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Research Tender Title: Hedonic Pricing Study to Determine whether Energy Efficiency Ratings and Council Tax Differentials Impact on Prices in the Domestic Buildings Sector Reference No: TRN 297/11/2011 15 December 2011 Department of Land Economy 19 Silver Street, University of Cambridge Cambridge, CB3 9EP Phone: 01223 337137 School of Real Estate & Planning Henley Business School University of Reading Whiteknights Reading RG6 5UD Section 1: Understanding of the requirement and objectives addressed A: Introduction Both internationally (via UN-led international protocols on carbon reduction) and nationally (via recently enacted legislation to legally limit carbon emissions), the UK has led action on climate change. The building stock is recognised as a major contributor to carbon emission with the domestic stock estimated to be responsible for approximately 27% of UK carbon emissions1. There has been substantial government investment in the development and deployment of technologies to reduce demand for building-related energy. Over the past decade, Energy Efficiency Commitments (EEC1 and EEC2), Warm-front, and the Carbon Emissions Reductions Target (CERT) have encouraged domestic occupiers to invest in energy saving technologies. The ‘Green Deal’, which the Government is currently consulting on, is the latest and most extensive initiative. It seeks to work with energy suppliers and encourage investment in renewable energy generation as well as energy reduction. Whilst recent DECC research has shown2 that there are demonstrable savings from investment in energy saving technologies, there is a lack of research into whether these cost savings are reflected in capital prices and rents paid. The same is true for property-related tax payments. Since the introduction of Energy Performance Certificates (EPCs) in 2008 and Council Tax bandings in 1993, very little research exists into whether these dwelling attributes are significant price determinants. Identifying such an effect, from what might be regarded as second order demand attributes, relies on the hedonic price modelling of comprehensive and well-specified data sets. Over the course of several real estate pricing studies, researchers at the Universities of Cambridge and Reading have acquired excellent data procurement, database assembly and price modelling skills in this field. Our most recent research focuses on the price impact of EPCs, BREEAM, LEED and Energy Star ratings on the price of non-domestic buildings. Combined with our understanding of energy modelling in the domestic building stock, we believe that our price modelling experience delivers the required skill-set for a hedonic pricing study in the domestic building sector. B: Background and context The changing preferences and attitudes of market participants and new environmental regulation are having an increasing impact on the operation of property markets. Among property occupiers, investors and professionals, there has been a growing awareness of the contribution that the property 1 http://www.direct.gov.uk/en/HomeAndCommunity/BuyingAndSellingYourHome/Energyperformancecertificat es/DG_177026 2 National Energy Efficiency Data-Framework: Report on the development of a data-framework and initial analysis, June 2011, Department of Energy & Climate Change 2 industry can make towards reducing the environmental effects of business. Similar to many other product markets, voluntary (albeit often prompted by government) environmental certification schemes have emerged in most mature property markets. A range of acronyms have appeared for similar property eco-certification schemes, e.g. BREEAM (UK), NABERS (Australia), CASBEE (Japan), HQE (France), LEED (USA) and DGNB (Germany). In addition to these voluntary ecolabels, Energy Performance Certificates (EPCs) and Display Energy Certificates (DECs) are examples of mandatory energy labels that have been introduced across the European Union. Our understanding of the objectives of this project rests on the assumption that EPCs and related policies aim to provide information to consumers or users about the environmental or energy performance of a product. The indirect objective is to then change consumption and investment choices, suppliers’ production outputs and, as a result, the level of environmentally harmful emissions. Assuming that energy efficiency is a salient attribute for consumers, we would expect that energy efficiency is reflected in rental values and capitalised into house prices via increased demand for properties with lower running costs and lower exposure to future energy price risk. We expect that any energy efficiency premium identified in the hedonic analysis is likely to be a relatively small component of the overall transaction price. With regard to policy interventions, it is thus pertinent to explore whether council tax levels are also capitalised into house prices and if so, assess the potential impact of a policy intervention that aims to differentiate council tax bands not only by value but also by the energy efficiency of a dwelling. There is a growing body of research related to this topic. In our database of empirical studies of the price effects of environmental or energy certification on property prices, we have documented over 20 papers that have been put into the public domain since 2008 (see Appendix 1 for a review of relevant studies). A number of observations can be made. Most of the studies have been on US offices. The vast majority of studies have found a positive (albeit variable and inconsistent) effect of environmental or energy certification on rents and sale prices. Usually due to incomplete information, the studies differ in sample size and composition, econometric model specification, outcome variables (appraisals, prices), handling of data errors and control for location effects. Outside of the US, preliminary studies presenting evidence of the effect of eco-certificates and/or energy efficiency on pricing have recently been published for the UK, Netherlands, Germany, Japan and Singapore. Finally, all the studies are snapshots in time. If market penetration of environmentally certified or highly energy efficient buildings (supply) continues to increase and the attitudes of investors and occupiers continue to change (demand), the price effects of environmental certification on buildings will also continue to evolve. 3 Much more developed is the long established body of work, particularly in the US, investigating the effects on house prices of variations in real estate taxes among different jurisdictions (see Cheshire and Mills, 1999 for a review). Theoretically, it is accepted that, all else equal, land rents should capture property tax differentials. There is substantive empirical evidence to support this hypothesis. For instance, following the introduction of Proposition 13 in California in the late 1970s, Rosen (1982) finds that jurisdictions with the largest decreases in tax experience highest house price growth. However, a key mediating factor is scope of local services. Later work in Massachusetts found that communities that were able to increase tax revenues more rapidly and to allocate more resources to education spending experienced faster growth in property values (see Lang and Jian, 2005). In the UK, there has been limited empirical investigation of the effect of property taxes upon property prices. Bond, Denny, Hall and McCluskey (1996) attempted to model the dynamic relationship between changes in non-domestic rates and rents for a sample of commercial properties. Whilst they find some evidence to support a negative impact on rents of increasing rates bills, they find large variations in lags between markets and, sometimes, rather implausible results. We are not aware of any empirical studies that investigate the impact of Council Tax variations on local house prices across the UK. C: Key Objectives and Aims It is expected that the research project will deliver: A comprehensive dataset of property attributes, prices, local property taxes and energy efficiency performance for a large sample of English residential properties. An evaluation of the potential contribution and limitations of hedonic analyses to estimating the price effects of Council Tax levels and EPC ratings on English residential properties. A comprehensive review of existing research on the effects of local property tax levels and environmental performance on property prices. Estimates of the effects of local council tax levels and EPC labels on residential property prices using standard cross-sectional hedonic modelling. Estimates of the effects of local property tax levels and energy labels on residential property prices using repeat sales modelling. D: Data Requirements The underlying premise of hedonic analysis is that values of numerous attributes of a multi-faceted economic good are reflected in either capitalised prices or annualised rents. Therefore, dwelling occupiers receive utility from each of the many attributes of a good, in this case the housing unit. Dwelling prices are hedonic in that they represent a bundle of attributes such as location advantages, 4 space, quality of product etc. The number of hedonic attributes could, theoretically at least, be large in number. However, often a small number of key characteristics tend to be the key price determinants. When examining the impact that EPCs and Council Tax might have on prices, it is essential that the key price determinants are identified and controlled for. Therefore, to conduct the hedonic regression analysis, the following attribute data are required: transaction price transaction date size (floor areas and/or number of bedrooms) type (detached, semi, terraced etc.) age (year built or suitably constructed age bands) location (exact address) changes (inflation/deflation) in house prices location area attributes property tax information A potentially significant variable that is missing from the list above is property condition. It is possible that older dwellings that have been refurbished or are well-maintained (new attic, extensions, new boiler, etc.) are going to have higher EPC ratings than poorly maintained buildings. Data on condition is not generally available in the UK at the dwelling level other than via the sample-based English Housing Survey. The Valuation Office Agency, widely regarded as the custodian of the most comprehensive set of dwelling attribute data, does not have up to date, detailed information on condition. Property tax information is not publicly accessible in England and Wales. It is possible to obtain Council Tax bands for small batches of dwellings via the Valuation Office website but not for large samples of several thousand dwellings. It is possible to obtain information from Communities and Local Government on the amount of Council Tax that each local authority charges on an annual basis. These amounts are expressed as average Council Tax for Band D; other bands can be calculated as they relate to Band D in fixed ratios. Using this data set, it is possible to investigate whether there is any impact on price paid as a result of variations in local authority Council Tax levels. Sources of data will need to be investigated in the first stage of the research. Key data holders are listed in Table 1 but more may be identified during Stage 1 of the project. The Land Registry record the address, property type and price paid for all freehold and most leasehold transactions in England 5 and Wales and this information has been publicly available since 1995. EPCs were introduced in September 2008 and therefore the first stage of this project would investigate the feasibility of obtaining transaction data from the housing market from that date onwards. The Land Registry data set is also commercially available in bulk form and several organizations have acquired the data and added further variables. Our enquiries in respect of this project and in previous work we have undertaken have shown Calnea to be a key source of real estate data, particularly regarding the additional data that they have added to the Land Registry data. We have obtained a quote from Calnea covering up to 1 million transaction prices with key property attributes such as type, number of bedrooms, year built and geo-coordinates matched to these prices. The company is now part of the Landmark Group and the research team has established relationships with staff at both Calnea and Landmark. Table 1 – Key data sources Data owner Legal status Data set Data items Land Registry An Executive Agency of the Lord Chancellor’s Department An Executive Agency of HMRC Transaction prices Title reference, address, price, quarter date of transaction, tenure Council Tax list Unique ID, Address, Council Tax band Calnea Private sector company Property attributes and prices Experian Public limited company Landmark Subsidiary company of the Daily Mail General Trust Various socioeconomic and demographic data sets Quest Property type, number of bedrooms, year built (1995 onwards), full address, transaction prices Wide range of modeled socioeconomic and demographic data Communities and Local Government Government Department English Indices of Deprivation Communities and Local Government Government Department English Housing Survey VOA Property attributes collected by mortgage valuers when assessing the value of dwellings for lending purposes LSOA-level data on income, employment, health and disability, education, housing and crime Dwelling level data on household characteristics and physical attributes Modelled data for property attributes and socio-economic characteristics of dwelling occupants are also available commercially from the information company Experian. Variables include house type, number of bedrooms, tenure, household income, number of occupants, age of main householder and length of residence. Experian collects data from a range of sources. The 2001 Census provides details of the neighbourhood and this is supplemented by Experian’s consumer survey and administrative data. The Experian model then derives variables for each address. In addition, Output 6 Area level demographic data are available from the Office for National Statistics. Property attribute data are collected and maintained by the Valuation Office Agency (VOA). Whereas Experian property attributes are modelled, the VOA, which is responsible for allocating homes in England and Wales to an appropriate Council Tax band, maintains a property attribute database and key attributes such as dwelling type, age and size are available for nearly all dwellings. However, these attribute data are not publicly available; only Council Tax bands for individual addresses are available. These data are free of charge from the VOA website but only downloadable in small batches. The ability to acquire and match Council Tax data from the VOA and match to the sample of transaction data would be investigated in the first stage of the project. Information on the private-rented sector and, in particular, rents paid is not readily available in England and Wales. Sources will be investigated including the Association of Residential Letting Agents, Housing Associations and the Local Government Association. E: Research Strategy and Analytical Framework This study aims to test whether energy efficiency performance proxied by EPC ratings is capitalised into house prices. It further seeks to identify whether the level of running costs of a property (proxied by EPC rating and local authority Council Tax costs) affects the transaction price of a property. The method of choice for studying the contribution of individual traits or characteristics of goods to their price is hedonic price analysis. This method will form the backbone of our empirical investigation into the research questions outlined above. In particular, this method allows us to control for a number of confounding factors such as age, size and location of a property in order to isolate the unique contribution of energy efficiency and property tax liability to house price. The analytical approach to determine the hedonic contribution of EPC rating and council tax to price is faced with the following problems which must be addressed within given time and resource constraints: First, a common problem is lack of control for unobserved heterogeneity that can arise from the local area. If these un-observables (e.g. attractive garden) are correlated to the observed attributes, then the estimates are biased. One way to address the issue is to include local area fixed effects (specified as dummy variables) in the model specification, assuming that correlated un-observables are time-invariant. In our cross-section model, we will explicitly control for such unobserved effects. Second, it is possible that a proportion the property units in the sample may have undergone 7 physical changes due to renovation. A renovation may affect both the price and the EPC rating. One way to address this concern is to form a sample of properties which are sold twice in the sample period i.e. repeat sales units for which it is reasonable to assume that those have not undergone significant changes between two transaction dates in terms of physical attributes. Therefore, we will also perform a hedonic analysis with only repeat sales transactions. Specifically, difference in sales prices between two transaction dates will be regressed on a set of property and unit attributes including the constant EPC ratings. This exercise will be able to estimate the extent to which growing awareness of EPC ratings and energy efficiency has affected levels of capital growth in residential dwellings. Third, an important risk in sale price analysis is that some properties may be more likely to be offered for sale than others (sample selection bias). This may be due to a property’s characteristics or the occupying household’s characteristics or a combination thereof. For example, less attractive properties might have a larger propensity to be sold since they are more likely to be occupied by transient and younger households. If this were the case, we might seriously underestimate or overestimate the effect of energy efficiency on price. The direction of this bias would be dependent on the differential characteristics of the households and properties occupying energy-efficient properties compared to the control group or general population. Appropriate econometric testing (two-step Heckman correction procedure) will be conducted to address this concern. If we find during Stage 1 that it is not feasible to obtain Council Tax payment or billing data at dwelling level, we propose an alternative approach that focuses on relative differences in Council Tax levels for ‘Band D’ properties across local authorities rather than differences across properties. This approach has the desirable property that it circumvents the inherent causality problem of actual Council Tax paid. This is due to the fact that more expensive dwellings incur higher Council Tax but it is primarily the value of each dwelling that determines the level of Council Tax paid and to a much lesser extent (or possibly even not at all) the other way around. More specifically, we will create a variable that expresses the indexed level of Band D Council Tax for each local authority as a percentage of the national average level. This variable will allow us to test in the hedonic regression model whether variations in Band D Council Tax both across local authorities and within the same local authority over time have any significant effect on prices. In summary, our analytical approach is two-pronged: we propose a repeat sales framework to address concerns about changes in unit attributes and a cross-section framework to address potential issues with selective samples and also to act as robustness checks. These regression-based models will be used to estimate the effect of EPC ratings and Council Tax levels on property prices and are suitable 8 for the task at hand in that they minimise potential selection and estimation biases that could invalidate the results. Section 2: Demonstration of experience in hedonic data analysis Appendix 2 contains a list of publications by the research team directly related to the proposed research project. Among the team members, there is significant experience in conducting large-scale hedonic studies. Dr Fuerst’s work, in particular, has been at the cutting edge of applying hedonic regression procedures to estimating the price effects of environmental performance on real estate pricing. Commissioned by DECC, Dr Wyatt has been involved in research conducting econometric modeling of domestic energy consumption for English households. Dr Nanda has previously undertaken a major hedonic analysis to study effects of school district performance on property values in US using transaction data. Having dealt with a large transaction dataset with potential issues and risk mitigation for such hedonic analyses, Dr Nanda will oversee database management and regression analysis. The data collection process as well as the application of these methods will be conducted by a team of researchers at the Universities of Cambridge and Reading with long-standing expertise in working with these complex and sensitive analytical tools. Brief biographical details of the members of the research team are provided below. Dr Franz Fuerst (FF) is the Principal Investigator of this project and will be responsible for ensuring the overall success of the proposed research as well as designing and applying the econometric modelling framework. He has conducted a number of research projects involving real estate market analysis and economic forecasting for public and private sector clients. He is currently Reader in Housing and Real Estate Finance in the Land Economy Department of Cambridge University and a Visiting Professor at the IREBS Centre of Sustainable Real Estate. He is also the Cambridge University Land Society Fellow (2011-14). Previous positions include Reader in Real Estate Economics at the University of Reading, Senior Consultant at BNP Paribas Real Estate and Research Fellow at the City University of New York. Main research interests include 'green' real estate economics, financial analysis of sustainable investments, portfolio and risk management, and real estate market forecasting as well as spatial economics. His research on the pricing of sustainable features in commercial properties is widely acknowledged as being among the first studies of the subject. His research was published in a number of top-ranked academic journals including Ecological Economics, Environment & Planning A, Energy Policy, Applied Economics, Journal of Air Transport Management, Real Estate Economics, Journal of Real Estate Research and Journal of Portfolio Management and he has won several best paper awards, most recently the 2011 Emerald 9 Outstanding Paper Award (jointly with Patrick McAllister). Professor Pat McAllister is a co-investigator of this project and will be responsible for interpretation, analysis and reporting of the research outputs. He is currently Professor of Real Estate Appraisal at the School of Real Estate and Planning at the University of Reading. His main research interests include real estate and sustainability, financial modeling of real estate developments and the pricing and appraisal of real estate assets. His research was published in a number of top-ranked academic journals including Ecological Economics, Environment & Planning A, Environment & Planning B, Energy Policy, Real Estate Economics, Journal of Real Estate Finance and Economics and Journal of Property Research. Dr Anupam Nanda (AN) is a co-investigator of this project and will be responsible for database management, empirical analysis and report writing. He has previously undertaken a major hedonic analysis with housing transaction data to analyse the effect of school quality on US house prices. He is currently working as Lecturer in Real Estate Economics and Finance, and Associate Programme Director for full-time MSc Real Estate at the University of Reading, UK. Previously, he worked with the Market Intelligence group of Deloitte & Touche in Mumbai. He was at the National Association of Home Builders (NAHB) in Washington DC, as Senior Research Economist, where his responsibilities included developing and implementing housing market research studies and was a member of the team forecasting state and metro area housing markets in US. Prior to joining NAHB, he worked as a graduate research assistant at the University of Connecticut, USA. He has also taught undergraduate Economics and Public Finance at the University of Connecticut during his graduate studies. His research areas include: dynamic interactions across urban and regional markets; housing market dynamics and forecasting; economic and econometric analysis of regulation; economics of sustainability and corporate social responsibility; applied econometrics. His teaching areas include: real estate economics; housing market analysis; quantitative methods. Dr Nanda holds PhD and MA in Economics from the University of Connecticut. His research papers have been published in Journal of Urban Economics, Journal of Real Estate Finance and Economics, and Cityscape etc. Dr Peter Wyatt (PW) is a co-investigator of this project and will be responsible for information management. This will involve the sourcing, sampling, collection, matching and administration of the data sets that will be required to build and test the hedonic pricing model. Dr Wyatt is a Chartered Valuation Surveyor who has conducted extensive teaching, consultancy and research in land management and valuation. He is involved in international land management projects and has a thorough knowledge of the theory and application of spatial analysis techniques for real estate research. Recent projects have investigated the energy performance of the domestic and non- 10 domestic building stock and he has worked with DECC on the development of a data framework for the monitoring of real estate energy consumption. Section 3: Explanation whether and how proposed approach would differ from existing hedonic pricing studies The Cambridge/Reading research team has a thorough understanding of the data and analysis issues that challenge real estate research of this nature. With regard to Stage 1 of the research project, the team will be able to apply its thorough knowledge of real estate and energy-related datasets. Given the timescale, it is important that the team undertaking this research be able to draw upon existing resources. Previous projects undertaken by the team in this field provide these resources. In particular, we are able to draw upon strong links to real estate data suppliers including Landmark and Calnea to acquire a large sample of dwelling prices and their associated attributes on which to conduct the hedonic study. While the study will utilise standard hedonic tools and techniques, there will be significant departure from existing practices. Most hedonic studies face perennial problems of unobserved effects and sample selection biases. A combination of cross-sectional and repeat sales analyses, as we are proposing in our proposal, will be able to disentangle these confounding issues. Specifically, use of EPC labels and council tax as hedonic characteristics involves model specification and econometric techniques to minimise biases arising from confounding factors at the unit and neighbourhood levels. The research team has wide experience of GIS and its application to real estate modeling. GIS will be used to geo-code each dwelling. This will enable household and lifestyle attributes recorded at an aggregated level (typically output area level or lower and medium level super output area level) to be included in the hedonic analysis. Data sets such as the Office for National Statistics Local Area Profiles and the English Indices of Deprivation published by Communities and Local Government include several variables that may affect price paid for dwellings. Inclusion of these attributes may prove to be useful in controlling for price effects. Section 4: Extent to which risks are identified and addressed Some potential areas and extent of risks can be identified at the onset. Table 2 summarises the risk assessment and our plans for mitigation. 11 Table 2 – Risk analysis Risk Non-supply of data Likelihood Low Impact High Bias in sample selection Medium Medium Data matching Medium High Data quality issues Medium Medium Omitted variables High Low Analytical risk Low High No identifiable impact Medium Medium Mitigation Previous experience of project team. Can use one of several private sector suppliers. Appropriate econometric techniques (e.g. two-step Heckman correction procedure) Two main areas of concern; matching with Landmark’s EPC data and other data sources that may be used. Experienced staff, time allowed for data cleaning and processing, check data quality before purchasing Appropriate econometric techniques (fixed effects and repeat sales method) Appropriate techniques (mainly tests for selection bias) A neutral or negative finding regarding the impact of energy efficiency (and Council Tax) on price cannot be ruled out a priori due to the presence of confounding factors at the unit and neighbourhood levels. Appropriate econometric technique will be employed to minimise such problems. The most significant risk involves data availability, quality and compatibility. While data sources with established track record have already been identified, there are potential challenges which may arise when the data is used in practice. It is usual for property attribute variables to be categorical (dwelling type and age band for example). These variables can be transformed into dummy variables. Generally speaking, there are two ways of handling location in a hedonic pricing model for dwellings. The first is to construct housing submarket areas that are relatively homogeneous in terms of price. The second is to include variables that measure price sensitive location attributes such as distance variables (distance to town/city centre, distance to main transport hub for example) and area variables (such as school catchment or neighbourhood crime rate). The method for handling location depends on several factors including data availability and size of sample. While we have recognised some potential areas of risk, we have also identified appropriate tools for mitigation. These tools are well-established in the literature to tackle such issues. Section 5: Delivery plan: tasks and milestones We have the capacity to complete this project within the specified timescale of early January 2012 to the end of March 2012. We would also be able to provide weekly updates and produce brief output reports at each stage. We outline the proposed work timetable in Table 3 and additional detail is provided below. 12 Table 3 – Delivery plan Tasks Milestones 1. Data collection and preparation Survey of the literature; pilot study to identify potential data problems (Stage I) Full sample data collection, compilation and quality checks (Stage II) Hedonic regression estimation (Stage III) Empirical analysis/sensitivity tests (Stage III) Progress reporting (ongoing) 2. Data analysis 3. Reporting January February March Draft Report (Stage IV) Final Report and Dissemination (Stage V) Tasks 1. Data collection and preparation a) Acquire core data set (property prices and attributes) b) Screen for data errors, data cleaning, database management (including mapping of dwellings using GIS) d) Matching of dwelling-level database with other sources (e.g. ONS Neighbourhood statistics, English Indices of Deprivation, etc.) e) 2. 3. Prepare database for external matching of EPC data and liaise with Landmark Data analysis a) Develop and implement hedonic repeat-sales modelling framework b) Perform cross-section hedonic analysis with appropriate robustness checks Reporting a) Liaise with DECC on weekly progress updates etc. b) Prepare and deliver final report Two stages of data acquisition and matching are envisaged. Initially, we would acquire data for a small, geographically specific, pilot sample of 5,000 dwellings. This pilot study would allow us to examine the data sets for missing data, possible ambiguities and so on. Metadata describing the 13 applicability or fitness for purpose of each data set for a residential hedonic pricing model would be an output from this stage. This will be in terms of: Lineage and provenance: details of the source and history of the data and a description of the set of processes that are used to produce a dataset. This would include how the data were digitised and from what sources, when they were collected and by whom, and what steps were used to process them. Availability: to what extent are the data publicly available? There are several dimensions to this question: at its simplest, it asks whether the data are released into the public domain at all. If the data are released then is there a cost involved. Another important dimension is whether the data are aggregated or anonymised prior to release and, if so, to what extent. Ideally, data should be disaggregated to the individual property level. Coverage: this aspect of fitness for purpose concerns the degree to which a data set conforms to its specifications. Are all the records that should be logged present? Content: the final and undoubtedly the most important aspect of fitness for purpose is the content of the dataset. Having identified and resolved where possible any ambiguities and data matching issues, a larger sample of dwellings would be acquired. Using a three-way classification of size, type and age of dwelling, it is envisaged that a sample of 500,000 records would be sufficient. The sampling procedure will aim to use sufficient properties in across England for an unbiased, uniform random sample to be drawn. In order to assess the robustness of our analysis, the sample will include repeat sales observations. The main model building and analysis stages can then begin. . 14 Appendix 1 - Studies on price effects of energy and environmental labelling in real estate markets Author(s) and status Miller. Spivey and Florance (2008) Published in Journal of Real Estate Portfolio Management Wiley, Benefield and Johnson (2010) Published in Journal of Real Estate Finance and Economics Data Approach Findings on price differentials ‘Filtered’ sample of Class A buildings (larger than 200,000 sq ft, multi-tenanted, over five stories, built after 1970) to compare to 643 ES buildings. 927 sale transactions between 2003 and 2007. Breakdown between LEED and ES sale price observations is unclear. Class A office buildings only. 46 metropolitan markets (25 markets for sales). Hedonic OLS regression for sale prices only. Finds no statistically significant sales price premium. Hedonic OLS and 2SLS regressions for rental and occupancy rates. Hedonic OLS and 2SLS find rental differentials of 15-17% for LEED and 79% for ES. Breakdown between LEED and ES is unclear. We estimate 30 LEED and 440 ES rental observations and 12 LEED and 70 ES sales observations. Control sample seems to be other buildings in same metropolitan area. No controls for microlocation effects. Hedonic OLS model of sales prices in absolute form. Estimate sale price premiums of $130 psf and $30 psf for LEED and ES. Controls for major markets but none for quality. Other findings and potential limitations Occupancy rate is 2-4% higher for ES compared to non-ES filtered sample. Report 30% lower operating expenses based on energy costs. Hedonic OLS and 2SLS with occupancy rate as dependent variable finds occupancy rate differentials of 16-18% for LEED and 10-11% for ES compared to control group. Key issue is location control. Metropolitan area may be too large. May be confusing location with certification effects. Potential omitted variable bias linked to dual certified buildings not taken into account. Eichholtz, Kok and Quigley (2010) To be published in American Economic Review Weighted average rents for 694 certified buildings. Sale prices for 199 certified buildings 2004-7. Hedonic OLS regressions for rental and sales prices. No statistically significant rental premium for LEED. 3% rental premium for Energy Star. Breakdown between LEED and ES is unclear. Control sample is buildings within 0.25 miles of certified building. No statistically significant sale price premium for LEED. 19% sale price premium for Energy Star. 15 No systematic treatment of data errors. Find a positive relationship between energy efficiency measure and level of rental premium. Potential omitted variable bias due to dual certified buildings not taken into account. LEED result is puzzling and may be due to dual certification problem. Fuerst and McAllister (2011) Asking rents for 990 ES and 210 LEED certified buildings. Published in Real Estate Economics Sale prices for 662 ES and 139 LEED certified buildings 19992009. Chegut, Eichholtz, Kok and Quigley (2010) Sale prices for 78 office BREEAM offices in UK. Sales data obtained from Real Capital Analytics Draft working paper ‘Achieved’ rents for 1011 offices obtained from CoStar Dermisi (2009) Published in Journal of Sustainable Real Estate Fuerst and McAllister (2009) Published in Journal of Sustainable Real Estate Fisher and Pivo (2009) Draft working paper Hedonic OLS regressions for rental and sales prices. Control sample is based on buildings within same CoStar submarkets. Hedonic OLS regressions and PSM for rental and sales prices. Location control is buildings with 500m radius. 6% rental premium for ES and LEED certified buildings. No systematic treatment of data errors. Potential omitted variable bias issue due to dual certified buildings. 35% and 31% price premium for LEED and ES. No systematic treatment of data errors. Estimate rental premium of 16-20% to eco-certification. Excellent – 22%-27% Very Good – 18%-19% Good – 8%-11% Pass – 17%-18% Controls for spatial auto-correlation. In two out of three specifications – no statistically significant sale price premium No age control reported in rental regression. Included? No discussion of controls for lease terms, lease incentives unexpired lease length, tenant quality, building quality. Appraisal estimates of Market Values for 351 LEED-rated US office buildings. Study period is first half of 2009. Robust, MLE and fixed effects regression models. Provides detailed results for NC, EB and CS sub-samples. Results are inconsistent between specifications. For LEED NC, estimates a 36% discount for LEED Silver. LEED EB has a 118% premium. Small sample problems in the sales data? Results do not seem plausible. It is not clear what the benchmark variable is for value differences - “other LEED buildings”? Seem to be an absence of location controls. Occupancy rates for 292 LEED and 1,291 ES office buildings from a sample taken in December 2008. OLS and quantile regression. Estimate 8% occupancy premium for LEED offices and 3% premium for ES. Did not control for potential omitted variable bias due to dual certification. Quantile regressions find that, for ES offices, increased occupancy is concentrated in first two deciles only. Investment performance of RPI properties – 209 Energy Star, 158 in regeneration areas, 669 near transit stations. Hedonic OLS procedures. Estimate 12.5% premium on appraised capital value for Energy Star compared to buildings in same CBSA. CBSAs are the location controls. Estimates 1% higher occupancy rates in Energy Star buildings. Estimate that utility costs were 10% lower in Energy Star offices. Energy Star offices have significantly lower income and total returns. Location controls are unlikely to fully 16 Deng, Li and Quigley (2011) Regional Science and Urban Economics forthcoming Residential sales prices of 74,278 dwelling units in 1439 projects in Singapore between 2000-2010. Hedonic OLS and GLS procedures. Sample refined using PSM. 4% of sample had Green Mark by 2009. Had 18269 transactions in 62 residential projects with Green Mark were matched against 55982 transactions. Location control is 55 planning areas. They also use project fixed effects in one model specification. Significantly different results for different models PSM Regression Estimate average price premium for Green Mark of about 4-6%. Platinum – 14% Gold Plus – 2.3% Gold – 5.5% Certified – 0.1% 51% Gold 21% Gold-plus 19% Green Mark 3% Platinum Draft working paper A blend of residential asking prices (80207) and actual (2063) sale prices for Tokyo 2005-2009. Estimate average price premium for Green Mark of about 14-21%. Platinum – 21% Gold Plus – 15% Gold – 15% Certified – 10% Estimate a 5% asking price premium for Green Label. Hedonic OLS procedures. Appears that approx 14%-15% of the sample had eco-labels. Brounen and Kok (2009) 18,190 residential sale prices in the Netherlands in 2008 for buildings with EPC rating. It is a concern that the premium for Gold is higher than the Gold-Plus in the PSM model. Project Fixed Effects Regression Have data on type of sale and buyer type. Shimizu (2010) capture the effects of variations in location quality. No explanation is offered for the fairly dramatic differences in estimated premium for the two model specifications. Hedonic OLS procedures Forthcoming in Journal of Environmental Economics and Management For ‘better’ model estimate a 3.4% premium for units rated A, B or C. Compared to buildings rated G, they estimate premiums of 12%, 7% and 4% for A, B and C respectively. No statistically significant effect estimated for time on market. 17 Some puzzling results. Effect of energy efficient equipment is significantly negative. Premium is lower for better environmental performance in some variables e.g. insulation and long life There are potential limitations due to lack of controls for quality. Higher rated buildings may be located in higher value locations within urban areas and/or have superior construction and/or specification. For instance, the only quality variable is condition and it is notable that, when it is included in the model, the premium drops substantially. Fuerst and McAllister (2010) Ecological Economics Eichholtz, Kok and Quigley (2010) Working paper Weighted Average rents for 1846 Energy Star, 268 LEED and 254 dual certified office buildings. Sale prices for 876 ES, 87 LEED and 123 dual certified office buildings 1999-2009. Occupancy rates for 2111 ES, 313 LEED and 254 dual certified office buildings. Two samples – 2009 and 2007 2007 694 green office buildings in a total sample of 8182 2009 – 2687 observations in a sample of 26794 Sales 744 rated 5249 control Rents 1943 rated 18858 control OLS and robust regression techniques. Estimate rental premium of 3%-4% for ES. 4%-5% for LEED and 9%-10% for dual certified. Control sample is based on buildings within same CoStar submarkets. Estimate sale price premium of 18% for ES, 25% for LEED and 28%-29% for dual certified buildings. Estimate 1%-3% higher occupancy rate for ES and 5%-6% lower occupancy rate for LEED. When comparing performance of 2007 sample, they find that estimated rental premium goes down to 1.2% Use panel data approach to compare 2007 and 2009 samples. WLS hedonic modelled with propensity score weighting of observations For 2009 sample, estimate rent premium of 2% for ES and 6% for LEED. Estimate sale price premium of 13% for ES and 11% for LEED. Breakdown between LEED and ES is unclear. Mentions 209 LEED rental buildings later in paper. Attempt to control for the potential of data errors and the inclusion of dual certified buildings to produce biased results. No control for potential bias due to spatial auto-correlation. The sale price premiums seem high. Is there an omitted variable problem? Does not control for potential omitted variable bias due to dual certification. No apparent controls for outliers or data errors. Why is aggregate green premium higher than LEED and ES? Why is ES sale price premium higher than LEED – dual certification problem? Finds that LEED registration is associated with rental premium of 7.9%! Not clear how potential tendency for LEED to have higher levels of single occupancy is handled in effective rent estimations. Also analyse the effect of LEED scores on rental premiums but not on sales premiums. The summary statistics contain some puzzling numbers. Whilst the control buildings have higher average rents and sale prices than green labelled buildings, the control buildings are on average 18 older, smaller and of lower quality (70% Class B or C compared to 25% of labelled buildings). Yoshida and Sugiura Presented in March 2011 1154 buildings evaluated under Tokyo Green Building Program which is mandatory for buildings exceeding 5000 square metres. Use standard hedonic regression procedure. Find a statistically significant discount of 5.5% for labelled buildings. Discount is robust in a number of tests. When they estimate the price effects of the different components of the rating, they find mixed results. The individual drivers of the negative premium tend to be increased energy efficiency, water efficiency and planting. They suggest that perceived additional maintenance costs associated with these features may produce the discount. They obtain a total sample of 34862 sales of condominiums. It is not clear how many condominiums are TGBP rated. Jaffee, Stanton and Wallace (November 2010) 15230 transactions (2001-10) for office buildings located in 43 US metropolitan areas. Working paper 545 Energy Star properties (3.6% of total). Only 142 rated at the time of sale (0.93% of total). Zheng, Wu, Kahn and Deng Have data of total expenses (1473), NOI (1532) and cap rates (2323) for a subset of the sample. (Presumably) Due to missing variables, this sample decreases substantially in the hedonic models. In the absence of an eco-label in China, an index of building Find evidence of lower depreciation for eco-labelled condominiums. Estimate an Energy Star premium of 13.5% when total expenses and operating costs are excluded as confounding factors. When they are included in the model of a subset of the data, the ES premium becomes statistically insignificant. Although sample size for Energy Star is not stated, it is likely to be quite small. Use standard hedonic regression procedure. In a subset of 816 observations, they find no significant ES effect on NOI, cap rate or operating expenses. However, again sample size of ES is not indicated and may be small. Estimates a green premium of 9.1%. Uses standard hedonic procedure. 19 No control for potential bias due to spatial auto-correlation. The authors spend a great deal of effort trying to falsify their finding of a discount. However, their robustness checks further confirmed their findings. When presented, it was argued that the finding was consistent with research in the 1980s that found that buyers tended to be sceptical of non-familiar environmental technologies when purchasing homes. Additional costs of maintenance are emphasised. The location control seems broad given the fact that ES buildings tend to be concentrated in CBDs. If sample size of ES is small, weak effects may be missed. Not clear if authors have tested for multi-collinearity. If there is a negative association between operating expenses and ES, it is possible that ES coefficient may be biased. It is not clear how the premium is estimated. The result implies that Feb 2011 Fuerst and McAllister Energy Policy, published 2011 greenness is estimated from marketing claims. Apply this index to 1992 residential building complexes constructed 2003-2008. Examines effect of EPC rating on yield, Market Value and Market Rent for 708 commercial property assets in IPD UK. Includes 23 BREEAM rated buildings. Date of data is Q3 2010. buildings were rated in a binary manner. However, the paper describes the creation of a relative score. Uses standard hedonic procedure. Finds no significant effect of EPC rating on Market Rent and Market Value. Very similar results for yield estimation. For one EPC rating (E compared to G for retail) was the coefficient significantly negative at the 10% level. Given the large geographical scope of the sample and the number of EPC and geographical ‘segments’, it is likely that there were small sample effects. Kok and Jennen May 2011 Examines the effect of EPC rating and Energy Index on 1072 rental transactions in Netherlands for the period 2005-2010. It is not clear how or whether separate groups of green buildings were identified. If they were identified, it is not clear how many there were. Paper argues that a larger sample is needed to provide a robust estimation of whether weak effects are being missed. The BREEAM results were similar. The coefficient on the BREEAM dummy was statistically significantly negative at the 10% level. Uses standard hedonic procedure. Finds a rental premium of approximately 7% for buildings rated C or lower compared to buildings rated D and above. Compared to D rated buildings, find significant premiums of about 10% for C rated and 5% for B rated. No significant discount for E, F and G rated buildings compared to D rated. Working paper. There may be a potential omitted variable problem. Buildings rated Class A, B and C may be better quality than buildings with inferior performance. The level of energy efficiency may be correlated with other unobserved quality variables e.g. design, interior finishes etc The pattern of premiums seems odd. Premiums decline from C to A rather than increase. Surprisingly, age of building does not have a statistically significant effect on rent. The sample of transactions covers the period 2005-2010. When were EPCs 20 introduced in Netherlands? For the UK, it was 2009. Harrison and Seiler Published in Journal of Property Investment and Finance 2011 Investigates whether there are rental price and occupancy rate premia in LEED and Energy Star certified office buildings. Also looks at variations in nature of variations focussing on the hypothesis that political characteristics determine level of premium. Uses hedonic procedure to investigate rent determinants. Seem to omit a number of variables – e.g. size, land area, stories. Does not report on price effects of ecolabel per se. However, the beta for the non-certified variable (0.93) implies a rental premium of 6%-7%. Estimate that premiums are higher in Democrat voting areas. No information is provided on number of assets in sample nor number of eco-certified assets. Newell, McFarlane and Kok Report for Australian Property Institute September 2011 Compares 206 NABERS rated office buildings with 160 nonNABERS rated buildings in Sydney and Canberra in March 2011. 23 (4-6) Green Star rated buildings were also included. Covers 51% of the total office market. Uses hedonic procedure to investigate rent and value (“a constructed proxy which incorporates gross rent, vacancy, incentives, outgoings and yields”) determinants. Seem to omit a number of potential price determinants – e.g. stories, age, unexpired lease terms, tenant quality etc 21 Providing no indication of statistical significance, the study finds a small rental and value premium for high NABERS-rated buildings 0.3% and 1.9% specifically. Finds a discount in value for offices with NABERS rating of 2.5 stars or less. In the UK, buildings may have multiple EPCs. This issue is not discussed. Much more detail required on sample and modelling to evaluate this paper. Using rents/vacancy rates of noncertified assets as independent variables in regression model produces high explanatory power but introduces issues of endogeneity and multi-collinearity which are not discussed in the paper. The limited number of control variables may also be a problem. For instance, since there is a well-known positive correlation between educational attainment and Democratic voting, there may be an omitted variable bias. The limited number of control variables may be a problem. The lack of any reporting of tests for statistical significance is a major omission. Appendix 2 - Relevant Publications by the Research Team Bruhns, H. and Wyatt, P. (2011) A data framework for measuring the energy consumption of the nondomestic building stock, Building Research & Information, 39, 3, 211-226 Caijas, M., Fuerst, F., McAllister, P and Nanda, A. Do Responsible Real Estate Companies Outperform Their Peers? under review in Real Estate Economics. Clapp, J., Nanda, A., and Ross, S. (2008). Which School Attributes Matter? The Influence of School District Performance and Demographic Composition on Property Values, Journal of Urban Economics, 63, 2, 451-466. Fuerst, F., Kontokosta, C. and McAllister, P. Spatial Determinants of Green Building Adoption, under review in Ecological Economics. Fuerst, F. and McAllister, P. (2011) The Impact of Energy Performance Certificates on the Rental and Capital Values of Commercial Property Assets: Some Preliminary Evidence from the UK, Energy Policy, 39, 6608-6614. Fuerst, F. and McAllister, P. (2011) Eco-labelling in Commercial Real Office Markets: Do LEED and Energy Star Offices Obtain Multiple Premiums?, Ecological Economics, 70, 6, 1220-1230. Fuerst, F., McAllister, P., Van de Wetering, J. and Wyatt, P. (2011) Measuring the Financial Performance of Green Buildings in the UK Commercial Property Market: Addressing the Data Issues, Journal of Financial Management in Property and Construction, 16, 2, 163-185. Fuerst, F. and McAllister, P. (2011) Green Noise or Green Value: Measuring the Price Effects of Environmental Certification in Commercial Buildings, Real Estate Economics, 39, 1, 46-69. Fuerst, F.; Reichardt, A.; Rottke, N.; Zietz, J. (2012): Sustainable Building Certification and the Rent Premium: A Panel Data Approach. Journal of Real Estate Research. Published online. Fuerst, F. and McAllister, P. (2009) An Investigation of the Effects of Eco-Labelling on Office Occupancy Rates, Journal of Sustainable Real Estate, 1, 1, 49-64. Fuerst, F. (2009): Building Momentum: An Analysis of Investment Trends in LEED and Energy-StarCertified Properties. Journal of Retail and Leisure Property, Vol. 8/4, 285-297. McAllister, P. (2009) Assessing the valuation implications of the eco-labelling of commercial property assets, Journal of Retail and Leisure Property, 8, 4, 311-322. McAllister, P. Editor of Special Edition (2009) Sustainable Property: Building the Research Base, Journal of Retail and Leisure Property, 8, 9, 239-322. van de Wetering, J. and Wyatt, P. (2010) Measuring the carbon footprint of existing office space, Journal of Property Research, 27, 4, 309-336 van de Wetering, J. and Wyatt, P. (2011) Office sustainability: occupier perceptions and implementation of policy, Journal of European Real Estate Research, 4, 1, 29-47 Dr Wyatt has also contributed substantially to the National Energy Efficiency Data-Framework: Report on the development of a data-framework and initial analysis, June 2011, Department of Energy & Climate Change 22