Using Contingent Valuation to Estimate a Neighborhood’s Willingness to Pay to Preserve Und
关于财务管理的英文单词
记帐:Bookkeeping Service对帐:Auditing Service联行:Associated Banks Service 或Affiliated Banks Service(我还是不明白这与5有何区别,但Associated和Affiliated不是动词原形,是形容词)代理业务: Agency Service银行卡接柜:Inter-Bank Bankcard Business Service现金审批:Cash Approval Service开销户: Account Opening/Closing Service开户的标牌还可以用:New Account/New Clientbig macs, big/large-cap stock, mega-issue 大盘股offering, list 上市bourse 证交所Shanghai Exchange 上海证交所pension fund 养老基金share 股票valuation 股价underwriter 保险商government bond 政府债券saving account 储蓄账户equity market 股市shareholder 股东delist 摘牌inventory 存货traded company, trading enterprise 上市公司market fundamentalist 市场经济基本规则damage-control machinery 安全顾问efficient market 有效市场opportunistic practice 投机行为entrepreneur 企业家cook the book 做假账regulatory system 监管体系portfolio 投资组合money-market 短期资本市场capital-market 长期资本市场volatility 波动diversification 多元化real estate 房地产option 期权call option 看涨期权put option 看跌期权merger 并购arbitrage 套利Securities and Exchange Commission 〈美〉证券交易委员会dollar standard 美元本位制budget 预算deficit 赤字bad debt 坏账macroeconomic 宏观经济fiscal stimulus 财政刺激a store of value 保值transaction currency 结算货币forward exchange 期货交易intervention currency 干预货币Treasury bond 财政部公债pickup in price 物价上涨Federal Reserve 美联储inflation 通货膨胀deflation 通货紧缩tighter credit 紧缩信贷monetary policy 货币政策foreign exchange 外汇spot transaction 即期交易forward transaction 远期交易quote 报价常见银行英语词汇account number 帐目编号depositor 存户pay-in slip 存款单a deposit form 存款单a banding machine 自动存取机to deposit 存款deposit receipt 存款收据private deposits 私人存款certificate of deposit 存单deposit book, passbook 存折credit card 信用卡principal 本金overdraft, overdraw 透支to endorse 背书endorser 背书人to cash 兑现to honor a cheque 兑付to dishonor a cheque 拒付to suspend payment 止付cheque,check 支票cheque book 支票本crossed cheque 横线支票blank cheque 空白支票rubber cheque 空头支票cheque stub, counterfoil 票根cash cheque 现金支票traveler's cheque 旅行支票cheque for transfer 转帐支票outstanding cheque 未付支票canceled cheque 已付支票forged cheque 伪支票Bandar's note 庄票,银票banker 银行家president 行长savings bank 储蓄银行Chase Bank 大通银行National City Bank of New York 花旗银行Hongkong Shanghai Banking Corporation 汇丰银行Chartered Bank of India, Australia and China 麦加利银行Banque de I'IndoChine 东方汇理银行central bank, national bank, banker's bank 中央银行bank of issue, bank of circulation 发行币银行commercial bank 商业银行,储蓄信贷银行member bank, credit bank 储蓄信贷银行discount bank 贴现银行exchange bank 汇兑银行requesting bank 委托开证银行issuing bank, opening bank 开证银行advising bank, notifying bank 通知银行negotiation bank 议付银行confirming bank 保兑银行paying bank 付款银行associate banker of collection 代收银行consigned banker of collection 委托银行clearing bank 清算银行local bank 本地银行domestic bank 国内银行overseas bank 国外银行unincorporated bank 钱庄branch bank 银行分行trustee savings bank 信托储蓄银行trust company 信托公司financial trust 金融信托公司unit trust 信托投资公司trust institution 银行的信托部credit department 银行的信用部commercial credit company(discount company) 商业信贷公司(贴现公司)neighborhood savings bank, bank of deposit 街道储蓄所credit union 合作银行credit bureau 商业兴信所self-service bank 无人银行land bank 土地银行construction bank 建设银行industrial and commercial bank 工商银行bank of communications 交通银行mutual savings bank 互助储蓄银行post office savings bank 邮局储蓄银行mortgage bank, building society 抵押银行industrial bank 实业银行home loan bank 家宅贷款银行reserve bank 准备银行chartered bank 特许银行corresponding bank 往来银行merchant bank, accepting bank 承兑银行investment bank 投资银行import and export bank (EXIMBANK) 进出口银行joint venture bank 合资银行money shop, native bank 钱庄credit cooperatives 信用社clearing house 票据交换所public accounting 公共会计business accounting 商业会计cost accounting 成本会计depreciation accounting 折旧会计computerized accounting 电脑化会计general ledger 总帐subsidiary ledger 分户帐cash book 现金出纳帐cash account 现金帐journal, day-book 日记帐,流水帐bad debts 坏帐investment 投资surplus 结余idle capital 游资economic cycle 经济周期economic boom 经济繁荣economic recession 经济衰退economic depression 经济萧条economic crisis 经济危机economic recovery 经济复苏inflation 通货膨胀deflation 通货收缩devaluation 货币贬值revaluation 货币增值international balance of payment 国际收支favourable balance 顺差adverse balance 逆差hard currency 硬通货soft currency 软通货international monetary system 国际货币制度the purchasing power of money 货币购买力money in circulation 货币流通量note issue 纸币发行量national budget 国家预算national gross product 国民生产总值public bond 公债stock, share 股票debenture 债券treasury bill 国库券debt chain 债务链direct exchange 直接(对角)套汇indirect exchange 间接(三角)套汇cross rate, arbitrage rate 套汇汇率foreign currency (exchange) reserve 外汇储备foreign exchange fluctuation 外汇波动foreign exchange crisis 外汇危机discount 贴现discount rate, bank rate 贴现率gold reserve 黄金储备money (financial) market 金融市场stock exchange 股票交易所broker 经纪人commission 佣金bookkeeping 簿记bookkeeper 簿记员an application form 申请单bank statement 对帐单letter of credit 信用证strong room, vault 保险库equitable tax system 等价税则specimen signature 签字式样banking hours, business hours 营业时间(Consumer Price Index) 消费者物价指数business 企业商业业务financial risk 财务风险sole proprietorship 私人业主制企业partnership 合伙制企业limited partner 有限责任合伙人general partner 一般合伙人separation of ownership and control 所有权与经营权分离claim 要求主张要求权management buyout 管理层收购tender offer 要约收购financial standards 财务准则initial public offering 首次公开发行股票private corporation 私募公司未上市公司closely held corporation 控股公司board of directors 董事会executove director 执行董事non- executove director 非执行董事chairperson 主席controller 主计长treasurer 司库revenue 收入profit 利润earnings per share 每股盈余return 回报market share 市场份额social good 社会福利financial distress 财务困境stakeholder theory 利益相关者理论value (wealth) maximization 价值(财富)最大化common stockholder 普通股股东preferred stockholder 优先股股东debt holder 债权人well-being 福利diversity 多样化going concern 持续的agency problem 代理问题free-riding problem 搭便车问题information asymmetry 信息不对称retail investor 散户投资者institutional investor 机构投资者agency relationship 代理关系net present value 净现值creative accounting 创造性会计stock option 股票期权agency cost 代理成本bonding cost 契约成本monitoring costs 监督成本takeover 接管corporate annual reports 公司年报balance sheet 资产负债表income statement 利润表statement of cash flows 现金流量表statement of retained earnings 留存收益表fair market value 公允市场价值marketable securities 油价证券check 支票money order 拨款但、汇款单withdrawal 提款accounts receivable 应收账款credit sale 赊销inventory 存货property,plant,and equipment 土地、厂房与设备depreciation 折旧accumulated depreciation 累计折旧liability 负债current liability 流动负债long-term liability 长期负债accounts payout 应付账款note payout 应付票据accrued espense 应计费用deferred tax 递延税款preferred stock 优先股common stock 普通股book value 账面价值capital surplus 资本盈余accumulated retained earnings 累计留存收益hybrid 混合金融工具treasury stock 库藏股historic cost 历史成本current market value 现行市场价值real estate 房地产outstanding 发行在外的a profit and loss statement 损益表net income 净利润operating income 经营收益earnings per share 每股收益simple capital structure 简单资本结构dilutive 冲减每股收益的basic earnings per share 基本每股收益complex capital structures 复杂的每股收益diluted earnings per share 稀释的每股收益convertible securities 可转换证券warrant 认股权证accrual accounting 应计制会计amortization 摊销accelerated methods 加速折旧法straight-line depreciation 直线折旧法statement of changes in shareholders’equity 股东权益变动表source of cash 现金来源use of cash 现金运用operating cash flows 经营现金流cash flow from operations 经营活动现金流direct method 直接法indirect method 间接法bottom-up approach 倒推法investing cash flows 投资现金流cash flow from investing 投资活动现金流joint venture 合资企业affiliate 分支机构financing cash flows 筹资现金流cash flows from financing 筹资活动现金流time value of money 货币时间价值simple interest 单利debt instrument 债务工具annuity 年金future value 终至present value 现值compound interest 复利compounding 复利计算pricipal 本金mortgage 抵押credit card 信用卡terminal value 终值discounting 折现计算discount rate 折现率opportunity cost 机会成本required rate of return 要求的报酬率cost of capital 资本成本ordinary annuity普通年金annuity due 先付年金financial ratio 财务比率deferred annuity 递延年金restrictive covenants 限制性条款perpetuity 永续年金bond indenture 债券契约face value 面值financial analyst 财务分析师coupon rate 息票利率liquidity ratio 流动性比率nominal interest rate 名义利率current ratio 流动比率effective interest rate 有效利率window dressing 账面粉饰going-concern value 持续经营价值marketable securities 短期证券liquidation value 清算价值quick ratio 速动比率book value 账面价值cash ratio 现金比率marker value 市场价值debt management ratios 债务管理比率intrinsic value 内在价值debt ratio 债务比率mispricing 给……错定价格debt-to-equity ratio 债务与权益比率valuation approach 估价方法equity multiplier 权益乘discounted cash flow valuation 折现现金流量模型long-term ratio 长期比率undervaluation 低估debt-to-total-capital 债务与全部资本比率overvaluation 高估leverage ratios 杠杆比率option-pricing model 期权定价模型interest coverage ratio 利息保障比率contingent claim valuation 或有要求权估价earnings before interest and taxes 息税前利润promissory note 本票cash flow coverage ratio 现金流量保障比率contractual provision 契约条款asset management ratios 资产管理比率par value 票面价值accounts receivable turnover ratio 应收账款周转率maturity value 到期价值inventory turnover ratio 存货周转率coupon 息票利息inventory processing period 存货周转期coupon payment 息票利息支付accounts payable turnover ratio 应付账款周转率coupon interest rate 息票利率cash conversion cycle 现金周转期maturity 到期日asset turnover ratio 资产周转率term to maturity 到期时间profitability ratio 盈利比率call provision赎回条款gross profit margin 毛利润call price 赎回价格operating profit margin 经营利润sinking fund provision 偿债基金条款net profit margin 净利润conversion right 转换权return on asset 资产收益率put provision 卖出条款return on total equity ratio 全部权益报酬率indenture 债务契约return on common equity 普通权益报酬率covenant 条款market-to-book value ratio 市场价值与账面价值比率trustee 托管人market value ratios 市场价值比率protective covenant 保护性条款dividend yield 股利收益率negative covenant 消极条款dividend payout 股利支付率positive covenant 积极条款financial statement财务报表secured deht担保借款profitability 盈利能力unsecured deht信用借款viability 生存能力creditworthiness 信誉solvency 偿付能力collateral 抵押品collateral trust bonds 抵押信托契约debenture 信用债券bond rating 债券评级current yield 现行收益yield to maturity 到期收益率default risk 违约风险interest rate risk 利息率风险authorized shares 授权股outstanding shares 发行股treasury share 库藏股repurchase 回购right to proxy 代理权right to vote 投票权independent auditor 独立审计师straight or majority voting 多数投票制cumulative voting 积累投票制liquidation 清算right to transfer ownership 所有权转移权preemptive right 优先认股权dividend discount model 股利折现模型capital asset pricing model 资本资产定价模型constant growth model 固定增长率模型growth perpetuity 增长年金mortgage bonds 抵押债券。
离散选择实验应用于2型糖尿病患者治疗偏好的文献分析
离散选择实验应用于2型糖尿病患者治疗偏好的文献分析作者:刘世蒙李顺平杨毅唐程翔陈英耀来源:《中国药房》2020年第20期摘要目的:为2型糖尿病患者的临床治疗和药物经济学研究提供参考。
方法:以“离散选择”“糖尿病”“Discrete choice”“Discrete ranking”“Conjoint analysis”“Diabetes mellitus”“Type2”“Type 2 diabetes mellitus”“Non-insulin-dependent diabetes mellitus”等为关键词,收集自建库起至2019年12月在中国知网、万方、PubMed、Web of Science等国内外数据库中发表的中英文文献,从属性与水平、DCE选项集、数据质量、样本量、计量经济学分析以及患者偏好结果等6个方面对离散选择实验(DCE)在2型糖尿病患者治疗偏好领域中的应用情况进行梳理总结。
结果与结论:共检索到相关文献295篇,其中有效文献30篇。
药物管理、血糖控制和低血糖事件是被纳入次数较多的属性;通常采用D-高效设计、D-最优设计或正交设计生成DCE选项集;问卷数据质量可通过问卷内部效度进行检验;样本量一般使用拇指法则进行计算;条件Logit模型、多项Logit模型以及混合Logit模型是最常使用的数据分析模型。
相较于轻微的低血糖事件,患者的治疗选择更容易受血糖控制的影响,但当低血糖事件发生在夜间或者程度较重时,患者的治疗偏好往往会发生改变;多数研究纳入了药物管理相关属性,但其并非影响患者治疗偏好的主要因素,且与患者既往服药史密切相关。
DCE已被广泛应用于国外2型糖尿病的相关研究中,但在我国应用不多。
DCE的数据质量较难控制,虽然构建复杂计量经济学模型的趋势在逐渐上升,但多数研究仍未就样本量确定方法、选项集设计原理、质量控制选项等设计细节予以充分的介绍,且部分研究存在属性數量过多、水平间距过大或过小等不足。
5 _Forest-Policy-and-Economics
Economic impact of enlarging the area of protected forests in EstoniaRisto Sirgmets ⁎,Paavo Kaimre,Allar PadariInstitute of Forestry and Rural Engineering,Estonian University of Life Sciences,Kreutzwaldi 5,Tartu 51014,Estoniaa b s t r a c ta r t i c l e i n f o Article history:Received 27January 2010Received in revised form 27September 2010Accepted 22November 2010Available online 15January 2011Keywords:Nature conservationEconomic impact assessment Forest policy implementationThe article deals with the economic impact of increasing strictly protected forest areas from the current 8.2%level up to 10%from the total forest area in Estonia.Whereas there is no concrete selection of areas added in the group of strictly protected forests,the impact on annual lost income due to forest management not carried out in protected forests was assessed according to two different assumptions:1.changing the status of forests without management restrictions (formal commercial forests)into the strictly protected ones;2.changing the status of forests with management restrictions (formal protection forests)into the strictlyprotected ones.Achieving the target set by the Estonian Forest Development Programme,increasing the share of strictly protected forests up to 10%,an additional 39,000ha of forest land will be out of management.Increasing the conservation area by 1.8%by forests without management restrictions,the reduction in potential net revenue will be 2%per year.Achieving the goal by conserving the forests with management restrictions,the total income will decrease by 0.76–1.9%per year.To realize the goal set by the Estonian Forestry Development Programme until 2010and 2020to enlarge the protected forest area up to 10%from one side,and the current economic recession on the other side,the economic solution could be enlarging the conservation on forests with management restrictions.©2011Elsevier B.V.All rights reserved.1.IntroductionOne characteristic trend in European forestry during the last decades is the increasing importance of non-timber values including nature protection.Between 1995and 2005,the share of forests providing environmental and protective services has increased from 4%to 10%and 4.7%of the forests are having strict environmental restrictions (FAO,2007;MCPFE,2007).Forest protection in Estonia is regulated by the Act of Nature Conservation and by the Forest Act.According to the Forest Act redaction which was in force until 01.01.2009Estonian forests were divided according to the management targets in three categories —protected forests,protection forests and commercial forests (Metsaseadus,2006).The only target in forests which belonged in the protected forest category was nature conservation where no economic activity was allowed.Special conservation areas,strict nature reserves and special management zones belonged in protected forests.In protected forests the economic activity was completely forbidden whereas in the forests belonging in the protected forest category the main goal was to protect the environment and the economic activitywas allowed according to the management plan of a speci fic protection area.Limited management zones belonged in protection forests.All forms of forest use were allowed in forests which belonged in the commercial forest category.The income from forest management is the main target in commercial forests.According to the new redaction of Forest Act (in force since 01.01.2009)aforementioned concepts of forest categories are not in use.In Estonia the protection of formal protected and protected forests is regulated by the Act of Nature Conservation (Looduskaitseseadus,2004).The protection of valuable key-habitats in commercial forests is regulated by the Forest Act and is based on voluntary agreements.The agreement with the forest owner is settled for 20years and lost income from forest management will be compensated.Approximately 31%of Estonian forest land is covered with man-agement restrictions.Strictly protected forests in Estonia cover an area of 182,300ha,which makes 8.2%of the total forest area (Keskkonnaministeerium,2009).The number is relatively big compared to other European countries,but according to Estonian Forest Development Programme it does not ensure the preservation of forest biodiversity,characteristic forest types and ecosystems.The Estonian Forestry Development Programme until 2010says that the preservation of biodiversity and the protection of natural values assume the undisturbed development of a part of the forests and the implementation of measures for the protection of biodiversity in theForest Policy and Economics 13(2011)155–158⁎Corresponding author.Tel.:+3725259499.E-mail address:risto.sirgmets@emu.ee (R.Sirgmets).1389-9341/$–see front matter ©2011Elsevier B.V.All rights reserved.doi:10.1016/j.forpol.2010.11.006Contents lists available at ScienceDirectForest Policy and Economicsj o u r n a l h o m e p a g e :w ww.e l s ev i e r.c o m /l o c a t e /fo r p o lrest(Keskkonnaministeerium,2002).The objectives set in the programme are based on consensus,which expresses the readiness of the society to give up the income from forest management for environmental values.But on the other hand,the opportunity cost of the forest conservation has not yet been calculated.The increase of area of protected forests up to10%acts also as a tool in preserving biodiversity and forest ecosystems.The enlargement of the area of protected forests is an important decision in forest policy.To estimate its relevant impact it is also essential to take into consideration social and economic aspects besides the environmental ones.Despite being an important issue in Estonian forestry,the social and economic impact of nature protection has not been discussed significantly.Economic impacts of nature protection and economic evaluation of biodiversity are one part of the Estonian forest sector macromodel in which the design started in2003by Hepner and Kosenkranius but is still under construction.The aim of designing an Estonian forest sector macromodel is to create simulations for weighting macroeconomic indicators(employment,GDP,tax receipts, consumption,and forest trade)and indicators of sustainable devel-opment(carbon balance,biodiversity,and social capital)necessary in economic decision-making(Hepner and Kosenkranius,2003).The prevailing issue in Estonia has been the evaluation of mon-etary value of some certain nature protected areas and semi-natural ecosystems.Habicht and Ehrlich(2000)have assessed the monetary value of Matsalu Nature Protection area(48,610ha)in1999.They assumed that the sum of different expenditures(expenditures made by visitors,domestic and foreign subsidies)expresses the value of Matsalu Nature Protection area.Summing all afore-mentioned ex-penditure categories the aggregate monetary value of Matsalu Nature Protection area by Habicht and Ehrlich was approximately 350,000Euros(7.2EUR/ha).Ehrlich(2007)has also assessed the value of Estonian semi-natural ecosystems through the willingness to pay measure using the contingent valuation method.The willingness of the Estonian working-age population to pay for the preservation of seminatural communities was assessed and the calculated monetary value was approximately8.3million Euros.An economic impact on the forest sector of increasing forest biodiversity conservation has gained more attention in Finland. Hänninen and Kallio(2007)have analysed economic consequences on the Finnish forest sector of conserving additional0.5%to5%of the old growth forest land in Southern Finland.They analysed the impacts on supply,demand and prices of wood and forest industry production employing a partial equilibrium model of the Finnish forest sector. Kniiviläet al.(2002)have studied the opportunity costs of forest conservation in a local economy in Eastern Finland.They focused on identifying,assessing and comparing the benefits and costs related to forest conservation at the local and regional level.Besides that the economic impact of increasing the area of strictly protected forests has gained much attention due to Natura2000 network,Pouta et al.(2000)have used contingent valuation to calculate the average willingness to pay for the Natura2000network,which is also compared to the costs of the conservation programme.Leppänen et al.(2005)have studied the lost income in Southern Finland due to Natura2000network.Empirical study revealed that during the next decade the state has to compensate1billion Euros per1%of the total forest area turned from commercial forests into protected ones.Kallio et al.(2006)have studied the impact of enlarging the area of protected forests in the European forest sector.Scenarios with either 3%or5%of the productive forest stock in Western Europe set-aside for conservation are compared to a baseline case.The scenarios are created by employing a global forest sector model,EFI–GTM.The increase of nature protection areas by5%will decrease the harvesting volumes and may cause the growth in timber prices.As a result the investments into timber processing and the level of employment will decline.Verkerk et al.(2008)have made similar conclusions assessing the influence of restrictions to harvesting volumes in Europe.Bolkesjøet al.(2005)analysed the impact on timber and forest products of increasing forest conservation in Norway using the partial equilibrium forest sector model.The article deals with the economic impact of increasing strictly protected forest areas up to10%from the total forest area in Estonia. The impact on annual lost income due to forest management not carried out in protected forests was assessed according to two dif-ferent assumptions.2.Material and methodsEven though the goal to increase the area of strictly protected forests up to10%of the Estonian forest area is set by the Estonian Forest Development Programme until the year2010,there is no concrete selection of areas added in the group of strictly protected forests. Therefore two assumptions were made in order to evaluate the economic impact of enlarging the area of strictly protected forests in Estonia:1.changing the status of forests without management restrictions(formal commercial forests)into the strictly protected ones;2.changing the status of forests with management restrictions(formal protection forests)into the strictly protected ones.Atfirst,assessing the economic impact of increasing the territory of protected areas,the annual potential long term average income of forest management in forests with different protection regimes per hectare was calculated,not considering the restrictions set in protected forests and in forests with different management restric-tions.This means that the calculation was made presuming that all forests are managed100%similarly to commercial forests.For calculations the theoretical long term average annual produc-tion of assortments by forest site types and quality classes was calculated,using the methodology which has been used previously by Padari and Muiste(2003)and Padari et al.(2009).The State Registry of Forest Data contains the information about Estonian forest inventory data.Unfortunately it contains only67%of Estonian forests.Therefore the calculations of theoretical long term average annual production per hectare of Estonian forests were done on the basis of the inventory data available in the State Registry of Forest Data.Theoretical long term average annual production(m3/ha) by site types and quality classes was obtained as a result of calculations which were expanded to all Estonian forests.On the ground of afore-mentioned calculations the potential long term annual income of all Estonian forests was ing average unit prices of activities in the State Forest Management Centre(Table1),cultivation costs by different species(Table2)and average road side prices of round-wood in the State Forest Management Centre(Table3)(Keskkonnaministeerium,2009).There are different reasons for management restrictions according to the data of the State Registry of Forest Data which can be seen in Table4.In Table4there can also be seen the distribution of forest area by reasons of protection and the percentage of potential income compared to the forests with no management restrictions in the same site conditions.Table1Unit cost of management activities in the State Forest Management Centre in2007. Activity Unit CostSoil scarification EUR/ha77.6 Tending of plantations EUR/ha59.5 Tending of young stands EUR/ha107.7 Thinning EUR/m315.2 Regeneration felling EUR/m38.6156R.Sirgmets et al./Forest Policy and Economics13(2011)155–158Estimating the potential income in forests,where some kind of regeneration felling(e.g.shelterwood cutting)is allowed,100%of potential income compared to forests without management restric-tions was used.In forests where only sanitation cutting for removing dead trees was allowed,0%was used for estimating potential income. 50%was used for estimating the potential income of forest areas of which the reason of restrictions in the database of State Registry of Forest Data was noted as“other reasons”,taking into consideration that regeneration felling is allowed approximately in half of these areas.The share of these areas was about1.5%with forests of no management restrictions and about6%without forests of no management restrictions of the forest area consisted in the State Registry of Forest Data(Table5).Finally the potential lost income from forest management due to increase of strictly protected forest areas up to10%was calculated according to aforementioned assumptions(Table6).To sum up the method of calculations:inventory data of stands, growth models,forest management models,forest management costs and timber prices were considered to assess annual net revenue of forest management.3.ResultsAssessing the potential net revenue from forest management in forests with different protection regime,the following results were got on the basis of the forest inventory data from Estonian State Registry of Forest Data,covering about67%of Estonian forests: Commercial forests:131EUR/ha year−1Forests with management restrictions:100%manageable:122EUR/ha year−150%manageable:100EUR/ha year−1Strictly protected forests:106EUR/ha year−1.The results reveal that the economic potential of environmentally more valuable stands is lower than in commercial forests.It is due to the fact that strictly protected stands are mostly overmatured mixed stands,where timber quality is lower because of its age.The results of calculation made with the forest inventory data from the Estonian State Registry of Forest Data were expanded for the whole Estonia.In addition to commercial forests,the data of forests with management restrictions were included into the calculations. Strictly protected forests were excluded from calculations because any forest management is prohibited in these areas.According to the calculations,the potential annual harvest volume at the current protection level in Estonia would be about11.3million m3and the potential annual net revenue from forest management is approximately255.8million EUR.At the moment8.2%(182,300ha)of Estonian forests are under strict protection.Achieving the target written down in the Estonian Forestry Development Programme,increasing the area of strictly protected forests at least to10%of the total forest area,means that approximately39,000ha of forest land will be out of management.According to thefirst assumption changing the status of com-mercial forests into the strictly protected ones up to10%of the total forest area,the annual harvest volume decreases by2%(226,000m3) and annual net revenue from forest management decreases approx-imately2%(5.1million EUR)per year.The second assumption,in changing the status of forests with management restrictions into the strictly protected ones,there are different possibilities.Atfirst,turning the areas,where management restrictions decrease potential annual net revenue by50%into the strictly protected ones,decreases the annual harvest volume by0.4% (46,000m3)and the annual potential net revenue decreases0.8% (2million EUR)per year.Changing the status of forests which have management restrictions,but forest management is still completely possible there,into the strictly protected ones decreases the annual harvest volume by 1.8%(206,000m3).The potential annual net revenue decreases by1.9%(4.8million EUR).The summary of the results can be seen in Table3.4.DiscussionThe paper introduces the economic impact of the goal set in Estonian Forestry Development Programme until2010and2020Table2Cultivation costs by different species.Species Unit CostScots pine(Pinus sylvestris)EUR/ha621.3 Norway spruce(Picea abies)EUR/ha550.3 Birch(Betula sp.)EUR/ha507Table3Average road side prices of round-wood by the State Forest Management Centre in 2005–2009.Assortment EUR/m3Pine logs59.1Pine logs d b18cm51.8 Spruce logs55.5 Spruce logs d b18cm50.1 Birch logs83.2 Birch logs d b18cm53.3 Aspen logs32.8Pine pulpwood29.2 Spruce pulpwood30.5 Birch pulpwood30.6 Aspen pulpwood12.7 Fuelwood17.0Table4The area of restricted areas by the reasons of restrictions(State Registry of Forest Data).Reason of restrictions Area(ha)Potential incomecompared tocommercial forests(%)Strict nature reserve12,695.60Special management zone120,644.90Limited management zone73,449.8100Special conservation area74.90Individual item25.30A protected natural object onlocal government level47,268.30Special management zone of habitat5721.90Limited management zone of habitat2328.0100Shores71,162.5100Heaths,erosion and wind hazardous areas23,197.1100Forest areas with infiltration or pressuredground-water10,383.2100National heritage area504.00Gene reserve17.8100Others24,037.950Total391,511.2Table5Forest area by potential income(State Registry of Forest Data).Potentialincome(%)Area withcommercialforests(ha)Relativeimportance(%)Area withoutcommercialforests(ha)RelativeImportance(%)0186,934.911.6186,934.947.8 5024,037.9 1.524,037.9 6.1 1001,401,265.186.9180,538.446.1Total1,612,237.9100.0391,511.2100.0157R.Sirgmets et al./Forest Policy and Economics13(2011)155–158increasing the percentage of strictly protected forests from current state up to10%of the total forest area,accordingly39,000ha.Lost potential net revenue from forest management as a result of nature conservation was calculated.The study indicated that different forest categories give remark-ably different calculated net revenue.The average long-run net revenue in commercial forest is131EUR per hectare,in forests with management restrictions accordingly100(50%)and122(100%)EUR per hectare which makes a difference of24%and7%.In total,increasing the conservation area by1.8%by commercial forests,the reduction in potential net revenue will be2%.Achieving the goal by conserving the forests with management restrictions,the total income will decrease by0.76–1.9%.The stands with high nature value are located both in public as well in private forests.In2008,13.8%of state owned forests and5.1% of forests belonging to other owners were strictly protected (Keskkonnaministeerium,2009).Non-industrial private forest own-ers have certain reimbursement expectation related to forest management restrictions.It means that if the Estonian society has decided to apply management restrictions on additional1.8%forest land,causing a deduction of forest revenue to forest owners,the society has to consider withfinancial compensation to owners.The last aspect is considered also in the Estonian Forest Policy. According to the Estonian Forestry Development Programme until 2010and2020,the increase of strictly protected forests is planned to be achieved in state forests.In other forests the conservation will be achieved by voluntary agreement between owner and Ministry of Environment.If restrictions are applied on the forest management in the public interests,the government can win the support of private forest owners applying variousfinancial incentives.In the Estonian Rural Development Programme2007–2013financial support for private forestry is available,e.g.support for Natura2000area.The aim of the support is to compensate the lost income from forest management.In 2009the compensation was110EUR/ha or60EUR/ha depending of the strictness of the protecting regime.While many areas with management restrictions do not belong to Natura network,another alternative support measures should be developed and implemented by policy makers and forest officers.The measures based on private initiative and voluntary agreements could be an opportunity to promote and develop the nature protection amongst Estonian forest owners.In the paper,the influence of forest conservation on the potential net revenue,related only to forest management,was studied.Obviously,the expanding of protected forest area is influencing not only the forest management but also the whole Estonian forest sector.Similar conclusions gave studies made in other countries and published by Kallio et al.(2006)and Verkerk et al.(2008).In conclusion,to realize the goal set in the Estonian Forestry Development Programme until2010and2020to enlarge the protected forest area up to10%from one side,and the current economic recession on the other side,the economic solution could be enlarging the conservation on forests with management restrictions (formal protection forest),although,the main objective of forest conservation should be the protection of endangered species and ecosystems in forests.ReferencesBolkesjø,T.F.,Trømborg,E.,Solberg,B.,2005.Increasing forest conservation in Norway: consequences for timber and forest products markets.Environmental&Resource Economics31,95–115.Ehrlich,Ü.2007.Ecological Economics as a Tool for Resource Based Nature Conservation Management in Estonia.Dissertationes Geographicae Universitatis Tartuensis.Tartu University Press.Food,Agriculture Organization of the United Nations(FAO),2007.State of the World's Forests2007.Rome.Habicht,K.,Ehrlich,Ü.2000.Kaitsealade struktuur,majanduslik mõju ja väärtustatus Läänemaa näitel.Tallinn(in Estonian).Hänninen,R.,Kallio,A.M.I.,2007.Economic impacts on the forest sector of increasing forest biodiversity conservation in Finland.Silva Fennica41(3),507–523. Hepner,H.,Kosenkranius,E.,2003.Economic evaluation of biodiversity in the context of Estonian forest sector macromodel.Forestry Studies XXXIX.Forest ecosystems on coastal dunes of Southwest Estonia.Tallinn.Kallio, A.M.I.,Moiseyev, A.,Solberg, B.,2006.Economic impacts of increased forest conservation in Europe:a forest sector analysis.Environmental Science&Policy9, 457–465.Keskkonnaministeerium.2002.Eesti metsanduse arengukava aastani2010.Tallinn.31pp.(in Estonian).Keskkonnaministeerium,Metsakaitse-ja metsauuenduskeskus.2009.Aastaraamat Mets2008.Tartu.228p.(in Estonian).Kniivilä,M.,Ovaskainen,V.,Saastamoinen,O.,2002.Costs and benefits of forest conservation:regional and local comparisons in Eastern Finland.Journal of Forest Economics8,131–150.Leppänen,J.,Linden,M.,Uusivuori,J.,Pajuoja,H.,2005.The private cost and timber market implications of increasing strict forest conservation in Finland.Forest Policy and Economics7,71–83.Looduskaitseseadus[The Act of Nature Protection]2004.Riigi Teataja I2004,38,258.(In Estonian).Metsaseadus[The Forest Act]2006.Riigi Teataja I2006,30,232.(In Estonian). Ministerial Conference on the Protection of Forests in Europe(MCPFE),2007.State of Europe's forests2007.Padari,A.,Muiste,P.,2003.Analysis of maturity ages of Estonian forests.Baltic Forestry 9(2),16–19.Padari,A.,Muiste,P.,Mitt,R.,Pärn,L.,2009.Estimation of Estonian wood fuel resources.Baltic Forestry15(1),77–85.Pouta,E.,Rekola,M.,Kuuluvainen,J.,Tahvonen,O.,Li,C.-Z.,2000.Contingent Valuation of the Natura2000Nature Conservation Programme in Finland.Verkerk,P.,Zanchi,G.,Lindner,M.,2008.Impacts of biological and landscape diversity protection on the wood supply in Europe.European Forest Institute Technical Report,27.Table6The impact of increasing the share of strictly protected forests area into10%on forestmanagement net revenue.Harvest volume(m3)Potential net revenue(EUR/year)Current state11.3million255.8millionAssumption1−226,000−5.1millionAssumption2(50%)−46,000−2millionAssumption2(100%)−206,000−4.8million158R.Sirgmets et al./Forest Policy and Economics13(2011)155–158。
基于条件价值评估法的生态价值评估
基于条件价值评估法的生态价值评估作者:李劲彬来源:《绿色科技》2018年第08期摘要:条件价值评估法(contingent valuation method,CVM)是一种通过假想市场来进行生态系统服务评估和环境物品价值评估的方法,其对地方经济决策有着重要影响。
本文以西安曲江遗址公园为例,利用CVM进行城市绿地的生态价值量研究。
依据西安城市2010人口数据进行评估,结果显示曲江遗址公园在改善生态环境的同时,其每年的生态价值量大约为5608万元,其对今后西安市生态城市建设过程中经济决策具有一定的指导意义。
关键词:西安市;条件价值评估法:生态价值中图分类号:TU986文献标识码:A文章编号:1674-9944(2018)8-0013-021 引言曲江遗址公园与周边的曲江寒窑遗址公园、秦二世陵遗址公园以及唐城墙遗址公园等,共同形成了1500亩的大西安城市生态景观带,成为了人文西安的新标志,为古都西安实现城市现代化以及历史文化遗产保护树立了先进成功典型,同时也为西安市民以及周边城镇提供一个人文、休闲、娱乐、和谐生态的城市活动区。
曲江遗址公同占地1000多亩,水而而积700多亩,总投资19亿元人民币,是西安南郊集生态重建、休闲娱乐、观光旅游等功能为一体的生态涵养区。
绿地率作为衡量城市生态系统忧虑的重要指标,国外许多国家大城市都拥有高比例绿地面积,如伦敦人均公共绿地面积为24.6 m2,绿地率为42%左右;而据西安市公布的2005年绿化概况显示绿地率为31.89%。
人均公共绿地面积仅为5.04 m2,因此不难发现,西安无论在绿地率还是人均公共绿地面积上与其他国家大城市都存在很大差距。
依照《西安市“十一五”生态城市建设》规划纲要,西安市生态城市指标其人均公共绿地面积要大于11 m2,因而西安在城市绿地、城市公园项目建设存在很大空间以及迫切需求,因而曲江遗址公园作为已建成的最大的城市生态涵养区,运用科学手段和方法评估其生态服务价值,对于科学制定城市规划和建设生态城市[1]有着重要意义。
资产评估基本准则英文
资产评估基本准则英文Asset Valuation Basic GuidelinesAsset valuation is the process of determining the economic value of an asset. It involves assessing various factors such as the asset's physical condition, market demand, legal and regulatory environment, as well as any relevant economic factors. The following are some basic guidelines for conducting asset valuation: 1. Objectivity:Asset valuation should be conducted by independent professionals who have no personal interest in the outcome. This ensures objectivity and minimizes bias in the valuation process. Independent valuation experts should be knowledgeable and experienced in the valuation methods applicable to the specific asset class.2. Use of Appropriate Valuation Methods:Different valuation methods may be used depending on the nature of the asset being valued. Common valuation methods include market approach, income approach, and cost approach. The market approach relies on comparable transactions in the market to estimate the asset's value. The income approach uses the expected future income generated by the asset to determine its value. The cost approach calculates the asset's value based on the cost to replace it.3. Consideration of Relevant Factors:In addition to the chosen valuation method, other relevant factors specific to the asset being valued should also be taken intoconsideration. For example, for real estate, factors such as location, condition, and zoning regulations may impact its value. For financial assets, factors such as interest rates, market conditions, and regulations may be important.4. Documentation:It is crucial to document all relevant information and assumptions used in the valuation process. This includes details about the asset, the chosen valuation method, data sources, and any adjustments or assumptions made during the analysis. Proper documentation ensures transparency and allows for a better understanding of the valuation results.5. Compliance with Applicable Standards and Regulations: Valuations should be conducted in compliance with relevant accounting, legal, and regulatory standards. These standards may vary depending on the jurisdiction or industry. Compliance ensures that the valuation is reliable, consistent, and comparable.6. Incorporation of Professional Judgment:While using standardized valuation methods is important, professional judgment is also necessary. Valuations often require making assumptions and estimates based on the available information. Professional judgment helps in applying the chosen method appropriately, considering uncertainties, and interpreting the results. However, professional judgment should be backed by reasonable justification and documented accordingly.7. Continuous Monitoring and Review:Assets' values may change over time due to various external andinternal factors. It is recommended to regularly review and monitor the assets' values, especially for long-term assets. This ensures that the valuations remain up to date and aligned with the market and economic conditions.In conclusion, asset valuation follows certain basic guidelines to ensure objectivity, accuracy, and compliance with applicable standards. These guidelines include using appropriate valuation methods, considering relevant factors, documenting the valuation process, complying with standards and regulations, incorporating professional judgment, and continuous monitoring and review. Following these guidelines contributes to reliable and transparent asset valuation.。
环境影响经济损益分析
影响的筛选 影响的量化 影响的货币化 货币化结果纳入 项目的经济分析
标准
方法
技术
步骤
3.1 基本概念
3.2 环境价值评估技术(方法)
3.3 成果参照法
环境总价值
使用价值
直接使用 价值
•食物
非使用价值
选择价值
•保留将来 使用它的 机会
间接使用 价值
•防风固沙
遗赠价值
•栖息地
存在价值
•特有物种
•木材
设计模拟市场 选择提问方式 选择实施方式 抽样调查
1. 界定、描述环境物品
2. 设计、描述支付手段
1. 2. 3. 1. 2. 3. 直接提问 投标博奕 公决(NOAA建议使用) 面对面 电话 信函
1. 完全随机 2. 分层随机
结果分析:WTP = f (EQ, IN, ED, …)
参照旅行费用法、隐含价格法、调查评价法
近期的:PM10对健康的损害 长期的:重金属污染,气候变化
从性质上分:
内部的 外部的 大的 小的
有形的:景观改变 无形的:环境存在价值
从实体上分(可以有许多种分法):
1. 对生产的影响:水净化成本增加、作物产 量下降、渔业损失、材料维护 2. 对健康的影响:大气SO2污染引起的COPD、 PHD等发病率、死亡率的增加 3. 对环境服务的影响:景观改变、能见度、 游憩价值改变(使用价值/存在价值) 4. 对生态和全球系统功能的影响:生物多样 性、洄游、温室效应、臭氧层破坏
靳乐山. “用旅行费用法评价圆明园的环境 服务价值”. 环境保护, 1999(4):31-33
TC TC3 TC2 TC1 VR
景观价值V = CSi (i = 1,2,3)
环境政策与管理(0830J1)硕士专业介绍
环境政策与管理(0830J1)硕士专业介绍环境政策与管理专业(3年制硕士)环境政策与管理专业是2012年经国家教育部批准备案的交叉学科(一级学科为公共管理和环境科学与工程)硕士点,2013年开始招生。
中国是一个发展中国家,且正处于工业化和城市化进程中,伴随着巨大的人口压力、高速的经济增长,能源需求和环境污染压力都在不断增加,对我国的可持续发展进程提出了越来越多的挑战,急需大批专业人才来从事环境政策与管理工作,本专业就是为此目的设计的。
主要研究方向为:水环境政策与管理,包括地表水和地下水污染;空气环境政策与管理;节能减碳政策与管理;可持续发展管理和环境信息管理。
强调学科交叉、问题导向,管理学科为主,还涉及经济学、社会学、法学、政治学等学科。
目标是培养了解中国国情和环境问题特点,具有环境政策和管理理论基础,熟练掌握环境政策分析工具,具有解决问题能力的环境政策与管理专业人才。
培养具有良好的科学技术修养,能够与科学家、工程师交流,归纳政策和管理的要点;具备基本的社会调查、访谈技术,能够与公众交流,归纳和概括需求;熟悉政府的管理,了解企业的环境管理。
具有较强数据处理和分析能力,具有管理学、经济学等修养的,具备良好的书面和口头语言能力的环境管理的专业人才。
本专业有4名专职教师:宋国君(教授、博士生导师,硕士生导师,中国人民大学环境政策与环境规划研究所所长)张磊(副教授,硕士生导师)李岩(副教授,硕士生导师)张巍(副教授,硕士生导师)开根森(兼职教授,美国加州环保署水资源管理局工程师)阿瑟·P.J.莫尔(讲座教授,Arthur P.J. Mol,荷兰瓦赫宁根大学环境政策系,教授)对外学术交流:美国加州环保署;日本埼玉大学、京都大学、北海道大学、名城大学等;台湾大学、台北大学;荷兰瓦赫宁根大学。
主要设置两个培养环节,一是课程学习,第一年完成学校要求的规定课程,31学分左右;第二、三年,参与研究项目和实习,准备毕业论文。
自然资源非市场价值评估的选择实验法_原理及应用分析_樊辉
以达到估计模型整体参数的目的。
假设效用取决于从某一选择集 C 中做出的选
择,被调查者的直接效用函数可表示成如下形式:
Uin = U(Zin, Sn)
(1)
式中对任意个体 n 来说,他的某个选择的效用取决
于那个选择的属性 Z 的数值。当且仅当被调查者
认为 Ui > Uj 时,选择 i 优于选择 j ,会选择 i 。同时,
估 计 模 型 还 有 条 件 对 数 模 型(Conditional Logit
Model)和混合对数模型(Mixed Logit Model),常用的
2013 年 7 月
樊 辉等:自然资源非市场价值评估的选择实验法:原理及应用分析
1349
估计方法是最大似然估计法。混合对数模型
源,即个人对于诸如“如果……你愿意怎么样?”或 “你愿意支付……吗?”之类的假定问题的回答。陈
述偏好法中最为传统的方法是意愿价值评估法 (Contingent Valuation Method,CVM),CVM 通过被调 查者对这些假定问题的真实回答来获取对价值的 直接表达 。 [3] CVM 在过去的 40 多年来得到了广泛 的应用 1);然而,CVM 在实践应用中常常面临一些困 难和缺陷。比如,CVM 运用一次通常只能解决一种 环境变化状态所引起的福利变化,而且只能解决环 境质量整体一种变化状态的价值估计。然而,在实 践中,环境物品都具有多重的属性,决策者更关心 环境物品某种属性的变化和整体质量状况不同变 化的价值估计[6]。
(Mixed Logit Model)的待估计系数是一个假设的分 布,需要通过模拟估计实现。假设受访者 n 面临一
个情形 t 下有 j 个选项的选择,这时适用的混合对
资源环境价值评估方法述评
DOCTOR AL FOR UM博士论点·综合(上)2009年第9期随着全球资源与环境问题的日益恶化以及可持续发展战略思想的确立,人们逐渐认识到资源环境是有限的,且是有价值的,因而如何对其价值进行评估,成为经济学、环境学、统计学、会计学等领域的研究热点。
国内外专家、学者对资源环境价值进行了广泛研究,提出了多种价值评价体系,尽管各种价值评价体系叫法不同,但概括起来可从三个途径出发,即成本途径、收益途径和市场调查途径,每种途径都包含有若干种具体的评估方法。
一、基于成本途径的资源环境价值评估方法以维持、保护、恢复及优化生态环境系统所付出的代价作为生态环境系统的价值。
成本途径的资源环境价值评估方法主要包括:机会成本法、防护费用法、恢复费用法、人力资本法和影子工程法等。
(一)机会成本法对一定资源总存在着多种用途,可以选择一种使用方式,同时也就失去了其他使用方式的机会,把失去使用机会的方式中能获得的最大收益称为该资源的使用机会成本(Opportunity Cost )。
如某水域被划为保护区后,不能进行水产养殖,该水域则失去了作为渔业生产的机会价值。
(二)防护费用法防护费用(Defense Expenditure ,DE )是指人们为了减少和消除环境污染或生态恶化的影响而支付的费用,避免了损失,就相当于获得了效益,因此用防护费用来替代资源环境的价值。
例如,为了得到安全卫生的饮用水而购买安装净水设备;治理噪音污染、防护噪音干扰的花费,计为选择低噪音或无噪音环境的价值。
(三)恢复费用法当某一生态环境污染恶化,其功能降低,为了能将其各种功能恢复到受污染破坏前的水平而采取措施,所花的各种费用相当于该生态环境质量的最低价值。
如当某湖泊遭破坏退化后把湖泊恢复到受破坏以前的状态所需的费用,即可看作湖泊的价值;矿山开采完后,对周边环境的恢复费用,计为矿区原有环境的价值。
(四)人力资本法人力资本法(Human Capital Approach ,HCA )是通过环境污染对人体健康影响的损失来估计资源环境价值,主要包括以下三个方面内容:人生活在受污染的环境中过早死亡和生病造成的投入损失;由疾病引起的医疗费开支;人们心理上的损害。
期权复习题11
期权复习题1. Explanationspeculators wish to take a position in the market.Either they are betting that a price will go up or they are betting that it will go down. They use derivatives to get extra leverageHedgers are interested in reducing a risk that they already face. Arbitrage involves locking in a risk-less profit by entering simultaneously into transactions in two or more markets.A call option gives the holder the right to buy an asset by a certain date for a certain price.Put option: A put option gives the holder the right to sell an asset by a certain date for a certain price.Futures contract: It is an agreement to buy or sell an asset for a certain price at a certain time in the future.In-the-money option:it would lead to a positive cash flow to the holder if it were exercised immediately.risk-neutral valuation: Firstly, assume that the expected return from the stock price is the risk-free rate r, then calculate the expected payoff from the option, at last, discounting the expected payoff at the risk-free rate Butterfly spreads: A butterfly spread involves positions in options with three different strike prices: buying two call options with strike prices X1and X3, and selling two call options with a strike price X2, X1<X2 <X3Factors affecting stock option pricing: stock price, strike price, risk-free interest rate, volatility, time to maturity, and dividends.Bull spreads: A bull spread can be created using two call options with the same maturity and different strike prices. The investor buys the call option with the lower strike price and shorts the call option with the higher strike price. Bull spreads can also be created by buying a put with a low strike price and selling a put with a high strike price.Bear spreads: A bear spread can be created by selling a call with one lower strike price and buying a call with another higher strike price2. What is the difference between a long forward position and a short forward position?Solution: When a trader enters into a long forward contract ,she is agreeing to buy the underlying asset for a certain price at a certain time in the future. When a trader enters into a short forward contract ,she is agreeing to sell the underlying asset for a certain price at a certain time in the future.3. “when a futures contract is traded on the floor of the exchange, it may be the case that the open interest increases by one, stays the same, or decreases by one .” Explain this statement.If both sides of the transaction are entering into a new contract, the open interest increases by one. If both sides of the transaction are closing out existing position, the open interest decreases by one. If one party is entering into a new contract while the other party is closing out an existing position, the open interest stays the same.4.The price of gold is currently $500 per ounce. The forward price for delivery in one year is $700. An arbitrageur can borrow money at 10% per annum. What should the arbitrageur do? Assume that the cost of storing gold is zero.5.Give two reasons why the early exercise of American options on a non-dividend-paying stock is not optimal.6 Three call options on a stock have the same expiration date and strike prices of $45, $50, and $55. The market prices are $7, $5, and $2, respectively. Explain how a butterfly spread can be created. Construct a table showing the profit from the strategy.7.What is the price of a European put option on a non-dividend-paying stock when the stock price is $69, the strike price is $70, the risk-free interest rate is 5% per annum, the volatility is 35% per annum, and the time to maturity is six months? If this option is a European call option, what is the price?8. What is the price of a European put option on the S&P500 that is six months from maturity, the current value of the index is 500, the exercise price is 500, the risk-free interest rate is 10% per annum, the volatility of the index is 30% per annum., Continuous dividend yields is 2% per annum?9.Consider one year American put option on a non-dividend-paying stock when the stock price is $300, the strike price is $300, the risk-free interest rate is 10% per annum, and the volatility is 40% per annum. Divide the year into three 4-month time intervals and use the tree approach to estimate the value of the option.10. Consider the price of a stock, S , which following the processt dW dt dS σμ+=where t W is a standard Brownian motion. For the first three years,5,211==σμ; for the next three years, 4,322==σμ. If the initial value of stock price is $10, what is the expect value of the stock price at the end of year 6?11. What is the difference between forward contract when the forward price is $40 and a call option with a strike price of $40?(2) Suppose that a U.S. company knows that it is due to receive £10,000 from one of its British exporter in 30 days. It is faced with a significant foreign exchange risk. If you are management, how to hedging the foreign exchange risk by using forward contract or call optionrespectively?the foreign exchange rates of 30-day forward on pound is 1.60the strike exchange rate of a 30-day call option on pound is 1.60.12 Explain carefully the meaning of the terms convenience yield and cost of carry. What is the relationship between the futuers price F, the spot price S, the convenience yield,y, and the cost of carry,c?The convenience yield,y,(便利收益)for a commodity is a measure of the benefits realized from ownership (所有权)of the physical commodity (具体商品、实物商品) that are not realized by the holders of a futures contract.The cost of carry, c , is the storage cost plus the interest that is paid to finance the asset less the income earned on the asset.relationship between and the futuers price, the spot price, the convenience yield and the cost of carry is))((t T y c Se F --=13. A one-year-long forward contract on a non-dividend-paying stock is entered into when the stock price is $40 and the risk-free rate of interest is 10% per annum with continuous compounding.(a) What are the forward price and the initial value of the forward contract?(b) Six months later, the price of the stock is $45 and the risk-freeinterest rate is still 10%. What are the forward price and the value of the forward contract?14 .Explain the differences between forward contract and futures contract? 15 .Explain the differences between exchanged –traded and Over-the- counter ?• Exchange Traded– standard products– trading floor or computer trading– virtually no credit risk• Over-the-Counter– non-standard products– telephone market– some credit riskPrivate contract between 2 partiesExchange traded Non-standard contractStandard contract Usually 1 specified delivery dateRange of delivery dates Settled at maturity Settled daily Delivery or final cashsettlement usually occurs Contract usually closed out prior to maturity FORWARDS FUTURES16. Calculate the value of a six-month at-the-money European call option on a stock index when the index is at 500, the risk-free interest rate is 10% per annum, the volatility of the index is 20% per annum, and the dividend yield on the index is 3% per annum.17 If a stock price, S, follows geometric Brownian motiont SdW Sdt dS σμ+=1) What is the process followed by the variable n S ? Show that n S also follows geometric Brownian motion.2)The expected value of ST is =)(T S E )(t T Se -μ. What is the expected value of n T S ?3) The varaince of ST is =)(T S D )1()()(222---t T t T e e S σμ.What is the variance of n T S ?18 Show that the probability that a European call option will be exercised in a risk-neutral world is, )(2d N . Using risk-neutral valuation to value the complicated digtial option whose payoff at maturity iselse 0X S X K f T T 1T ⎩⎨⎧<<=2: 19 Suppose that a portfolio is delta neutral and has a gamma of Γ = -3,000, The delta and gamma of a particular traded call option are ΔT = 0.62 and T Γ= 1.50, respectively. What position in the traded call optionand in the underlying asset would make the portfolio both gamma neutral and delta neutral?=> The portfolio can be made gamma neutral by including a longposition ofwT = -Γ / ΓT = 3000/ 1.5 = 2,000 traded call options in the portfolio. However, the delta of the portfolio will then change from zero toΔ = 2,000 ΔT = 2,000 × 0.62 = 1,240=> A quantity, 1,240, of the underlying asset must be sold from the portfolio to keep it delta neutral.20. The stock price process assumed satisfiesSdW Sdt dS σμ+=Suppose that f is the price of a call option or other derivative contingent on S. Using no arbitrage opportunity to derive the Black-Scholes Differential Equationrf S f S S f rS t f =∂∂+∂∂+∂∂222221σ21. Give the definitions of delta, gamma, vega, theta, and rho of the derivative 。
城市地下空间土地使用权价格评估探讨——以单建式地下商业为例刘亚婷
城市地下空间土地使用权价格评估探讨——以单建式地下商业为例刘亚婷发布时间:2021-07-27T11:32:33.020Z 来源:《基层建设》2021年第14期作者:刘亚婷[导读] 随着城市人口、环境、资源三大难题愈加凸显,城市土地资源愈加珍贵青岛理工大学管理工程学院山东青岛 266525摘要:随着城市人口、环境、资源三大难题愈加凸显,城市土地资源愈加珍贵,拓展地下空间是世界城市发展的成功经验和必然趋势,对推动城市经济、社会环境协调健康发展具有十分重要的意义,为此需要对地下空间土地使用权价格进行科学评估,规范地下空间的开发利用。
本文首先通过明晰地下空间土地使用权及其价格的概念,评述国内外研究现状,分析出传统评估方法应用于地下空间的局限性;进而具体到单建式地下商业空间的评估,根据单建式地下商业空间特点,选取收益还原法并对其进行一定的改进,将其与立体空间楼层效用比率相结合,利用AHP层次分析法确定楼层效用比主要影响因素,建立特征价格模型,确定单建式地下商业空间土地租金;最后通过选取合理的土地还原率评估土地价格,为我国此类地下空间的评估提供一定的借鉴、参考价值。
关键词:单建式地下空间;楼层效用比;改进的收益还原法;AHP层次分析法引言当前城市化发展面临着严峻挑战:土地资源紧张、绿地面积减少、城市人口暴增、交通堵塞、能源消耗增大、环境污染、房价上涨等问题。
大力开发利用地下空间资源、拓展人类活动空间越来越迫切,合理、有序地开发利用地下空间,可以有效缓解城市土地资源的紧缺矛盾,提高土地利用效率,节约土地和空间资源,补充完善城市功能,提升土地资源价值,实现可持续发展。
在城市地下空间日渐被大规模开发利用的形势下,科学合理地对其土地使用权进行评估成为目前急需解决的问题。
但目前我国依然缺乏明确的城市地下空间定价体系,《城镇土地估价规程》也缺乏相应规定,关于城市地下空间土地使用权价格评估尚无统一标准,不论是地下空间宗地价格还是地下空间基准地价,均处于探索阶段,对地下空间使用权评估及理论方法的研究便显得尤为重要。
查看文献后的读书笔记模板
竭诚为您提供优质文档/双击可除查看文献后的读书笔记模板篇一:文献阅读笔记格式年月日文献名称(杂志、年卷期号)一、Introduction研究对象:研究地区:科学问题与假说:相关领域的最新研究进展和理论:二、methods野外采样方法(或实验室分析方法)数据的处理方法(统计方法和相关软件)三、Results开展的研究内容:1...............2.……………………获得的研究结果:1...............2.……………………四、Discussion1.从哪些角度讨论了研究结果;2.讨论了哪些关键指标和因素?3.讨论的思路是怎样的(比如平行的关系,还是递进的关系)4.作者得出的(验证的)或者引用的重要理论和假说五、Referencers列出你认为重要的值得一看的参考文献(标准格式)篇二:科研文献阅读笔记模板(word版)目录1usingthecontingentvaluationmethodtomeasurepatronbe nefitsofreferencedeskserviceinacademiclibrary........................... (122)334455注:只要不改变下面“标题与编号”项下的格式,填写完文献阅读笔记后,将鼠标对着本页目录内容,可通过:“单击右键弹出菜单–选择更新域,单击左键–选择更新整个目录”,即可在本页生成文献阅读笔记的目录。
1usingthecontingentvaluationmethodtomeasurepatronbe nefitsofreferencedeskserviceinacademiclibrary ?来源(期刊/书籍名称):collegeAssociateDirectoroftheuniversityofcentralFlo ridaLib-raries?文献类型:[实证研究]理论探讨在线网页或资源?文献价值:高[中]低?阅读内容:[文摘][前言][方法][结果]讨论结论要点:1评估参考咨询台服务的用户受益价值应包括使用价值(使用图书馆文献的受益)和选择价值(当潜在用户获知可选择该服务内容后的受益)[见摘要]2.共设置了3个问题来计算用户的支付意愿值(wTp),包括“维持现有服务时间”、“每周多开放18个小时”和“多开放18.5个小时”,使用10%切尾均数(trimmedmean)表示wTp平均值,结果显示该项服务的RIo可达3.5。
环境影响经济损益分析
“(四)建设项目环境保护措施及其技术、经济论证;” “(五)建设项目对环境影响的经济损益分析;”
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为什么要进行环境影响的 经济评价? 一种对话尝试 项目的经济评价和环境评价之间的对话。假如环境评价的结果是项目不可行,因为项目排放污染物的量太大,危害公众健康,那么,从理论上讲(先不从法律条例上看),从项目可获得的“经济利益”与项目产生的“环境危害”之间如何权衡? 一个社会要权衡,决策者要权衡,所以评价专家要权衡。 权衡,就需要一个统一的尺度。
存在价值
特有物种 独特景观
保留将来使用它的机会
间接使用价值
防风固沙 涵养水源
食物 木材 旅游
直接使用价值(DUV):指环境资源直接满足
人们生产、消费需要的价值,直接贡献
间接使用价值(IUV):是人类从环境所提供
的用来支持目前的生产、消费活动的各种功能中 间接获得的效益。
环境资源的价值构成
选择价值(OV):相当于消费者为一个未利用 的资产所愿意支付的保险金,目的是为避免将来失去它的风险。 环境资源供应和需求的不确定性的存在、人们对风险的态度决定选择价值的大小。
界定、描述环境物品 设计、描述支付手段
ห้องสมุดไป่ตู้
完全随机 分层随机
设计模拟市场
选择实施方式
选择提问方式
直接提问 投标博奕 公决(NOAA建议使用)
参照旅行费用法、隐含价格法、调查评价法的评价结果,用于评价一个新的环境物品。
最大优点:节省时间、费用。做一个完整的TCM,HPM,或CVM,通常要花费6-8个月,5-10万美元(在发达国家)。因此,环评中最常用的就是成果参照法。
基于意愿调查法的绍兴会稽山古香榧群游憩价值评估
基于意愿调查法的绍兴会稽山古香榧群游憩价值评估陈亚琳1,唐晓岚1,2,王斌3,周铭杰1(1.南京林业大学风景园林学院,南京210037;2.南京林业大学中国特色生态文明建设与林业发展研究院,南京210037;3.中国林业科学研究院亚热带林业研究所,杭州310000)摘要:采用意愿调查法(CVM )调查浙江绍兴古香榧群景观游憩功能的支付意愿(WTP ),对其游憩价值进行货币化的评估。
对被调查者的社会经济特征和人均支付意愿相关性进行分析,得出被调查者对古香榧群的了解程度与支付意愿有正相关性,年龄、月收入水平以及之前参观古香榧群的次数与支付意愿值呈显著正相关。
并针对会稽山古香榧群游憩价值开发现状,为提高绍兴会稽山古香榧群的游憩价值提出了建议。
关键词:意愿调查法;游憩价值;会稽山古香榧群;农业文化遗产中图分类号:F590文献标识码:A文章编号:1673-5919(2021)06-0112-04DOI :10.13691/23-1539/f.2021.06.027Recreational Value Evaluation of the Ancient Fragrant Torreya Group in Kuaiji Moun-tain,Shaoxing Based on the Willingness Survey MethodCHEN Ya-lin 1,TANG Xiao-lan 1,2,WANG Bin 3,ZHOU Ming-Jie 1(1.College of Landscape Architecture,Nanjing Forestry University,Nanjing 210037,China;2.Research Institute of Ecological Civilization Construction and Forestry Development with Chinese Characteristics,Nanjing Forestry University,Nanjing 210037,China;3.Research Institute of Subtropical Forestry,ChineseAcademy of Forestry,Hangzhou 310000,China )Abstract:This paper used CVM to investigate the willingness to pay (WTP)of its landscape recreation function ,and monetarily evaluated its recreation value.Through the correlation analysis between the re⁃spondents'socio-economic characteristics and their per capita WTP,it ’s found that their understanding degree was positively correlated with their WTP.Moreover,the monthly income level and the times of pre⁃vious visits between the value of WTP were more obvious.Then,it put forward some suggestions to improve the recreation value development of Torreya grandis group.Key word:CVM;Recreation value;Ancient Torreya grandis in Kuaiji Mountain1引言游憩价值是游客在景区等进行休闲游憩活动时,所产生的包括经济社会等方面的多重效益[1]。
假想(创建)市场评估法
7.1.3 (3)假想(创建)市场评估法(hypothetical/created market approaches)或(Hypothetical Valuation Method)7.1.3 (3)假想(创建)市场评估法(hypothetical/created market approaches)对没有市场交易和实际市场价格的生态系统产品和服务(纯公共物品),只有人为地构造假想市场来衡量生态系统服务和环境资源的价值。
代表性方法:意愿调查评估法(条件价值评估法)(Contingent Valuation Method,CVM)是一种典型的陈述偏好评估法。
意愿调查评估法(条件价值评估法)典型的陈述偏好法•定义:是一种基于调查的评估非市场物品和服务价值的方法,是在假想市场情况下,直接向有关人群样本询问对某种生态系统服务的支付意愿(WTP,willingness to pay) ---对某一环境改善效益的支付意愿或者受偿意愿---对环境质量损失的接受赔偿意愿(WTA,(willingness to accept),以人们的支付意愿来估计生态系统服务的经济价值。
意愿调查评估法•投标博弈法•比较博弈法•无费用选择法•专家调查法(Delphi法)投标博弈法(Bidding Game Approach)•概念:要求被调查对象根据一定情况,说出他们对不同水平的环境物品或服务的支付意愿(WTP)或接受赔偿意愿(WTA)。
广泛地应用于对公共物品的价值评估方面定义单次投标博弈收敛投标博弈单次投标博奕的步骤:•向被调查者解释要估价的环境物品或服务的特征及其变动的影响,以及保护这些环境物品或服务的具体办法,•询问被调查者,为了改善保护该热带森林或水体不受污染他最多愿意支付多少钱(即最大的支付意愿),•或者反过来询问被调查者,他最少需要多少钱才愿意接受该森林被砍伐或水体污染的事实(即最小接受赔偿意愿)在巴西里约热内卢进行的一项关于地表水质量改进的支付意愿的调查使用了单次投标博弈法(Scura and Maimon,1993)。
期权复习题11-12
期权复习题1. Explanationspeculators wish to take a position in the market.Either they are betting that a price will go up or they are betting that it will go down. They use derivatives to get extra leverageHedgers are interested in reducing a risk that they already face. Arbitrage involves locking in a risk-less profit by entering simultaneously into transactions in two or more markets.A call option gives the holder the right to buy an asset by a certain date for a certain price.Put option: A put option gives the holder the right to sell an asset by a certain date for a certain price.Futures contract: It is an agreement to buy or sell an asset for a certain price at a certain time in the future.In-the-money option:it would lead to a positive cash flow to the holder if it were exercised immediately.risk-neutral valuation: Firstly, assume that the expected return from the stock price is the risk-free rate r, then calculate the expected payoff from the option, at last, discounting the expected payoff at the risk-free rate Butterfly spreads: A butterfly spread involves positions in options with three different strike prices: buying two call options with strike prices X1and X3, and selling two call options with a strike price X2, X1<X2 <X3Factors affecting stock option pricing: stock price, strike price, risk-free interest rate, volatility, time to maturity, and dividends.Bull spreads: A bull spread can be created using two call options with the same maturity and different strike prices. The investor buys the call option with the lower strike price and shorts the call option with the higher strike price. Bull spreads can also be created by buying a put with a low strike price and selling a put with a high strike price.Bear spreads: A bear spread can be created by selling a call with one lower strike price and buying a call with another higher strike price2. What is the difference between a long forward position and a short forward position?Solution: When a trader enters into a long forward contract ,she is agreeing to buy the underlying asset for a certain price at a certain time in the future. When a trader enters into a short forward contract ,she is agreeing to sell the underlying asset for a certain price at a certain time in the future.3. “when a futures contract is traded on the floor of the exchange, it may be the case that the open interest increases by one, stays the same, or decreases by one .” Explain this statement.If both sides of the transaction are entering into a new contract, the open interest increases by one. If both sides of the transaction are closing out existing position, the open interest decreases by one. If one party is entering into a new contract while the other party is closing out an existing position, the open interest stays the same.4.The price of gold is currently $500 per ounce. The forward price for delivery in one year is $700. An arbitrageur can borrow money at 10% per annum. What should the arbitrageur do? Assume that the cost of storing gold is zero.5.Give two reasons why the early exercise of American options on a non-dividend-paying stock is not optimal.6 Three call options on a stock have the same expiration date and strike prices of $45, $50, and $55. The market prices are $7, $5, and $2, respectively. Explain how a butterfly spread can be created. Construct a table showing the profit from the strategy.7.What is the price of a European put option on a non-dividend-paying stock when the stock price is $69, the strike price is $70, the risk-free interest rate is 5% per annum, the volatility is 35% per annum, and the time to maturity is six months? If this option is a European call option, what is the price?8. What is the price of a European put option on the S&P500 that is six months from maturity, the current value of the index is 500, the exercise price is 500, the risk-free interest rate is 10% per annum, the volatility of the index is 30% per annum., Continuous dividend yields is 2% per annum?9.Consider one year American put option on a non-dividend-paying stock when the stock price is $300, the strike price is $300, the risk-free interest rate is 10% per annum, and the volatility is 40% per annum. Divide the year into three 4-month time intervals and use the tree approach to estimate the value of the option.10. Consider the price of a stock, S , which following the processt dW dt dS σμ+=where t W is a standard Brownian motion. For the first three years,5,211==σμ; for the next three years, 4,322==σμ. If the initial value of stock price is $10, what is the expect value of the stock price at the end of year 6?11. What is the difference between forward contract when the forward price is $40 and a call option with a strike price of $40?(2) Suppose that a U.S. company knows that it is due to receive £10,000 from one of its British exporter in 30 days. It is faced with a significant foreign exchange risk. If you are management, how to hedging the foreign exchange risk by using forward contract or call optionrespectively?the foreign exchange rates of 30-day forward on pound is 1.60the strike exchange rate of a 30-day call option on pound is 1.60.12 Explain carefully the meaning of the terms convenience yield and cost of carry. What is the relationship between the futuers price F, the spot price S, the convenience yield,y, and the cost of carry, c ?The convenience yield,y,(便利收益)for a commodity is a measure of the benefits realized from ownership (所有权)of the physical commodity (具体商品、实物商品) that are not realized by the holders of a futures contract.The cost of carry, c , is the storage cost plus the interest that is paid to finance the asset less the income earned on the asset.relationship between and the futuers price, the spot price, the convenience yield and the cost of carry is))((t T y c Se F --=13. A one-year-long forward contract on a non-dividend-paying stock is entered into when the stock price is $40 and the risk-free rate of interest is 10% per annum with continuous compounding.(a) What are the forward price and the initial value of the forwardcontract?(b) Six months later, the price of the stock is $45 and the risk-freeinterest rate is still 10%. What are the forward price and the value of the forward contract?14 .Explain the differences between forward contract and futures contract? 15 .Explain the differences between exchanged –traded and Over-the- counter ?• Exchange Traded– standard products– trading floor or computer trading– virtually no credit risk• Over-the-Counter– non-standard products– telephone market– some credit riskPrivate contract between 2 partiesExchange traded Non-standard contractStandard contract Usually 1 specified delivery dateRange of delivery dates Settled at maturity Settled daily Delivery or final cashsettlement usually occurs Contract usually closed out prior to maturity FORWARDS FUTURES16. Calculate the value of a six-month at-the-money European call option on a stock index when the index is at 500, the risk-free interest rate is 10% per annum, the volatility of the index is 20% per annum, and the dividend yield on the index is 3% per annum.17 If a stock price, S, follows geometric Brownian motiont SdW Sdt dS σμ+=1) What is the process followed by the variable n S ? Show that n S also follows geometric Brownian motion.2)The expected value of ST is =)(T S E )(t T Se -μ. What is the expected value of n T S ?3) The varaince of ST is =)(T S D )1()()(222---t T t T e e S σμ.What is the variance of n T S ?18 Show that the probability that a European call option will be exercised in a risk-neutral world is, )(2d N . Using risk-neutral valuation to value the complicated digtial option whose payoff at maturity iselse 0X S X K f T T 1T ⎩⎨⎧<<=2: 19 Suppose that a portfolio is delta neutral and has a gamma of Γ =-3,000, The delta and gamma of a particular traded call option are ΔT = 0.62 and T Γ= 1.50, respectively. What position in the traded call optionand in the underlying asset would make the portfolio both gamma neutral and delta neutral?=> The portfolio can be made gamma neutral by including a longposition ofwT = -Γ / ΓT = 3000/ 1.5 = 2,000 traded call options in the portfolio. However, the delta of the portfolio will then change from zero toΔ = 2,000 ΔT = 2,000 × 0.62 = 1,240=> A quantity, 1,240, of the underlying asset must be sold from the portfolio to keep it delta neutral.20. The stock price process assumed satisfiesSdW Sdt dS σμ+=Suppose that f is the price of a call option or other derivative contingent on S. Using no arbitrage opportunity to derive the Black-Scholes Differential Equationrf S f S S f rS t f =∂∂+∂∂+∂∂222221σ21. Give the definitions of delta, gamma, vega, theta, and rho of the derivative 。
环境管制收益与成本评估与分配
环境管制收益与成本的计量问题,是一个特别有争议的领域,主要原因有以下两点:第一,管制的收益与成本牵涉到现成市场计量措施无能为力的要素,如健康收益和景观美感改善的价值等;第二,政策制定者不愿使用如“人类生命价值”这类的货币计量手段,来评估环境管制的得与失。
当然第二点也是可以理解的。
然而,环境经济学家在评估“非市场化”(non-rnarket)的环境服务方面已取得了重要的进展。
自从上个世纪六十年代末的“环境革命”至今,环境经济学在收益与成本计量方面,主要取得了以下两点进展:首先,环境以及其他领域的经济学家发展出了利用环境质量与各种市场化产品之间关系的技术,即间接市场法(indirect market methods)。
这些方法允许我们从市场化产品,以及以各种方式与其相关的物品的价格,来推测环境质量改善的价值。
其次,环境经济学家还借助于在经济学领域一直存在争议的个人直接调查法(direct questioning of individuals),即直接问询个人对环境服务的估价。
如个人直接调查法中“或有评估”法,能被用来引出明确而可靠的环境质量改善的个人评价。
在转入评述之前,需简略说明我们是如何界定这个文献评述的。
为了这一目的,我们尝试对“环境经济学”和“自然资源经济学”作一划分。
自然资源经济学的突出特征是,它专注于可再生的与不可再生的自然资源的跨期(inter-temporal)配置。
自然资源经济学理论是运用动态控制方法来分析跨期资源利用问题的典型,它起始于Hotelling。
的一篇开创性文章。
此后,关注渔业、森林业、矿产业、自然能源、濒危物种的管理以及可持续发展的文献大量涌出。
我们评述的对象不包括这类文献。
此外,必须指出的是,环境经济学与自然资源经济学的划分界线是相当模糊的。
然而,为了使文献评述易于处理,我们将集中于环境管制的两个重要方面:环境管制收益和成本的评估与分配,来展开评述。
一、环境质量变化价值的评估环境经济学文献的标准方法,是将生产过程中的废物排放导致的污染,作为“公害”(public“bad”)来处理。
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April 11, 1997Using Contingent Valuation to Estimate a Neighborhood’s Willingness to Pay to Preserve Undeveloped Urban LandWilliam S. Breffle, Edward R. Morey, and Tymon S. LodderSummary. Contingent valuation (CV) is used to estimate a neighborhood’s willingness to pay (WTP) to preserve a 5.5-acre parcel of undeveloped land in Boulder, Colorado, that provides views, open space, and wildlife habitat. Households were surveyed to determine bounds on their WTP for preservation. An interval model is developed to estimate sample WTP as a function of distance, income, and other characteristics. The model accommodates individuals who might be made better off by development and addresses the accumulation of WTP responses at zero. Weighted sample WTP estimates are aggregated to obtain the neighborhood’s WTP. This application demonstrates that contingent valuation is a flexible policy tool for land managers and community groups wanting to estimate WTP to preserve undeveloped urban land.William S. Breffle is at the Department of Economics, University of Colorado, Boulder, CO 80309 and Hagler Bailly Consulting, P.O. Drawer O, Boulder, CO 80306; Edward R. Morey is at the Department of Economics, University of Colorado, Boulder, CO 80309; and Tymon S. Lodder is at the Regional Air Quality Council, 1445 Market St. #260, Denver, CO 80202.1.IntroductionThe combination of abundant open space and other natural amenities with urban amenities is motivating the rapid growth of many medium-sized cities in the western United States. However, the congestion and development brought by this growth reduces access to and services from natural amenities. Such growth concerns have led several cities such as Eugene (Oregon) and Boulder (Colorado) to initiate programs to restrict development and expansion in an effort to maximize the well-being of citizens. For example, the Boulder City and County Comprehensive Plan preserves virgin county land by supporting infill within the city limits and slow expansion of the city 1boundaries. Pressures to develop unused portions of land within or near city limits, especially on the edges of the city, create tension at the local level when neighborhoods have strong preferences to preserve their scarce remaining open space and natural areas. Our intent is to estimate the neighborhood’s willingness to pay (WTP) for preservation.We propose the use of contingent valuation (CV) as a method to estimate WTP. Put simply, contingent valuation estimates individuals' WTP for some policy, such as a change in environmental amenities, using survey questions that elicit information on how much each sampled individual2would be willing to pay to have the policy implemented. To demonstrate, we use CV to value the preservation of the Cunningham property, a small, undeveloped lot in Boulder. The preservation values estimated by CV include both values in active use (“use values”) and values in passive use (“passive use values”).By definition, use values from a site-specific resource such as the Cunningham property can be obtained only if one is at or near the site. For example, obtaining use benefits from a mountain requires that one be at or near the mountain. Obtaining the use benefits from hiking requires that onebe on site. Enjoying scenic views of the mountain constitutes a use benefit that requires either a trip to the mountain or a residence near it. One does not need to deplete the resource to enjoy use benefits, though some activities such as hunting do use up the resource. Passive use values are those values that one can obtain from a resource without being at or near the resource. For example, the pleasure one gets from knowing that fish live in quality habitat does not require one to visit the stream.If a property is preserved, households may have either increased or decreased use benefits because of better or worse views, changes in recreational opportunities, and so forth. Additionally, households can experience increased or decreased passive use benefits, such as the contentment associated with knowing wildlife habitat is being preserved. Use values have the potential to be3capitalized into land prices, wage rates, or both. Passive use values cannot be capitalized into property values or rents because individuals can realize them without residing near the property.Contingent valuation is not presented as a replacement for a hedonic property value study to estimate the impact of natural amenities on property values. It is well documented that residential property values are influenced by proximity to site-specific amenities and disamenities. For example, property values are influenced by proximity to undeveloped coastline (Dale-Johnson and Yim, 1990; Frech and Lafferty, 1984), retail sites and highways (Waddell et al., 1993), traffic (Asabere, 1990), clean air (Harrison and Rubinfeld, 1978), and open space (Correll et al., 1978). See also Linneman (1981). A negative effect of development on nearby property values could be a significant reason why property owners would be willing to pay to preserve undeveloped urban land, and hedonic4studies can be used to quantify this effect. However, WTP for preservation does not necessarily equal the expected impact that preservation will have on the value of other property. If WTP forpreservation is due in part to passive use motives, a hedonic property value study can provide values that are significantly more or less than WTP for preservation. Of course, many individuals may have both use values and passive use values that are positive, which is likely to be the case in our study. If passive use values are positive, a hedonic property value study would underestimate total WTP for preservation.Even when it is expected that preservation will not affect wage rates (which is true for this study) and that most of the value of preservation is use value, measurement of preservation benefits using a hedonic property value technique is difficult. Complications include disequilibrium in the real estate market, the role expectations play in determining when the benefits of preservation are capitalized into land prices, and the difficulties associated with factoring out other influences.While we do not use hedonics explicitly to estimate the impact of the proposed Cunningham development on property values, Correll et al. (1978) found that distance to official open space, or "greenbelt," has a significant effect on property values in Boulder. Assuming that prior to development, the Cunningham property was viewed as equivalent to official open space, and taking into account that the Cunningham property is the closest access to open space for approximately 200 households, the reduction in property values suggested by their rent gradient is in the range of $500,000 to $1.5 million, depending on the specific assumptions adopted.2.The Cunningham Property and CoalitionThe Cunningham property is a 5.5-acre parcel of land that lies on the northwestern edge of Boulder, a mid-sized city bounded by mountains on the west and prairie on the east (see Figure 1). In its undeveloped state, including an old, abandoned house and a few fruit trees, the property provideswildlife habitat, views of the mountains to the west, and access to designated open space. The property’s north boundary is an important east-west road that provides access to Boulder for many mountain residents, but the neighborhood to the east and south of the property is currently buffered from this traffic because there is no north access for traffic near the property. The single north outlet from this neighborhood is a popular bike path.Figure 1Figure 1. The Cunningham property and Boulder, ColoradoA construction company purchased the land in 1991 for $600,000 and hoped to build a luxury-home subdivision. A north-south street on the eastern boundary of the property would have been constructed to provide access. In addition to increasing traffic from the additional homes, this street would have eliminated the bike path and created a new route from the mountains to downtown Boulder. For many reasons, the development would have been possible only if the city annexed the land.A neighborhood group called the Cunningham Coalition formed to lobby against the proposed development and to raise donations to allow the City’s Open Space Program to purchaseand preserve the property. The Cunningham Coalition’s periodic newsletter solicited donations and described the property and the status of the proposed development plan. One of the newsletters included a pledge card on which one could pledge a cash contribution to the direct purchase of the property or indicate a willingness to pay additional property taxes to purchase the property via a special tax district. The newsletter of January 9, 1992, noted that $98,600 had been pledged by approximately 130 households in the north Boulder area.3.Sample and SurveyWe restricted our investigation to residents of the City of Boulder who live within one mile of the5Cunningham property, hereafter “the neighborhood”. The neighborhood can be envisioned as a pie with the Cunningham property at the center and the western quarter slice removed. We estimated that there were 2,561 city residences within one mile of the property. An in-person CV survey was administered in 1991 to 75 households, and 72 complete interviews were obtained. Arrow et al. (1993), the “Blue Ribbon Panel,” recommend in-person interviews as preferable to mail or telephone surveys to elicit contingent values. The survey is presented in the Appendix.The sampling scheme was designed to obtain a representative sample of city households within one mile of the property. The sampling area was divided into ten one-tenth-mile-wide bands: the first was zero to one-tenth of a mile from the property, and the outermost was nine-tenths to one mile from the property. There are 12 residences in the innermost band and 435 in the outermost. The number of households targeted in each band was proportional to the total number of households in the band. Target households were chosen randomly, and interviews varied by time of day and day of week. If no one was home on the first attempt, the residence was revisited on a different day ata different time. If the individual contacted did not want to be interviewed at the time of first contact, the interviewer attempted to schedule a more convenient time. No residence was visited more than twice.The response rate for those households successfully contacted with two visits was almost 100%; there was a high level of interest in the neighborhood about the Cunningham property. Comments indicated that many of those contacted appreciated that the interviewers did not represent the coalition, the city, or the developer. The overall response rate was 63%; two visits were not sufficient to contact the rest of the households. A 63% response rate is in the range of many CV 6studies. Sample selection bias is always a concern with CV studies. For example, households indifferent to the scenario (those with $0 WTP) might be less inclined to be interviewed. Therefore, if a significant proportion of the households contacted refused to be interviewed, attempts should be made to determine why and the results used to model sample selection. In our case, the fact that the response rate among those contacted was effectively 100% indicates that households were not selecting out of the survey on the basis of their WTP.The percentages of households in the neighborhood and sample are presented by band in Table 1. Only one household was sampled in the innermost band. Average neighborhood WTP is calculated as a weighted average of the WTP estimates for the sample households in the next section, where the weights correct for misrepresentation by distance band.Table 1. Proportion of households at varying distances from the Cunningham propertyDistance (miles)Sample Neighborhood0.1 1.4%0.5%0.2 2.8% 2.5%0.3 5.6% 5.3%0.4 5.6%7.2%0.58.5%11.1%0.611.3%13.1%0.714.1%14.3%0.815.5%12.7%0.915.5%16.5%1.019.7%17.0%We have no independent estimate of income for the neighborhood. Percentages of the sample in three income categories are reported in Table 2, which show that the neighborhood is relatively affluent. We have no reason to believe that our sample is unrepresentative in terms of income. However, income data by category from the 1990 U.S. Census is also presented in Table 2 for ZIP code 80304, of which the neighborhood is only a very small component. We do not believe that income statistics for the broader ZIP code should be the basis to gauge the representativeness of the sample in terms of income, because the neighborhood is more affluent than the rest of the ZIP code. Looking ahead, we feel that the best estimate of neighborhood WTP is that which weights the sample WTP in terms of distance, but makes no adjustment for income distribution. However, as a conservative estimate of neighborhood WTP, we also report an estimate that is weighted for both distance and income.Table 2. Income distribution for the sample and surrounding ZIP code Annual income category Sample ZIP code 80304Less than $35,00025.4%47.3%$35,000-$65,00035.2%25.4%More than $65,00039.4%27.3%The survey asks the respondent in two separate questions (12 and 13) to state whether she would pay each of an ascending or descending sequence of specific amounts as a one-time payment to preserve all undeveloped land within one mile of Boulder, and to preserve the Cunningham 7property. To test for potential starting-point bias, we started half of our inquiries for these questions at the top of the range (descending values) and half at the bottom (ascending values). We could not reject the null hypothesis of no starting-point bias. While we are not directly concerned with the answer to Question 12, it was included in an effort to help make clear the distinction between the Cunningham property and other undeveloped land. Kahneman and Knetsch (1992) have provided strong evidence of “embedding”, which is the tendency to value a scenario that is more encompassing than the one presented.In all CV studies there is a potential for strategic bias, and a concern is that this will cause households to overstate their WTP. Some respondents might overstate their WTP, hoping to influence a City Council decision, if those respondents thought they would never have to pay. However, the Cunningham Coalition had clear intentions to try to raise the money needed to purchase the property. If respondents thought the Coalition would actually try to collect reported WTP bids, some respondents might instead understate their true values in order to free-ride on others’ contributions. (In fact, many of the pledges to the Coalition were substantially larger thancomparable WTP values estimated using the CV data.) We made clear that we did not represent any advocacy group that stood to gain or lose from development.Our survey does not produce a specific estimate of the household’s maximum willingness to pay to preserve the Cunningham property, but rather places upper and lower bounds on willingness to pay. For an ascending survey, suppose the individual said yes to $100 but no to $125; $100 is a lower bound on that household’s WTP, and $125 is an upper bound. If we were to conduct another Cunningham survey, we would first ask whether the development scenario described would make the household better or worse off, and then ask Question 13 only of those individuals who indicated8that development would make their household worse off. Knowing whether the household would be better or worse off would provide a strong validity check on zero bids. A respondent might have a negative WTP if he or she believes that the Cunningham property is an eyesore because of the presence of the abandoned, rundown house, that jobs and increased economic activity are desirable for Boulder, or that inhibiting growth and development is unethical and elitist. WTP might also be negative for a respondent who believes that homes built on the property would be more expensive than the average home in the neighborhood and would raise property values. Knowing whether zero bids are true zeros or truncations of negative values is important for modeling purposes and the estimation of WTP values, as discussed in the next section.WTP questions about other development scenarios for the site might also have been included. We did not anticipate how the developer’s proposal would evolve over time, so we asked only about the proposal that was current at the time of the survey (i.e., nine houses and the creation of a north-south connecting street, which would increase traffic and eliminate the bike path). Because the potential connecting street, with its resulting increase in traffic, was the primary negative feature ofWTP i 'E (WTP i )%%2DIST 2i%4HINC2i%i (1)the development for many, we might have asked those who reported a positive WTP how much their WTP would decrease if the development did not include the street connection.94.Estimation of WTPAn interval model is used to estimate household WTP as a function of distance, income, and other characteristics. The model accommodates individuals who might be made better off by 10development (negative WTP) and addresses the accumulation of refusal responses at the lowest possible bid, $5. Individuals who stated they would not pay $5 for preservation (the lowest amount in our survey) indicated that their WTP is less than $5; there is a possibility that these households would benefit from development.We hypothesize that respondent i’s WTP, WTP , lies between a lower bound (WTP ) equal i Li to the highest amount to which he or she responded yes and an upper bound (WTP ) equal to the Ui lowest amount to which he or she responded no. Assume that expected WTP for respondent i,E(WTP ), is a function of the respondent’s household characteristics:i where DIST is the distance to the property in tenths of a mile, HINC1 equals one if household income is between $35,000 and $65,000 and zero otherwise, HINC2 equals one if household income is greater than $65,000 and zero otherwise, and PRSVLAND is the response to Question 2 on the importance of preserving land (where 1 is not at all important and 7 is very important). The randomterm,, where+Prob (WTP Li <WTP i <WTP Ui )'Prob (WTP i <WTP Ui )&Prob (WTP i <WTP Li )'i )&i )Log L '71i '1log[i )&i )](2)(3)HINC2. This specification ofis the standard normal cumulative distribution function. The maximum likelihood program in the computer package Gauss (Aptech Systems, Inc., 1995) was used to find the values of the parameters that maximize the log of the likelihood function:11Likelihood ratio tests indicate that distance, income, and PRSVLAND are all significant determinants of WTP. No other variables were found to be significant, but others may be important in similar applications of CV. Number of children in the household, gender, political affiliation, hours spent participating in outdoor recreation each week, home ownership status, and north versus south portion of the neighborhood were found to be insignificant determinants of WTP. The WTP and standard deviation parameter estimates and t-statistics are reported in Table 3. All coefficient estimates in the WTP equation are significant at the 10% level or better using a one-tailed test, except for the coefficient on HINC1(( to vary with distance and income significantly1iimproves the fit of the model.12Table 3. Interval-model parameter estimatesEstimated coefficient t-statistic WTP parameters:Intercept ()-2,407.66-1.981DIST ()21.420.363HINC2 ()75.59 2.265Standard deviation parameters:Intercept ()-742.00-4.241HINC1 ()54.040.663NOBS:712Pseudo-R:0.72 (final model compared to a model that assumes WTP is randomlydistributed across the real numbers); 0.16 (final model compared to a modelthat estimatesincome categories, holding PRSVLAND constant at the sample mean, 6.2. These estimates demonstrate the decreasing effect of distance on WTP, and the increasing effect of income.Table 4. Estimated WTP as a function of income and distance category*Distance (miles)Income categoryLess than $35,000$35,000-$65,000More than $65,0000.1$1,135$1,157$1,2870.2$925$947$1,0770.3$736$757$8880.4$567$588$7190.5$419$440$5710.6$291$312$4430.7$184$205$3360.8$97$119$2500.9$31$53$1831.0-$14$7$138*Estimated values are computed holding PRSVLAND constant at the sample mean, 6.2.A few respondents had much lower values for this variable, which has a strongnegative effect on estimated WTP.The estimated sample mean WTP is $294; the median is $234. The standard deviation of mean WTP for the sample is $46, which was derived using the method of bootstrapping. The mean13WTP for households within one-tenth of a mile is $1,197 (standard deviation of the mean is $345), and the mean WTP for households between nine-tenths of a mile and one mile is $47 (standard deviation is $33). Figure 2 depicts how estimated WTP varies across the 71 households in thesample. The negative estimated values are for households far from the property with low income who place little importance on preserving undeveloped land.14Figure 2Figure 2. Distribution of estimated sample WTP to preserve the Cunningham property.The data suggest that passive use values are a small but significant portion of the total WTP for preservation of the Cunningham property. Passive use motives for WTP were frequently reported in survey comments. In addition, the finding that WTP is significantly greater than $0 for households in the outermost distance shell, where WTP is largely unrelated to property value effects and use, is another indicator that preservation would provide some passive use benefits.It is of interest to compare our WTP estimates to the Cunningham Coalition’s pledges, which averaged $760 per household for the 130 households that pledged. Most (95%) of the households within a mile of the property did not pledge and were not directly asked to pledge. It is our understanding that most of the pledges came from households relatively close to the property, thearea where the coalition focused its fundraising activities. The pledges ranged from a few dollars to two pledges of $20,000; removing these two high pledges reduces the average pledge to $458. We were unable to match pledges and WTP survey responses by household; the coalition felt that giving us this information would violate confidentiality. However, because we sampled up to a mile from the property and chose our sample to be representative in terms of distance from the property, and because the coalition’s main solicitation efforts were directed toward households within a few blocks of the property, it is unlikely there is much overlap between the two groups. In one case, a surveyed household indicated that it chose its response to our survey to be consistent with its pledge to the coalition. That household had pledged $5,000 to the coalition, and it reported its WTP as greater than $2,000, the highest amount queried on the survey. This was the largest indicated WTP in our sample. In contrast to the population that pledged, 11 of the 71 households in our sample reported a WTP of close to zero (# $5). It is reasonable to assume that few of these households pledged to the coalition.The largest CV-estimated household WTP is $1,197, which is an order of magnitude less than the two $20,000 pledges. This result demonstrates that the model is not overestimating maximum WTP. Estimated average WTP for the households within one-half mile is $709, which is also less than the average pledge, so based on the pledges it would be difficult to argue that CV is overestimating the neighborhood’s WTP for preservation.Sample estimates of WTP are extrapolated to derive an aggregate estimate for the neighborhood using weights that account for differences between the sample and the population in terms of distance. Multiplying the weighted mean WTP of $302 by the 2,561 city households within one mile of the property generates an expected neighborhood WTP of $774,000. The bootstrappinganalysis indicates that the standard deviation of expected aggregate WTP is $121,000, and the probability that neighborhood WTP is greater than $600,000, the developer’s purchase price, is 92%. Weighting for income in addition to distance is possible, but as noted in Section 3, we have doubts that comparing household income for the entire ZIP code to this specific, relatively affluent neighborhood is appropriate. Weighting for both ZIP code income and distance, the estimate of neighborhood WTP would be $642,000 with a standard deviation of $122,000.5.ConclusionThe best estimate of neighborhood WTP, $774,000, is greater than what it might have cost to purchase the property from the developer. The estimated model suggests the likelihood of raising sufficient funds is maximized by first collecting voluntary contributions, and then administering a local referendum to determine whether a special property-tax district should be constructed to raise the additional revenues. Given the incentive to free-ride on the contributions of others, it is unlikely that voluntary funds would be sufficient, which is corroborated by the Cunningham Coalition’s pledges of only $98,600. To raise the rest of the funds, the city could consider a neighborhood bond issue. Based on the estimated model, a neighborhood bond issue that increased every household’s property taxes one time by $192, the median neighborhood WTP, would just pass and would raise $493,000. Because there are more voters farther from the property and WTP decreases with distance, more money could be raised if the proposed tax varied by distance. For example, if the tax varied by increments of one-third of a mile, $831,000 could be raised by referendum, suggesting that a distance scheme is a vital component of a referendum intending to maximize revenue. Income wasalso found to be a significant determinant of WTP, so the likelihood of the bond issue passing might increase if low-income households were made exempt.This study demonstrates that CV is a flexible policy tool for both government land managers and private community groups concerned about whether to preserve undeveloped urban land. Each study could be uniquely designed to meet limited local budgets, yet provide definitive policy guidance. Our survey and model, with relevant modifications, including those discussed in Section 3, could be used as templates for similar applications.6. EpilogueAt one point the Cunningham Coalition entered into an agreement with a private individual. The coalition agreed to subsidize that individual’s purchase of the property subject to a restrictive covenant in the title so that only one house could be built, and the rest of the property would have to remain undeveloped forever. This individual made an informal proposal to purchase the property, but the proposal never came to fruition because the parties could not agree on timing.Because of this study and other factors, the City of Boulder decided that annexing the property was not in the best interest of the community, ending all plans for a housing development.A t that point the coalition’s attempts to purchase the property ended. However, the developer sold the property to another buyer who, in accordance with county regulations, built one home with a pool, tennis court, artificial ponds, golf greens, expansive grass, and a tall iron fence. While development was limited to one house, these modifications are not consistent with the coalition’s original vision of preservation.。