A review of green roof incentives as motivators for the expansion of green infrastructure in European cities
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Scientific Review – Engineering and Environmental Sciences (2019), 28 (4), 641–652 Sci. Rev. Eng. Env. Sci. (2019), 28 (4) Przegląd Naukowy – Inżynieria i Kształtowanie Środowiska (2019), 28 (4), 641–652 Prz. Nauk. Inż. Kszt. Środ. (2019), 28 (4) http://iks.pn.sggw.pl DOI 10.22630/PNIKS.2019.28.4.58 Ewa BURSZTA-ADAMIAK, Wiesław FIAŁKIEWICZ Faculty of Environmental Engineering and Geodesy, Wrocław University of Environmental and Life Sciences A review of green roof incentives as motivators for the expansion of green infrastructure in European cities Key words: green roof, green infrastructure, adequate space for green infrastructure. incentives, benefits, European cities As a result, building green roofs, which are one of the green infrastructure solu- tions, is becoming increasingly perceived Introduction as an action with a beneficial influence on the urban environment. Apart from City development for residential, the possibility to recreate biologically commercial and transportation purposes active areas in cities (partly, e.g. 50% in contributes to the disappearance of green Poland), numerous studies confirm the areas. Only in Austria, 15–25 ha of land capacity of green roofs to retain rainwa- are sealed every day (Pendl, Hüfing, ter and delay runoff, as well as to reduce Muerth, Tributsch & Jäger-Katzmann, the amount of pollutants in air, improve 2009). The urban sprawl tendency only the microclimate and positively influence enhances this phenomenon. The develop- the urban heat island effect (Shafique, ment of biologically active areas leads to Kim & Rafiq, 2018; Burszta-Adamiak, the loss of recreation areas and potential Stańczyk & Łomotowski, 2019). Ano- habitats. The biodiversity of the given ther factor that is increasingly appreci- land decreases and the proportional share ated in cities, is the fact that green roofs of specific elements in the water and heat provide friendly, green leisure spaces and balance become distorted. According to improve the aesthetical values of build- the World Health Organization (WHO), ings (Sutton, 2014). Other argument that the minimum green areas should be supports their construction is the possi- 50 m2 per urban agglomeration resi- bility to reduce carbon footprint in cities dent (Russo & Cirella, 2018). However, (Ugai, 2016) and direct water footprint the reality is different. In many Euro- (Fialkiewicz et al., 2018). Green roofs pean cities, urban areas do not provide can also be included in the “smart city” A review of green roof incentives as motivators for the expansion... 641
policies adopted by numerous cities, tional and regional government policies, where the aim is to improve service effi- in several Asian and American cities ciency and urban quality of life by using (Chen, 2013; Olubunmi, Xia & Skitmore, new technology (Brudermann & Sang- 2016). A review of the green roof legisla- kakool, 2017; Shafique et al., 2018). The tion, policies and tax incentives in North increased interest in these solutions also America can be found also at the website results from the fact that cities are will- of the Environmental Protection Agency ing to present themselves as regional, na- (EPA, 2019). As a result of the growing tional or global centres of active adapta- interest in the benefits of constructing tion to climate changes. This is reflected green roofs in Europe, including in Po- in the provisions of numerous strategic land, the need to introduce various kinds documents, climate change adaptation of incentives for the popularisation of plans, in technical guidelines, as well as green roofs in urban areas has been no- in legal regulations, including, among ticed in European cities as well. The main others, construction law and water man- reasons for the realisation of investments agement regulations. with green roofs in European countries The current state of knowledge con- include the need to increase biologically firms that measurable effects of the green active areas in towns, to reduce carbon roofs application in urban areas may be emissions of cities, mitigate heat island achieved first of all when large green effects and improve urban flood control. areas located near one another are con- The main aim of this paper is to re- structed. Due to that, the construction of view the European experiences (includ- green roofs in cities should not be limited ing Polish) in the area of implementing to single investments scattered all over tools used to motivate public investors the town. The surface of roofs in urban as well as individuals to construct green areas account for approx. 40–50% of the roofs. All information gathered and col- total sealed areas in cities (Stovin, Ve- lated were used to identify the most suviano & Kasmin, 2012), so the poten- popular initiatives for the construction tial for constructing green roofs is much of green roofs and to formulate recom- higher than the current state of their real- mendations for creating future incentive isation. One of the reasons of the limited programmes addressed to various groups number of green roof investments is the interested in constructing green roofs in insufficient number of incentives for in- urban areas. vestors which might reduce the relative- ly high initial construction costs of such solutions and contribute to raising social Material and methods awareness of the possibility to construct such roofs and the need to maintain them The review of incentives aimed at in good condition throughout their op- the popularisation of constructing green eration period. roofs in European cities was based on in- So far, the practices of stimulating formation contained in research articles, the development of green roofs have technical reports, design guidelines, law been recognised quite well through na- regulations and case studies. The scope 642 E. Burszta-Adamiak, W. Fiałkiewicz
of the analysis included both financial Czech Republic. In some German lands and non-financial incentives. Each of the and certain Dutch cities, local govern- incentives encourages the installation of ment policy combines the possibility green roofs on existing or new buildings. to obtain subsidies with statutory obli- The analysis covered 52 cities located gation to construct a green roof during in 11 countries in Europe. The period the construction of new buildings. This of implementing the incentives were the incentive involves various requirements years 1970–2017. All the analysed moti- that have to be met if a green roof is con- vational tools are still used in the cities structed (e.g. a flat roof or a specific roof included in the review. inclination). Other financial solutions used in practice are tax allowances (e.g. real property tax allowance). This form Results and discussion of incentive was introduced in Wrocław (Poland) in 2015. Based on it, the usable The first initiatives aimed at support- areas of residential premises located in ing the construction of green roofs in buildings, on which green roofs were European cities were introduced in Ger- constructed while the resolution was many in the 1970s (Brudermann & Sang- effective, were exempt from tax. The kakool, 2017). Since that time, consider- amount of tax allowance depends on ing the measurable benefits from their im- the number of floors in the building, on plementation that translated into a grow- which the green roof was constructed ing number of investments with green and the surface area of the green roof roofs, an increasing number of countries (the share of the green roof area in the have become interested in green policies total surface of the roof) (Resolution for sustainable urban development. XV/268/15). In several cities (e.g. Düs- Local authorities, who decide wheth- seldorf, Hamburg), constructing a green er to grant subsidies and to what activi- roof results in decreased fees for dis- ties and regulate the principles of eligi- charging stormwater and snowmelt to bility for such donations, are important the sewage system. elements in promoting environmentally Another group of motivational tools friendly solutions. The initiatives taken are non-financial incentives. They in- with the aim to increase the surface area clude instruments that focus on gratifica- of green roofs in cities are divided into tion (gratifying incentives). Most of the financial or non-financial incentives society has a positive attitude towards (Tables 1 and 2). The first ones consist investments that comply with green in granting financial support aimed at policy and receive various awards and convincing the potential investors to green certificates for sustainable devel- construct a green roofs. This group of opment. As a result, residents will be incentives includes subsidies or dona- more willing to purchase such residen- tions granted to reimburse part of the tial premises. Such incentives involve costs incurred on the realisation of the granting additional points during the investment. This solution is common in green buildings certification process, i.e. Belgium, Germany, Switzerland and the the Building Environmental Assessment A review of green roof incentives as motivators for the expansion... 643
Method (BEAM) which was established sation. For example, the weighting of in Hong Kong in 1996 (BEAM Society, surfaces with vegetation unconnected to 2010) or the Leadership in Energy and soil below is 0.5; of green roofs is 0.7 Environmental Design (LEED) which and that of surfaces with vegetation con- is a certification rating system devel- nected to soil below is 1.0. The develop- oped by the US Green Building Council ers can thus use a wide range of options (USGBC, 2009). During the certification, combining different areas with differ- 1–2 points are awarded additionally for ent types of surfaces for achieving the ensuring biodiversity on roof surfaces. required standard. Such planning tools This results in the necessity to construct have different names throughout Europe, green roofs taking into account various such as green space factor, green points plant species and to design areas that will system, the maximum density of built- foster the development of small fauna. up area or green-area-per-capita factor One of the tools used to reduce the (Kruuse, 2011). surface of sealed areas in towns is the The non-financial incentives also enforcement of land usage intensity and include the so-called secondary motiva- the surface of biologically active areas. tional tools, i.e. those that are executed in Due to that, non-financial incentives the “background”, alongside other forms also include solutions that introduce the of incentives. They are realised in all the indicators taken into consideration in analysed European cities. They consist compensatory environmental activities. in providing expert designer support as One of such factors is the Biotope Area well as marketing and legal assistance Factor (BAF), developed in the 1990s in at the stage of planning, designing and Berlin (Badach & Raszeja, 2019). The realisation of the investment. Such form BAF factor enables to classify land sur- of support not only allows the investor faces depending on their ecological val- to save time, but, first of all, to minimise ue, based on evapotranspiration capacity, the risk of an erroneous project and to permeability, possibility to store rain wa- expedite formal procedures. Market de- ter, relationship to soil functioning and mand-related incentives and educational provision of habitat for plants and ani- incentives are equally important. Ex- mals. The BAF factor is calculated as the amples of such tools are those that are quotient of biologically active area for based on promoting the benefits of green the given area to the total surface area roofs in terms of the pro-environmental of the land plot, according to the set of actions of the investor (improved micro- assumptions. The obtained results con- climate, reduced energy consumption in stitute the basis for formulating target buildings, etc.) aimed at improving the BAF factors for specific urban func- quality of life of residents. Other types tions, which the developers are obliged of promotional instruments are market to comply with at the stage of obtaining demand-related incentives. These tools building permits for new investments. use the knowledge about the increased The higher the BAF factor, the more im- demand for buildings with greenery and portant is the given type of biologically the fact that buyers are willing to pay a active area in environmental compen- higher price in comparison to traditional 644 E. Burszta-Adamiak, W. Fiałkiewicz
TABLE 1. Financial incentives in selected cities (own studies based on Carter & Fowler, 2008; Claus & Rousseau, 2012; Boas Berg, Radziemska, Adamcová & Vaverková, 2017; Brudermann & Sangkakool, 2017) COUNTRY; City Type of financial support Subsidies – co-financing the construction of green roof: 8–25 EUR·m–2 (max. 2,200 EUR per project). Additionally, co-fi- AUSTRIA; Vienna nancing maintenance costs: 0.19 EUR·m–2 (Inspection twice a year, removal of growing trees, cutting grass). Subsidies – co-financing the construction of green roof: BELGIUM; Flanders 31 EUR·m–2. Subsidies – co-financing the construction of green roof: around CZECH REPUBLIC 18 EUR·m–2. Subsidies – co-financing the construction of green roof: up to GERMANY; Darmstadt 5,000 EUR. 50% reduction of the fees for rainwater and snowmelt discharge GERMANY; Düsseldorf for a constructed green roof. Subsidies – co-financing the construction of green roof: GERMANY; Esslingen, Stuttgart 17.9 EUR·m–2, max. up to 50% of the costs. Real property tax allowance (up to 50%), provisions in the Hamburg Strategy on the realisation of the green smart city concept; the Ministry of Environment and Energy provides financial support needed for the construction of green roofs GERMANY; Hamburg (a total of 3 million EUR by the end 2019), co-financing up to 60% of the costs of green roof construction, reduction of storm- water fees up to 50%. If the green roof is not connected to the sewage system, then stormwater fees are not charged. Subsidies – co-financing the construction of green roof: 30 EUR·m–2, reduced stormwater and snowmelt fees (buildings GERMANY; Munich with green roofs of a height up to 10 cm and a pitch lower than 15° pay fees reduced by up to 70%). NETHERLANDS; Alphen aan den Rijn, Almelo, Amsterdam, Ams- telveen, Apeldoorn, Co-financing of the construction of green roof: 30 EUR·m–2. Capelle aan den IJssel, Den Haag, The maximum amount requested is 2,500 EUR for individuals Groningen, and 25,000 EUR for the construction of apartment buildings Den Bosch, Leeuwarden, Leiden, and businesses. The maximum subsidy is 50% of the total roof Nijmegen, Nieuwegein, Rotterdam, cost. Soest, Utrecht, Tilburg, Zoeter- woude, Zwijndrech Local legal regulations on the exemption of usable areas of resi- dential premises from real property tax (up to 100%) as part of POLAND; Wrocław the project of intensification of the development of green areas in the city of Wrocław (2015–2021). Reduced stormwater fees (based on the annual amount of storm- SWEDEN; Stockholm water discharge per building). SWITZERLAND; Basel, Zurich, Subsidies – co-financing the construction of green roof: Lucerne 32 EUR·m–2. A review of green roof incentives as motivators for the expansion... 645
TABLE 2. Non-financial incentives in selected cities (own studies based on Carter & Fowler, 2008; Boas Berg, Radziemska, Adamcová & Vaverková, 2017; Brudermann & Sangkakool, 2017; Wolański, 2019) COUNTRY; City Type of non-financial support The Ministry of Environment together with the State Environ- CZECH REPUBLIC mental Fund of the Czech Republic announced a new continu- ous call in the New Green Savings Program (2017–2021). Green roofs are a part of the Wastewater Plan, the Climate Plan of the City of Copenhagen, some technical guidelines, e.g. the guidelines for sustainability in constructions and civil works DENMARK; Copenhagen and the city’s Strategy for Biodiversity. Since 2010 green roofs are mandated in most new local plans. Legislation – green roofs are required for all newly constructed roofs with a pitch of less than 30°. GREAT BRITAIN; London, West- Provisions in the Climate Change Adaptation Strategy set re- minster, Camden, Islington, Hack- quirements for green roofs in new buildings in London’s Cen- ney, Tower Hamlets, Southwark, tral Activities Zone policy area. Lambeth, Kensington, Chelsea Legal regulations – since 2015 all new buildings in commercial FRANCE zones must be partially covered by either green roofs or solar panels. Realisation of numerous programmes aimed at making the city GERMANY; Berlin greener, e.g. the Courtyard Greening Programme (1983–1996); Biofactor – Biotope Area Factor (BAF). Legal regulations – each newly constructed or modernised GERMANY; Essen building in the city centre should contain green areas. Legal regulations – all roofs of a pitch below 12° and all roofs GERMANY; Esslingen, Stuttgart of new buildings should be green. Legal regulations – flat roofs of a surface area over 100 m2 have GERMANY; Munich to be green to designate the land area for other purposes. SWEDEN; Malmö Biofactor – Green Space Factor (GSF). The requirement to construct green roofs on all newly construc- SWITZERLAND; Basel, Zurich, ted buildings with flat roofs; the requirement to select compo- Bern, Lucerne nents to increase biodiversity. buildings. In such event, developers treat conducted review of motivational solu- green roofs as added value of their in- tions demonstrates that the most com- vestment, which is an additional incen- monly used forms of incentives are direct tive for their potential customers. subsidies for the construction of green Introducing incentives to popularise roofs and legal regulations (Table 3). green roofs proves the need to perform Practice shows that these are the solu- actions aimed at increasing biologically tions that achieve the best results. This active areas in cities and at increasing is proven by Germany, which has a long city resistance to climate changes by tradition of using this type of incentives. introducing nature based solutions. The The surface of green areas in Germany 646 E. Burszta-Adamiak, W. Fiałkiewicz
increases by 13.5 million m2 every year mentation of the adopted incentives also (Mentens, Raes & Hermy, 2006). This leads directly to the realisation of green translates directly into the increase in roof. The requirements concerning the studies conducted there to evaluate construction of green roofs included in various aspects of the functionality and the local spatial development plans ena- usefulness of constructing green roofs. bled to construct 200,000 m2 of green One of the tangible effects of these ex- roofs in Copenhagen only in two years periences was the introduction of the (2010–2011). The most diversified range Forschungsanstalt Landschaftsentwick- of incentives exists in Germany (Table 3). lung Landschaftsbau (FLL) guidelines This results from the fact that each of the (FLL, 2002), which were first developed German lands conducts a separate green in 1997 and published in 2002 (the last policy in terms of the activities aimed at update was introduced in 2018). Since sustainable development of cities. Table then, most European countries have con- 3 demonstrates that the form of incen- sidered the FLL guidelines as the basis tives that is most often used in European for constructing green roofs. Another cities is co-financing the construction of example of a country, where initiatives green roofs and local legal regulations supporting the development of green that oblige investors to construct such roofs are successfully implemented, is roofs on newly constructed or modern- Denmark. There, the successful imple- TABLE 3. List of incentives used in specific countries Type of incentive maintenance of green construction of green Reduced stormwater Co-financing of the Co-financing of the Legal requirement Tax allowance Country Biofactor roof roof fees Austria + + Belgium + Czech Republic + Denmark + Great Britain + France + Germany + + + + + Netherlands + Poland + Sweden + + Switzerland + + A review of green roof incentives as motivators for the expansion... 647
ised buildings in cities, subject to certain ing incentives may be insufficient infor- conditions. mation about the required administra- The conducted analysis reveals that tive actions which are often excessively the type and number of the introduced in- complex and prolong the procedure of centives does not depend on the climate, obtaining a building permit. In the opin- in which green roofs may be developed. ion of the authors, setting the incentives Semaan & Pearce (2016) proved that it at a low return on investment level might does not depend on the country’s eco- be another factor that leads to poor inter- nomic health (gross domestic product – est in the proposed solutions. Such situ- GDP), either. In fact, many factors exist ation may be encountered when reduced that influence both the adoption of green stormwater or snowmelt fees are offered, innovations and the development of poli- or during the settlement of real property cies to promote that adoption, includ- tax. If savings on fees are in the amount ing other socio-economic factors. One of several or over 10 PLN annually, the of these factors is the attitude towards investment costs may be returned after green solutions, which results from the 20–30 years, which is not an attractive social awareness of the benefits of con- offer for investors. In some of the cities structing green roofs and the advisability there is a lack of strategy and vision by of their use. This makes it extremely im- leaders, executives and administrators. portant to implement the aforementioned This also translates into insufficient in- “background” incentives alongside other terest in the construction of green roofs. financial and non-financial incentives. Incentives based on excessively strict The analysed countries also include requirements for the structure of the those, where the incentives were intro- constructed green roof (e.g. minimum duced only one or two years ago, and surface area or substrate thickness) to be their measurable effects are not as spec- eligible for co-financing or tax allowance tacular as in Germany or Denmark. Un- may also make the offer less attractive fortunately, in many European cities, for investors. Some cities complained green roofs are still treated as a relatively about the public procurement procedures unimportant element of the urban envi- (the administratively easiest approach, ronment (Brudermann & Sangkakool, selecting the cheapest offer, creates a lot 2017). This sceptical attitude of inves- of undesirable side effects and in the lack tors to constructing green roofs is usu- of integration each managing organiza- ally linked to the lack of knowledge of tion behaves differently). The monitor- the technology of their construction and ing systems to measure success are also of the environmental, social and eco- usually weak. Therefore, maintaining nomic benefits from their realisation. green space is seen as another financial This phenomenon is enhanced by the oc- barrier. Many public and private clients casional news about poorly constructed see maintenance as an obstacle, ignoring green roof (leaks, dampness, problems the potential it holds. Hence, many cit- with maintaining the roof vegetation in ies called the attention to the difference good condition, etc.). Another limitation between the creation vs maintenance that affects the current state of introduc- of green spaces. Complaints usually 648 E. Burszta-Adamiak, W. Fiałkiewicz
concentrated on the lack of funding for educational programme for residents, in- regular maintenance. All these barriers vestors, and city policy makers should directly affect the degree of using the be closely integrated with a municipal proposed incentives by investors. campaign aimed at the popularisation of green roofs. Such campaign may be con- ducted through various channels, includ- Recommendations ing leaflets, press articles, posters, online promotion, etc. Another important aspect Identifying the barriers that emerge of a well-developed incentive should be during the practical implementation of its flexibility. At the stage of considering the adopted incentives allowed us to pin- the BAF factors in the design, developers point the weaknesses of the motivational may choose from several different op- system. In the opinion of the authors, tions of greenery or creating water-per- this may be the basis for determining the meable surfaces. Thus, they may select directions of establishing future incen- such systems that will be the most ben- tives for cities that will decide to intro- eficial for them, for future users of the duce them. The awareness of the exist- area and for the environment. Another ing types of barriers may also encourage important feature of a motivational tool those cities that have already introduced should be its simplicity. Both the struc- green policies to modify them in order ture of the proposed incentive (in terms to improve the current state of use of of calculations) and the implementation the incentives. The motivational system procedure (administrative issues) should should be modified on several levels. be simplified. An example of such incen- First of them is education. The satisfac- tive is determining the subsidy amount tory level of acceptance of the BAF fac- per each constructed square meter of the tor in Berlin proves that this aspect has green roof, along with tax allowance or been taken into account. At the stage of reduction in stormwater or snowmelt dis- creating the factor, groups of experts, rep- charge fees. The experiences of Europe- resentatives of the local community, the an cities show that the best results, trans- public administration, and environmen- lated into the number of realised green tal NGOs had the possibility to express roof investments, are achieved when the their opinions on the weighting assigned set amount of subsidies is reasonable, so to the given type of development (sin- that the investor can receive return on gle-family, multi-family, etc.). Another investment within several (max. 5–10) major success of these consultations was years. Incentives should be created in the fact that BAF was taken into account form of packages (several options at in urban spatial development (i.e. in lo- the same time), in connection with legal cal spatial development plans). Another regulations. The aim of such strategy is form of improving the awareness of the to include the provisions on green roofs functioning of green roofs in cities is the in legal regulations concerning con- realisation of demonstration projects, ac- struction, water management and spatial cessible to those who are interested in planning of green areas. Provisions in le- learning more about the technology. The gal regulations should be introduced on A review of green roof incentives as motivators for the expansion... 649
statutory or ordinance (national) level. growing interest in this type of solutions In the existing system, regulations on in- is expected. Due to that, it is necessary to centives are limited to provisions in local develop motivational instruments for the laws (city development strategies, local construction of green roofs. Such tools spatial development plans, etc.), which should include mainly financial incentives fosters the development of green roofs in and obligatory legal provisions. Addition- certain parts of the country (often limited ally, promotion, social dialogue, good to one city), while the issue is neglected tactics (policies, strategies), and studies in other parts. are required. Further challenges for to- Future financial incentives should day’s cities include providing technical not be limited only to co-financing the and administrative support in designing, stage of construction of the green roof. constructing and maintaining green roofs. As far as green infrastructure solutions Only such multi-faceted approach will are concerned, the stage of operation is lead to the increase in the number of cities extremely important, as it requires, when with well-developed green infrastructure necessary, conducting maintenance on the map of our continent. works (fertilising, weeding and irrigation during long dry periods). Among the an- alysed cities, only Vienna (Austria) has References foreseen subsidies on maintenance costs in the incentives. The maintenance costs Badach, J. & Raszeja, E. (2019). Developing a are co-financed in the amount of approx. framework for the implementation of land- 0.19 EUR·m–2 and the scope of works scape and greenspace Indicators in sustain- cover inspection twice a year, removal able urban planning. Waterfront landscape of growing trees and cutting grass. management: Case studies in Gdańsk, Poznań and Bristol. Sustainability, 11(8), 2291. https://doi.org/10.3390/su11082291 BEAM Society (2010). BEAM Plus for New Conclusions Buildings, Version 1.1. Hong Kong: BEAM Society. The degree of realisation of green Boas Berg, A., Radziemska, M., Adamcová, D. & Vaverková, M.D. (2017). Green roofs as an roofs in cities that have introduced incen- alternative solution to reduced green surface tives, compared with cities where such area in highly urbanized cities of the Europe- motivational tools have not been imple- an union – the study case of the Netherlands. mented yet, allows us to conclude that Acta Scientiarum Polonorum. Architectura, the implementation of such incentives 16(4), 59-70. for various groups of stakeholders is cur- Brudermann, T. & Sangkakool, T. (2017). Green roofs in temperate climate cities in Europe rently an indispensable element of local – an analysis of key decision factors. Urban policy. Nowadays, local governments Forestry and Urban Greening, 21, 224-234. possess tools that enable them to moti- Burszta-Adamiak, E., Stańczyk, J. & Łomotowski, vate residents and local entities to con- J. (2019). Hydrological performance of green struct green roofs in municipal areas. roofs in the context of the meteorological factors during the 5-year monitoring period. In spite of several barriers that hinder Water and Environment Journal, 33, 144- the development of green roofs in towns, -154. 650 E. Burszta-Adamiak, W. Fiałkiewicz
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Authors’ address: Ewa Burszta-Adamiak (https://orcid.org/0000-0003-3755-2047) Wiesław Fiałkiewicz (https://orcid.org/0000-0002-2517-5064) Uniwersytet Przyrodniczy we Wrocławiu Instytut Inżynierii Środowiska pl. Grunwaldzki 24, 50-363 Wrocław Poland e-mail: ewa.burszta-adamiak@upwr.edu.pl wieslaw.fialkiewicz@upwr.edu.pl 652 E. Burszta-Adamiak, W. Fiałkiewicz
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