. The oxidation ditch has been used for many years worldwide as an economical and efficient wastewater treatment technology that can remove COD, nitrogen and a fraction of the phosphorusefficiently. Anaerobic tanks (Liu et al., 2002 and phased isolation ditch systems with intra-channel clarifier (Hong et al., 2003 were added to the system to increase the TP removal efficiency. The proposed process takes an artificial process in combination with natural purification, transforming the natural lake into the wastewater treatment plant, and could evidently reduce the costs of sewage collection, the landspace requirement and the construction costs compared with the conventional sewage treatment plants. This process could be especially suitable to subtropical regions and to many water bodies in south China and southeast Asia where sewage treatment facilities are not well established. China. The authors are grateful to Dr. P. Christie, Department of Agricultural and Environmental Science, Queen’s University Belfast, UK, and Dr. Y. Ouyang, Department of Water Resources, St. Johns River Water Management District, Palatka, FL, USA, for their valuable suggestions and language corrections. references 4. Conclusions The present study adapted the oxidation ditch on the lake surface for in situ treatment of municipal sewage or polluted lake water in combination with plant biofilms for performing N and P removal, and running experiments at pilot scale for about 1.5 years resulted in the following observations: (1 The system was quite satisfactory and stable for treatment of municipal sewage and polluted lake water in removing COD, NH4 + -N and P. (2 The direct uptake of N and P by plants was negligible in comparison with the totalremoval by the system, but indirect mechanisms via plant root exudates and biofilms merit further studies. (3 The proposed process could dramatically reduce the costs of sewage collection, the land-space requirement and the construction costs compared with conventional sewage treatment plants; might be suitable for treatment of both municipal sewage and polluted lake water; and could lead to the promotion of wastewater treatment in many developing countries. Acknowledgements This study was funded by Department of Science and Technology of Guangdong Province (Grant no. 2004B33301007, American Public Health Association (APHA, 1995. Standards Methods for the Examination of Water and Wastewater, 19th ed. American Public Health Association, Washington, DC. Belmont, M.A., Cantellano, E., Thompson, S., Williamson, M.,S’anchez, A., Metcalfe, C.D., 2004. Treatment of domestic wastewater in a pilot-scale natural treatment system in central Mexico. Ecol. Eng. 23, 299–311. Chen, Y.C., 2003. Bioremediation Engineering of Polluted Environment. Chemical Industry Press, Beijing, p. 304 (in Chinese. 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Effect of turbulence on nitrifying biofilms at non-limiting substrate conditions. Water Res. 26, 1629–1638. Li, F.X., Xin, Y., Chen, W., 2000. Assessment of eutrophication level of lakes. Chongqing Environ. Sci. 22, 10–11 (in Chinese. Li, F.B., Wu, Q.T., 1997.Domestic wastewater treatment with means of soilless cultivated plants. Chin. J. Appl. Ecol. 8, 88–92 (in Chinese. Liu, J.X., Wang, B.Z., van Groenestijn, J.W., Doddema, H.J., 2002. Addition of anaerobic tanks to an oxidation ditch system to enhance removal of phosphorus from wastewater. J. Environ. Sci. 14, 245–249.130 e c o l o g i c a l e n g i n e e r i n g 2 8 ( 2 0 0 6 124–130 Lu, R.K., 2000. Soil and Agricultural Chemistry Analysis. China Agriculture Press, Beijing (in Chinese. Mitsch, W.J., Horne, A.J., Nairn, R.W., 2000. Nitrogen and phosphorus retention in wetlands—ecological approaches to solving excess nutrient problems. Ecol. Eng. 14, 1–7. Pu, P., Hu, W., Yan, J., Wang, G., Hu, C., 1998. A physico-ecological engineering experiment for water treatment in a hypertrophic lake in China. Ecol. Eng. 10, 179–190. Ray, B.T., 1995. Environmental Engineering. PWS Publishing Company, New York, pp. 299–341. Sooknah, R.D., Wilkie, A.C., 2004. Nutrient removal by floating aquatic macrophytes cultured in anaerobically digested flushed dairy manure wastewater. Ecol. Eng. 22, 27–42. Van Munch, E.P., Land, P., Keller, J., 1996. Simultaneous nitrification and denitrification in bench-scale sequencing batch reactors. Water Sci. Technol. 20,277–284. Wang, C.X., Lin, H., Shi, K.H., 1999. Restoration of polluted river by pure oxygen aeration. Shanghai Environ. Sci. 18, 411–413 (in Chinese. Walpersdorf, E., Neumann, T., Stuben, D., 2004. Efficiency of natural calcite precipitation compared to lake marl application used for water quality improvement in an eutrophic lake. Appl. Geochem. 19, 1687–1698.。
外文翻译要求
一、外文翻译的目的:
通过外文文献查阅与翻译,熟悉本专业主要的外文书刊,了解毕业设计课题的国内外发展现状和发展趋势及其使用的技术手段和研究方法,进一步提高对外文的阅读应用能力。
二、外文翻译的内容:
阐述所选课题在相应学科领域中的发展进程和研究方向,特别是近年来的发展趋势和最新成果。
可以是系统业务上的文档,也可以是系统涉及到的技术手段的文档。
三、外文翻译的要求:
1.需符合学校相关要求。
3.需认真研读和查阅术语完成翻译,保证翻译语句流畅。
4.翻译的外文文献应主要选自学术期刊、学术会议的文章、有关著作及其他相关材料,应与毕业设计主题相关,并作为外文参考文献列入毕业设计的参考文献。
以下为学校的要求:
一、译文文本要求
1.外文译文不少于2000汉字;
2.外文译文本文格式参照论文正文规范(标题、字体、字号、图表、原文信息等);
3.外文原文资料信息列文末,对应于论文正文的参考文献部分,标题用“外文原文资料信息”,内容包括:
1)外文原文作者;
2)书名或论文题目;
3)外文原文来源:
□出版社或刊物名称、出版时间或刊号、译文部分所在页码
□网页地址
二、外文原文资料(电子文本或数字化后的图片):
1.外文原文不少于10000印刷字符(图表等除外);
2.外文原文若是纸质的请数字化(图片)后粘贴于译文后的原文资料处,但装订时请用纸质原文复印件附于译文后。
毕业论文(设计)外文翻译题目:面对绿色贸易壁垒升级系部名称:经济管理系专业班级:国贸08 学生姓名:潘学号:200880514指导教师:教师职称:副教授2011年12月30日面对绿色贸壁垒升级萨金特摘要:今年五月,欧盟在签发符合RoHS,WEEE,EUP的法令,REACH法规和规章和绿色贸易措施,提出并实施了DMF的顺序法令;DMF的命令禁止有“二甲酯”产品的流向和销售导欧盟市场,然而,3个月后执行的命令,让不少企业都受到影响,特别是金融危机的背景下的中国出口产业。
一些专家指出,绿色贸易壁垒成为继汇率影响外贸的又一个关键因素。
关键词:欧盟、绿色贸易壁垒、中国一、不可避免的“绿色贸易壁垒”近年来,由于欧洲和美洲国家绿色贸易壁垒不断升级;跨越关税壁垒后,另一种非关税的绿色贸易壁垒等待像中国这样的发展中国家。
从2009年2月至4月,欧盟非食品类产品快速预警系统(RAPEX)发布了30条关于对中国鞋和玩具产品的信息,德国、西班牙和法国召回,因为含有DMF。
2009年3月28日,山西检验检疫局工作组从企业收到一份报告,说是遏制拖拉机备用零件出口到意大利,由于使用木质包装已没有“自由DMF”的证明号码。
从2009年7月开始,广州芳村的包装材料制造商受到的退货和返工,因为在其产品中二甲基甲酰胺。
近年来,为什么绿色贸易壁垒在广泛领域的频率使用,它背后有一个深层次的原因。
例如,全球环境恶化,如:臭氧损耗,全球变暖,生物多样性丧失和其他问题,直接影响到人们的消费观念和价值观念,特别是在欧洲和美国等发达国家,消费者的'绿色价值观已经形成,并显示他们对绿色产品的需求和喜好,这也提供了绿色贸易壁垒的形成条件和机会。
此外,传统的非关税越来越多地被谴责,在这种情况下,出于自身利益的欧洲,美国和其他国家开始寻求新的贸易保护措施。
此外,在国家环保标准的差异,以及当前的国际贸易规则和协议是不完整的provids绿色贸易壁垒的借口。
中国环境标志产品认证委员会秘书处主任,教授夏青表示,'绿色贸易壁垒'是不可避免的,任何国家在保护国家安全,动物和植物的安全,公众健康,环境,防止欺诈行为的期限,将提请了相关规定,发布有关规章制度,并采取技术防范措施。
他们提出的测试标准中的规定,构成了一系列可能的'绿色壁垒'。
不过,也有“绿色标准”本身也有差异,这导致欧盟的产品被出口,而中国的一些产品不能进入国际市场中。
二、树起“绿色壁垒”,加剧贸易摩擦在全球经济一体化进程中,以达到保护国内市场的目的,欧盟和其他发达国家采取更多和更加隐蔽的措施,对进口产品的技术要求越来越严格,以及配套的法律法规相继出台。
例如:2007年6月起,欧盟全面实施REACH法规,要求企业申请授权,通知15项高度关注物质(SVHC),2008年6月欧盟发出一个限制使用全氟辛烷磺酸化合物(PFOS)的法令,标志着欧盟正式禁止PFOS在商品的使用;中国的一些出口行业,包括纺织,皮革等出口企业的影响。
作为另一个绿色贸易壁垒,将中国的皮革,家具和其他出口行业的DMF禁令的实施。
欧盟成员国以环保的名义,提出单方面的贸易措施,限制从国外进口,从而导致越来越多的双边或多边贸易摩擦。
欧盟和北美自由贸易区成员国的两个大区域组织基本上都是发达的国家,他们的环保水平和环保标准是相似的,而某些个别成员国之间的差距也往往要协调。
因此,他们可以通过区域自由贸易的模式,以遏制由于没有按照他们的环保标准以外地区的产品。
虽然看似合法的绿色壁垒正在成为流行,但它可能对发展中国家构成严重挑战。
据粗略统计,中国遭受的绿色壁垒,66.1%来自欧盟之间,这一趋势可能对中国——欧盟经贸关系的受到长期的影响。
三、对绿色贸易壁垒积极和客观的回应中国和其他发展中国家在金融危机的背景下应该怎样做,作为绿色贸易壁垒是否应该加强据。
有关业内人士表示,中国将准备在不久的中长期内做出回应。
在短期内,他们对纺织品积极响应,有相关专业人士在市对外经济贸易局,中国贸促会,以及行业协会,以帮助联系律师,并进行协调,以使案件应诉的准备。
在中期,他们必须加快外贸人才的储备,尤其是时下的贸易壁垒变更频繁,外贸人才的专业素质提出了更高的要求。
从长远来看,出口企业应加紧努力,以调整产品结构,加快产业升级,提高产品科技含量,这样才能从根本上减少贸易摩擦。
据悉,中国政府正在分担困难,帮助企业解决问题;由商务部主办,当地职能部门积极发挥'四体联动'机制的作用与商业协会和企业共同面对贸易摩擦;加强贸易摩擦对企业的培训和法律咨询宣传,也做了很多的努力,帮助企业用法律手段来积极应对和回应摩擦。
其实,从保护环境和国家卫生保健的前景来看,所谓的新的壁垒,包括绿色壁垒和知识产权保护也有合理的一面,这可能会促进企业产业结构的优化和升级。
另一个知情人士认为,拿海尔作为一个例子,从20世纪80年代末至90年代初,由于欧洲、美国和其他发达国家进行立法,以限制或禁止进口含有氟氯化碳的冰箱,这使得中国冰箱出口遭受重大损失,海尔集团也没有例外。
然后,海尔冰箱及时推出一个“绿色革命”。
海尔集团在1984年,引进德国技术和德国的高标准环保观念,并不断努力,以减少氟氯化碳的使用,直到制造无氟冰箱;同时无氟冰箱也具有显着的能源节约功能,超越欧洲节能标准20%,美国的18%。
最终,海尔集团在20世纪90年代初已取得欧盟绿色标签证书,在1992年和1996年先后通过了ISO9001和ISO14000体系认证证书。
由于采取了一系列环保措施,海尔集团的产品已达到进口国的环保要求,在1990年以前扭转小的出口市场和出口量,海尔集团在1996年出口21万台冰箱,价值25.71亿美元,从而为海尔成为国内第一出口企业的地位奠定了基础,在向德国出口的亚洲公司中海尔排名第一,这也有利于海尔集团在全国500强企业名单。
四、绿色贸易壁垒对中国对外贸易的影响由于绿色贸易壁垒,中国对外贸易额遭受了巨大的损失。
2002年,因为日本严格的检查和要求价格的大幅度降低,台州蔬菜被阻止进入日本市场。
还是在2002年,因为宁波市水产品不能达到欧盟所要求的卫生标准而被限制进入欧洲联盟(欧盟)。
由于绿色贸易壁垒,60种中国农药被禁止进入欧盟市场,因为他们不能达到欧盟的绿色标准。
根据联合国统计,由于“绿色贸易壁垒”,在2002年这一年中国遭受损失74亿美元。
中国出口到欧盟,日本,韩国和其他国家的跌幅尤其明显。
一般而言,由于严格的绿色壁垒,农产品和食品,纺织产品和机电产品的三个主要行业遭受损失最为严重。
由于这三大类产品是中国出口最多的产品,我们可以很容易地得出一个结论:“绿色贸易壁垒”已成为限制中国产品出口的一个主要障碍。
五、应对发达国家绿色贸易壁垒的主要对策如上所述,这是一个事实即中国出口产品遭受发达国家绿色壁垒的严重限制,遭受了巨大损失。
因此,中国出口商应该仔细考虑对策,以消除绿色贸易壁垒不利影响。
首先,我们应该充分利用的优惠待遇来减少绿色贸易壁垒对发展中国家的限制。
根据协议对绿色贸易壁垒的有关规定,发达国家应当充分考虑到发展中国家的特殊发展,确保发展中国家在财政和贸易需要等方面不受绿色贸易壁垒的限制,确保绿色条款,标准和合格评定程序不给发展中国家带来不必要的麻烦,从而保证发展中国家的正常出口。
因此,作为世界贸易组织中的一个发展中国家,中国有权享受这种优惠待遇。
其次,中国应利用世界贸易组织的争端解决机制来保护自己的利益。
不同于关贸总协定,世贸组织已成立了一个更有力的争端解决机制来解决世贸组织的成员之间的纠纷。
因此,如果我们的利益受到其他世贸组织成员不公平的绿色贸易壁垒的损害,我们可以诉诸争端解决机构来解决这一争端,并敦促其他成员改变其不公正的做法,以保护我们的利益。
第三,中国应强调保护环境,并采取措施提高产品质量和水平,多出口达到绿色出口水平的产品,以满足更高的环保标准,这将从根本上解决我过所遭受绿色贸易壁垒这个问题。
附注:摘自EUROPECHINA,2009年第10期Facing the Upgrade of Green Trade BarrierThomas J. SargentAbstract:The European Union proposed and implemented DMF order this May after issuing RoHS, WEEE, EUP orders, REACH rules and regulations and green trade measures (TBT); the DMF order bans the product containing `dimethylfumarate` (hereafter referred as DMF) to flow and sale in the European Union market, however, after 3 months implementation of the order, quite a few enterprises have been affected, especially for China`s relevant exporting industries under the background of financial crisis. Some expert points out that green trade barrier become the second crucial factor influencing the foreign trade following the exchange rate.Key words:European Union、Green trade barrier、ChinaUnavoidable `Green Trade Barrier`In recent years, owning to the European and American countries green trade barrier is upgrading continuously; after crossing the tariff barrier, there is another non-tariff green trade barrier waiting for developing countries like China there.From February to April of 2009, the EU Rapid Alert System for Non-food Products (RAPEX) released 30 pieces of information on Chinese shoes and toy products are recalled by Germany, Spain and France because of containing DMF.Jincheng residential working group of Shanxi Inspection and Quarantine Bureau received a report from an enterprises on March 28, 2009, saying that the a number of tractor spare parts exporting to Italian, using wooden packaging due to have provide no `free DMF` proof is curbed.Guanzhou Fangchun`s packaging materials manufacturer suffered from total return and reproduction on July 2009, because DMF is contained in its products.In recent years, why Green trade barrier is used with increasing frequency in wider fields, there is a deep-rooted reason behind it. For instance, the world environmental degradation, such as: ozone depletion, global warming, biodiversity loss and other problems which directly affect people`s consumption concept and values; particularly in Europe and the United States and other developed countries, consumers` green values have been formed and show their demands and preferences towards green products, which also provided the conditions and opportunities for the formation of the green trade barriers. In addition, the traditional non-tariff is increasingly being condemned, in such a case, European, American and other countries for their own interests began to seek new trade protection measures. Moreover, differences innational environmental standards, as well as the current international trade rules and agreements are incomplete provids an excuse for the green trade barriers.Director of Secretariat of China Certification Committee for Environmental Labeling Products, Professor Xia Qing expresses that `green trade barrier` is unavoidable, any country in term of protecting national security, animal and plant safety, public health, environment, and preventing fraud, will draw up relevant provisions, release relevant rules and regulations, and adopt technical preventive measures. They propose testing standards in their provisions, which constitute a series of possible `green barriers`. However, there are differences in `green standard` itself, which cause the EU products is liable to be exported, while some Chinese product can`t go to international market.Erected `Green Barrier` and Intensified Trade Friction In the process of global economic integration, in order to achieve the purpose of protecting the domestic market, the EU and other developed countries resort more and more hidden measures, the technical requirements for imported products become increasingly stringent, and the supporting laws and regulations are issued one after another. For example: since June 2007, the EU fully implemented REACH regulations requiring enterprises to apply for authorization, notify 15-item highly concerned materials (SVHC); in June 2008, the EU issued a `PFOS order` restricting the use of perfluorooctane sulfonate compounds (PFOS), marked the EU officially bans usage of PFOS in the commodities; for which China`s several exporting industries are effected including the textile, leather and other export enterprises. The implementation of DMF ban to serves as another green trade barrier for China`s leather, furniture and other export industries.The EU member states take the name of environmental protection to launch unilateral trade measures to restrict imports from foreign countries, thus lead to an increasing bilateral or multilateral trade friction. The two large regional organizations of the EU and the North American Free Trade Area member states are basically developed countries, their environmental protection level and environmental standards are similar, while certain gaps between individual member states also tend to be coordinated. So they can adopt regional free trade mode to curb the outside region products due to not in accordance with their environmental standards.While the seemingly legitimate green barrier is becoming popular, it may pose serious challenges towards the developing countries. According to rough statistics, among China`s suffering green barrier, 66.1% of that comes from the European Union, this trend may exertlong-term influence on China-EU trade and economic relationship.Response `Green Trade Barrier` Positively and Objectively What China and other developing countries should do in the context of financial crisis, and as the `green trade barriers` is intensified? According to relevant insiders that China`s foreign trade enterprises should be prepared `in the near-medium-long term`. In the near term, they have to actively respond to suits, there are relevant professionals in the municipal Foreign Economic Trade Bureau, CCPIT, as well as industry associations, who can help to contact lawyers, and coordinate to make preparation for responding to suits. In the medium-term, they have to speed up the reserves of foreign trade talents, especially nowadays the trade barriers change frequently, which proposes higher requirements of professional quality of the foreign trade talents. In the long term, exporting enterprises should intensify efforts to adjust product structure, speed up industrial upgrading, improving product technology content, so as to reduce trade friction fundamentally. It is reported that Chinese government are sharing difficulties and help the enterprises to solve the problems; organized by the Ministry of Commerce, local functional departments actively play the `four-body interaction` mechanism role to face trade frictions with business associations and enterprises; strengthening the advocacy of training and legal advice of trade frictions to enterprises, as well as having done lots of effort to help the enterprises to use legal means to actively respond to suits.Actually, from the prospect of environmental protection and national health care, the so-called new barriers including green barrier and intellectual property protection also had a reasonable side, which may urge enterprise to promote the optimization and upgrading of the industrial structure.` Another insider believes that take Haier as an example: from the late 1980s to early 1990s, due to European, American and other developed countries make legislation to restrict or to prohibit imports of refrigerators containing CFC, which makes China`s refrigerator export suffer heavy loss, Haier Group is also no exception. Then Haier Refrigerator launches a `green revolution` in a timely manner. In 1984, Haier Group introduced both German technology and a high level of environmental awareness in Germany, and constantly strived to reduce CFC usage until the Freon-free refrigerators is created; meanwhile the Freon-free refrigerators also has significant energy saving function, surpassing European standards A - 20% energy-saving, and the U.S. 18% energy-saving. As a result, Haier Group has made the EU`s `Green Label certificate` in the early 1990s, and passed the ISO9001 and ISO14000 system certificates in 1992 and 1996 successively. Owning to adopting a series of green measures, Haier Group products has met the environmental requirements of importingcountries, reversing small exporting market and exporting volume prior to 1990; in 1996 Haier Group exported 210,000 units refrigerators, amounting to 25.71 million dollars, thereby laying a foundation of first exporting position in China`s domestic market, and ranking first in Asia to export to Germany, all of which is conducive for Haier Group to crowd in the national top 500 enterprises list.Influences of Green barriers on China's foreign trade China has suffered great loss due to the "Green barriers". In 2002, vegetables from Taizhou were prevented from entering Japan because of Japanese strict inspection and the price was greatly cut down. Also in 2002, the aquatic products from Ningbo were restricted by European Union (EU) because they could not reach the sanitary standards of EU. Due to Green trade barriers, 60 kinds of Chinese agricultural chemists were banned by EU because they could not reach the Green standards of EU. In accordance with the statistics of United Nations, China has suffered a loss of $7.4 billion in 2002 due to "Green barriers trade". China's export to EU, Japan, Korea and other countries decreases notably. Generally speaking, agricultural products and foodstuff, textile products and mechanical and electronic products are the three main industries which suffer great loss because of the strict Green barriers. Since these three products constitute the majority of Chinese exportation, we can easily draw a conclusion: "Green barriers to trade" has become one of the major obstacles in Chinese exportation.Countermeasures to the Green barriers of the developed countriesAs mentioned above, it is a fact that the Chinese export products are facing Green barriers of the developed countries and has suffered great loss. Therefore Chinese exporters should think carefully about the countermeasures to eliminate the unfavorable influences of such measures. First, we should make full use of the preferential treatment to the developing countries stipulated in the Agreement of Green trade barrier. According to the provisions of the Agreement of Green trade barrier, developed countries should take account of the special development, financial and trade needs of developing country members with a view to ensuring that such Green regulations, standards and conformity assessment procedures do not create unnecessary obstacles to exports from developing countries. So, as a developing member of WTO, China is entitled to such preferential treatment. Secondly, China should make use of the Dispute Settlement System of WTO to protect her interests. Different from GATT, WTO has set up a powerful dispute settlement system to solve the disputes between the members of WTO. So, if our interests are harmed by the unfair Green barriers of other WTO members, we can resort to Dispute Settlement Body to settle this dispute and urge other members to change their unfair practices so as to protect our interests. Thirdly, China should stress the protection of environment and take measures to improve the quality and Green level of her export products to meet higher Green standards, which will fundamentally solve the problem of Green barriers.Source:EUROPECHINA 2009-10-25。