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Article

Economic Benefits: Metrics and Methods for Landscape Performance Assessment

by
Zhen Wang
1,
Bo Yang
2,*,
Shujuan Li
2 and
Chris Binder
2
1
School of Architecture and Urban Planning, Huazhong University of Science and Technology, 1037# Luoyu Road, Hongshan District, Wuhan 430074, China
2
Department of Landscape Architecture and Environmental Planning, Utah State University, 4005 Old Main Hill, Logan, UT 84322-4005, USA
*
Author to whom correspondence should be addressed.
Sustainability 2016, 8(5), 424; https://doi.org/10.3390/su8050424
Submission received: 2 April 2016 / Revised: 24 April 2016 / Accepted: 25 April 2016 / Published: 29 April 2016
(This article belongs to the Section Economic and Business Aspects of Sustainability)
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Abstract

:
This paper introduces an expanding research frontier in the landscape architecture discipline, landscape performance research, which embraces the scientific dimension of landscape architecture through evidence-based designs that are anchored in quantitative performance assessment. Specifically, this paper summarizes metrics and methods for determining landscape-derived economic benefits that have been utilized in the Landscape Performance Series (LPS) initiated by the Landscape Architecture Foundation. This paper identifies 24 metrics and 32 associated methods for the assessment of economic benefits found in 82 published case studies. Common issues arising through research in quantifying economic benefits for the LPS are discussed and the various approaches taken by researchers are clarified. The paper also provides an analysis of three case studies from the LPS that are representative of common research methods used to quantify economic benefits. The paper suggests that high(er) levels of sustainability in the built environment require the integration of economic benefits into landscape performance assessment portfolios in order to forecast project success and reduce uncertainties. Therefore, evidence-based design approaches increase the scientific rigor of landscape architecture education and research, and elevate the status of the profession.

1. Introduction

Recognizing and quantifying the economic benefits of landscape performance demonstrates the fiscal argument for considered landscape designs. These benefits have their foundations in the use of cost/benefit analyses that allow researchers to assess the landscapes in question and compare them in time or space based on their economic impact for clients and surrounding areas. These benefits are demonstrated as monetary savings, profits, and other results (e.g., job creation) that are widely considered to be positive economic outcomes.
Economic benefits are defined through their intimate connections with nature, justice, and time [1]. This definition demonstrates how economic benefits exist in concert with environmental and social benefits (nature and justice), but that they also must be lasting and sustainable. As one of the three pillars of sustainable development (environmental, social, and economic), economic benefits have been examined by a number of studies within the landscape architecture discipline [2,3,4]. For instance, an urban forest provides multi-faceted environmental benefits (e.g., improved air quality, reduced urban heat island effect, better urban habitat) and these ecosystem services generate economic benefits. Other observable economic outcomes would also benefit local businesses, who may see more customers as a result of their business’ proximity to the urban oasis [5]; may attract qualified workers who appreciate clean air and recreation opportunities; and may find that their property value has increased.
Advancing research into landscape economic performance is essential for scholars and practitioners to close the gap between science and practice [6] and to advocate for the economic relevancy of the discipline [7,8,9]. In a broader context of advancing research in the landscape architecture discipline, various studies have suggested the importance of post-occupancy evaluation of built works [10,11]. For instance, van den Brink and Bruns [12] suggest three types of research in landscape architecture and advocate research-in-design as a means to invigorate the scientific dimension of education and practice. Some scholars further argue that it is important to assess project performance at every stage of its development [13], and monitoring and assessment should be integrated with project implementation [14].
In 2010, the Landscape Architecture Foundation (LAF) in the United States launched a seminal research program—the Landscape Performance Series (LPS)—whose goal is to showcase exemplary built projects with quantified landscape performance benefits [15]. Its purpose is to “fill a critical gap in the marketplace and make the concept of landscape performance and its contribution to sustainability as well-known as building performance is today”. Each LPS case study includes a study of environmental, social, and economic benefits, along with a method document explaining how these benefits are determined [16]. The reporting format and structure of LPS cases are built upon the case study method that Mark Francis developed for the LAF [17], while quantitative performance assessment is required in the LPS.
Although economic considerations are included as a crucial component of the LPS research, little progress has been made towards evaluating the rich LPS database in order to identify trends (or pitfalls) and best practices in economic benefits assessment. The study objectives are to perform a comprehensive analysis of the current status of LPS research, economic performance assessment in particular, and to summarize metrics and methods used for the assessment based on published LPS cases. Academic institutions and design firms may incorporate lessons learned from empirical analyses of built projects in order to optimize landscape designs for better performance outcomes.

2. Economic Benefits Categories and LPS Assessment Status

We outline the results of a comprehensive analysis of the LPS research approaches, as organized following the seven economic performance categories established by the LAF: (1) property value, (2) operations-and-maintenance savings, (3) construction cost savings, (4) job creation, (5) visitor spending, (6) increased tax base/revenue, and (7) economic development (Table 1). Figure 1 is an overview of the percentages of economic benefit categories in LPS. There are 24 detailed metrics under these seven categories. Figure 2 shows the benefit breakdowns per metric.
As shown in Figure 1, the top three assessed economic benefit categories are: operations-and-maintenance savings (34%), construction cost savings (19%), and economic development (18%). The sum of these three totals is 71% of the total cases evaluated. In addition, 68% of the cases that fall under the operations-and-maintenance savings category belong to the metric of irrigation-and-water. The disparity is apparent with respect to benefit categories and associated metrics being assessed, while suggesting room for improvement in other less-evaluated areas. It is apparent that the top-assessed categories and metrics (see Figure 1 and Figure 2) are directly related to the design process (e.g., site inventory, planning/design, and construction) and, as a result, designers and researchers find first-hand data readily accessible. On the other hand, in benefit categories that designers encounter less in their daily practice, or when designers/researchers need to rely on additional information or expertise to perform the assessment (e.g., tax revenue, visitor spending), the numbers of reported LPS cases decrease substantially. The section below provides a detailed account on possible metrics and methods for economic benefits assessment as synthesized from the LPS database.

3. Existing Metrics and Methods in LPS

Table 2 presents a comprehensive list of metrics and methods used in LPS economic benefit research. For most of the metrics, project performance may be obtained remotely using secondary data. Regarding the metric of construction cost savings, data may be available from contractors, clients, municipalities, or other sources. In other cases, such as for the metrics of visitor spending and increased tax base/revenue, it would be necessary to review receipts or financial records in order to assess visitor spending and tax revenue data. No specialized or expensive equipment is necessary to perform the methods recommended in Table 2. Below is a description of the seven LAF-defined economic benefit categories.

3.1. Property Values

Property values are a benefit concerned with measuring the increase in real estate value derived from a landscape design. Property value increases are perhaps the most tangible indicators of landscape economic performance, and are highly relevant to real estate developers and others who often fund the development of green spaces [19]. At times, the landscape project may be the only change which occurred in an area, showing a direct impact on property values. At other times, the project may have occurred in conjunction with a rezoning, additional development, or other relevant factors. In the latter cases, the landscape intervention can be framed as a contributor to increased property values rather than the sole driver.

3.2. Operations and Maintenance Savings

By creating a resilient and self-sustaining landscape that requires fewer inputs of time, money, and resources than are traditionally required, landscape design can result in significant long-term savings over the entire life of a project. The savings that accrue fall into the category of operations-and-maintenance savings.

3.3. Construction Cost Savings

LPS categorizes one-time savings that result from reducing the expenses associated with implementing a landscape design as construction cost savings. The construction phase of landscape design can be planned in such a manner that it results in significant cost savings for the client [20]. In turn, many of these cost saving measures also provide environmental benefits. For example, reusing concrete from a demolished building on a site not only obviates the need to purchase new concrete, it also reduces the project’s environmental impact by diminishing the materials and energy needed to produce new concrete and aggregate. Demonstrating construction cost savings can be a valuable tool in persuading clients of the value of sustainable landscape practices, such as demonstrated through the Sustainable Sites Initiative (SITES) [21,22]. Calculating the value of materials and the costs of hauling and dumping are based on local prices for landfill access, gasoline, and other factors.

3.4. Job Creation

Landscape development projects can often result in the creation of full-time permanent employment for land managers, support staff, maintenance crews, and others. In addition, projects may contribute to the local economy by indirectly creating jobs in nearby areas that serve visitors, residents, or others who are drawn to the area by the landscape development [23]. Finally, all projects not undertaken entirely by volunteers will also create temporary jobs during the construction and implementation of the design. These facets of economic growth fall under the category of job creation, including direct and indirect permanent jobs. Job creation is a key indicator of economic health and can be a powerful tool for researchers quantifying landscape performance.

3.5. Visitor Spending

Visitor spending refers to the amount of money spent by visitors to a designed landscape. This spending is derived from landscape design projects that have the ability to draw local, regional, national, and international visitors. Depending on the type of landscape, there may be entrance fees, membership fees, or other types of visitor spending that can be quantified and analyzed. Particularly large and well-known sites that may draw hundreds of thousands or even millions of visitors per year can have a significant impact on the visitor spending within a city or a region. These projects can be treated as having enough impact on larger trends to derive information about their contribution from city- or region-wide data on visitor spending and other activity.

3.6. Increased Tax Base/Revenue

Measuring the tax revenue generated for towns, municipalities, or other governments through landscape improvements falls into the category of increased-tax-base/revenue. An increase in tax base can be seen as the public-sector equivalent benefit that derives from increased property values. This information can be enormously valuable to municipal partners investing in parks, open spaces, business improvement districts, and other landscape projects. Investment in landscape projects can lead to a broader tax base, which may lead to increased revenue district-wide as an area becomes a more popular and active destination.

3.7. Economic Development

Finally, landscape design can have a profound influence on overall economic development of a site, neighborhood, or region [24]. Economic development is a catch-all category that concerns benefits that assess the impacts on spending and occupancy derived from landscape projects. Economic development can be indicated by measurements of spending, growth, and increased revenue in areas directly affected by landscape development projects. Typologies such as streetscapes, transit-oriented developments, and waterfront redevelopments are particularly suited to this category of benefit quantification.

4. Case Studies

LAF’s case study method involves the collection and analysis of different kinds of information, including (1) baseline data, (2) role of key project participants, (3) financial aspects, (4) project goals, (5) design and decision-making processes, (6) use and perceptions, (7) unique constraints, and (8) project successes and limitations [17,25]. The intent is to provide in-depth analyses of cases that would warrant replicable solutions to complex problems
In this study, three case studies are chosen, each representing a good example for one of the top three economic benefit categories assessed. These three categories are: operations-and-maintenance savings, construction cost savings, and economic development (see Figure 1). The specific benefit shown for each case study is chosen because its method is highly replicable in similar projects. Table 3 summarizes the basic information of the three cases and the corresponding economic benefits.

4.1. Gary Comer Youth Center—An Example of Operations-and-Maintenance Savings

The Gary Comer Youth Center (GCYC) is located on Chicago’s south side. It offers extracurricular activities and hands-on learning opportunities in a safe environment. Its economic benefit assessment offers an example of operations-and-maintenance-savings because of an intensive green roof design (Figure 3) [26].
Energy savings from this green roof are calculated based on the Green Roof Calculator developed by the Portland State University Green Building Research Laboratory. The Green Roof Energy Module estimates the combined energy savings (cost/therms and cost/kWh) compared to a conventional roof. This module is based on the type and location of the building, roof surface area, growing media depth, leaf area index, and percentage of plant coverage [27].
Electricity rates for the state of Illinois are based on the U.S. Department of Energy’s Average Retail Price [27]. The average cost of natural gas is 121.8 cents/therm and 9 cents/kWh [28]. The total amount of energy saved is based on GCYC roof specifications and averaged energy costs. The energy savings are then used to calculate the corresponding monetary savings. The estimated savings of 642.58 kWh and 156.53 therms, would generate an annual savings of $248.80 [26].

4.2. Blue Hole Regional Park—an Example of Construction-Cost Savings

The Blue Hole Regional Park is located in the heart of the rugged Texas Hill Country in Texas (Figure 4). In 2005, the city of Wimberley purchased the “Blue Hole” swimming area and surrounding 126 acres (50.99 ha) in order to protect the pristine waters [29]. According to the construction documents, nearly 5 acres (2.02 ha) of the park receives mulch. This area is multiplied by a 5-inch (13 mm) average depth (number confirmed by the landscape contractor). The total volume is multiplied by the average cost of local mulch (c.a., $70/cubic yard ($92/cubic meter)) [29].
Construction savings are calculated as follows: 4.957 acre (23,992 square yard) (2 ha) of mulch used on site; 23,992 square yard @ average 5-inch depth = 3332 cubic yard (2547 cubic meter); 3332 cubic yard @ $69/cubic yard = $229,908 saved [29].
Enough cedar mulch is created to cover all designed mulch areas plus an additional 1–2 inch (2.54−5.08 mm), and to create a stockpile on site for future freshening of the mulch areas [29]. Limitations of this method include fluctuating mulch prices and an assumption that the mulch is spread at a uniform thickness throughout all mulched areas of the park.

4.3. Uptown Normal Circle and Streetscape—an Example of Economic Development

This streetscape retrofit project incorporates stormwater management and public recreation into a vibrant gathering space that also encourages economic development (Figure 5). Researchers’ communication with the Bloomington-Normal Marriott hotel indicated that there have been four professional conferences held in Normal because of the completion of the traffic circle (AIA Illinois Chapter, Illinois Association for Floodplain and Stormwater Management, Illinois Association of Wastewater Agencies, Illinois City/County Management Association, and Illinois Chapter American Planning Association) [30].
Researchers then contacted the organizations holding the conferences to obtain data on attendance, hotel room rates, registration fees, and other economic impacts. As a result, the approximate amount of revenue generated is determined: number of participants × registration fees + cost of hotel rooms (assuming $119 per night per person, the conference rate) + a $46 per diem per day (based on the federal per diem rate for Illinois). For these four conferences, the estimated revenue generated totals $681,398 [30]. Limitations of this method include an inability to determine further impacts that conference attendees may have had while dining in restaurants, using local transportation, and other spending.

5. Discussion

Compared with other allied disciplines, scholarly productivity in United States within the field of landscape architecture remains low, although with steady improvements in the past decades [31,32,33,34]. In this sense, landscape performance assessment would be an actionable agenda item that contributes to landscape research and practice. Supported by empirical examinations, such as cases from the LPS database, landscape architecture, as a discipline, would gain a better status in society.

5.1. Considerations for Improvement

The need of demonstrating economic benefits of landscape performance is clear, while some considerations are key to the success of performance assessment. Temporal scale is one of them. Landscapes are dynamic systems; hence, the reported benefits are arguably temporary, given that no tree or other landscape modification will last forever without maintenance. A tree, itself, needs time to reach maturity in order to provide the expected benefits. Therefore, truly sustainable economic benefits must be more than simply the construction of a beneficial landscape—they must also include a long-term plan for the upkeep and continued viability of that landscape that is self-sustaining and able to carry the current benefits into the future.
Another important consideration is to contextualize economic analysis and report the direct impacts from the project under investigation, rather than encompassing the spillover effects. For the metric of job creation, for instance, it is cautionary to attribute job creation in nearby developments as being caused by the landscape project. There must be a direct and identifiable link between the landscape project and the jobs created in order to create a defensible benefit. Similarly, for the metric of economic development, the size of the project and its impact on the area must be accounted for and noted in reporting benefits. It may be advantageous to state that the landscape project contributed to certain increases rather than to say they it caused them as there are likely many variables at play.
Finally, the robustness of the method and validity of data sources in LPS, in general, need improvement. Using the metric of property values as an example, one should be careful not to substitute one metric with another, as oftentimes data are reported in different forms, such as a total value, a percentage change in value for the entire assessed area, or a percentage change per property in relation to the city median. It is also recommended that researchers collect first-hand data whenever possible and develop hypotheses that directly examine the research questions, and reduce the instances where proxy data or information are relied upon.

5.2. Implications to Landscape Architecture Education and Design Process

Although economic benefits are often considered as project priorities in professional practice [35,36,37], the assessment of these benefits in education needs to be better emphasized, as it is not a strength area in the current curricula. Most curricula put emphasis on environmental benefits. When economic benefits are addressed, few courses illustrate a procedure that can effectively measure or assess them.
Compared with environmental benefits which may be predicted in the design phase, many economic benefits aforementioned (e.g., visitor spending, increased tax base/revenue) are not easy to predict at this phase. Landscape architects are either not acquainted with ways to access these benefits, or they do not normally perform a follow-up analysis after the project is built. On other occasions where economic benefits could be assessed during project design and construction, designers are recommended to document evidence. For example, the reuse of materials will generate construction cost savings, a metric that can be assessed rather accurately through construction documentation (e.g., delineate areas where reused materials are applied).
In short, integrating economic benefits assessment in the design process, and in-studio teaching in particular, would help instill a culture of performance assessment for the next generation of practitioners, in the enterprise of achieving (better) sustainable design solutions anchored in empirical evidence. It takes time for a project’s economic benefits and fiscal impacts to become observable and measurable. Long-term and short-term economic benefits need to be gauged for benefit optimization. So doing will enhance designers’, decision-makers’, and the general public’s confidence in the level of services that landscape designs can provide.

6. Conclusions

This paper introduces a research and practice frontier in landscape architecture, landscape performance research, and reviews the current status of economic benefits assessment in the LPS. The grand sustainable challenges that we face today cannot be solved by a single design profession. Resilient landscape design calls for (quantitatively) demonstrated project performance in order to reduce uncertainties, and whole-systems designs, from site to regional scales, are essential. Central to this endeavor is the integration of landscape architecture with allied professions, and through evidence-based designs that are informed by science.

Acknowledgments

We thank Katharine Burgess, Heather Whitlow, Barbara Deutsch, Allyson Mendenhall, and Kurt Culbertson for their indispensable help with this research. We also thank Di Wang for preparation of an early version of the database. This research was supported by the Landscape Architecture Foundation (LAF) Landscape Performance Analysis Grant, the California Landscape Architectural Student Scholarship Fund (CLASS Fund), the Utah Agricultural Experiment Station, Utah State University (approved as journal paper number 8731), the NSF EPSCoR grant EPS 1208732 awarded to Utah State University, as part of the State of Utah Research Infrastructure Improvement Award, the National Natural Science Foundation Project of China (grant number: 51008135), and the Fundamental Research Funds for the Central Universities, HUST (grant number: 2015QN060). Any opinions, findings, and conclusions or recommendations expressed are those of the authors and do not necessarily reflect the views of the LAF, the CLASS Fund, the Utah Agricultural Experiment Station, the National Science Foundation, the National Natural Science Foundation of China, or the Fundamental Research Funds for the Central Universities, HUST.

Author Contributions

The authors have contributed equally in the research design and development, the data analysis and the writing of the paper. The authors have read and approved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

The following abbreviations are used in this manuscript:
LPS
the Landscape Performance Series
LAF
the Landscape Architecture Foundation
GCYC
The Gary Comer Youth Center

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Figure 1. Percentage of economic benefits by category in the Landscape Architecture Foundation’s Landscape Performance Series.
Figure 1. Percentage of economic benefits by category in the Landscape Architecture Foundation’s Landscape Performance Series.
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Figure 2. Economic benefits assessed by metric categories in the Landscape Architecture Foundation’s Landscape Performance Series.
Figure 2. Economic benefits assessed by metric categories in the Landscape Architecture Foundation’s Landscape Performance Series.
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Figure 3. Gary Comer Youth Center Roof, Chicago, Illinois (photo courtesy: Scott Shigley. Hoerr Schaudt, Chicago, USA).
Figure 3. Gary Comer Youth Center Roof, Chicago, Illinois (photo courtesy: Scott Shigley. Hoerr Schaudt, Chicago, USA).
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Figure 4. Blue Hole Regional Park, Wimberley, Texas (photo © D.A. Horchner. Design Workshop, Inc., Denver, USA).
Figure 4. Blue Hole Regional Park, Wimberley, Texas (photo © D.A. Horchner. Design Workshop, Inc., Denver, USA).
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Figure 5. Uptown Normal Circle and Streetscape, Normal, Illinois (photo courtesy: Hoerr Schaudt. Hoerr Schaudt, Chicago, USA).
Figure 5. Uptown Normal Circle and Streetscape, Normal, Illinois (photo courtesy: Hoerr Schaudt. Hoerr Schaudt, Chicago, USA).
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Table
Table 1. Categories and metrics for economic benefits assessment in the Landscape Architecture Foundation’s Landscape Performance Series.
Table 1. Categories and metrics for economic benefits assessment in the Landscape Architecture Foundation’s Landscape Performance Series.
MetricEconomic Categories
Property ValueOperations and MaintenanceConstructionJob CreationVisitor SpendingTax RevenueEconomic Development
Benefit MetricsIncrease in Property ValueIncrease in Sales PriceIncrease in rentsHeating and CoolingIrrigation and WaterGeneral MaintenanceVolunteer HoursHauling/DumpingMaterialsInstallationEarthworksPermanentTemporaryEntry FeesSalesRentalsGeneral SpendingProperty Tax RevueProjected Tax RevenueInvestment/Projects CatalyzedRetail SalesSpace or UnitsOccupancy Rate
Total by Category14 (12%)40 (34%)23 (19%)20 (17%)13 (11%)7 (6%)22 (18%)
Table
Table 2. Metrics and methods used in landscape performance assessment in the Landscape Architecture Foundation’s Landscape Performance Series.
Table 2. Metrics and methods used in landscape performance assessment in the Landscape Architecture Foundation’s Landscape Performance Series.
CategoryMetricMethod
(1) Property ValueIncrease in property value for adjacent or nearby properties
  • Compare all real estate values within an established vicinity of the site before and after project completion
  • Compare the property value of a single building before and after the landscape intervention
  • Compare real estate values to other comparable properties elsewhere in the vicinity that do not enjoy benefits from the landscape intervention
Increases in sales price for adjacent or nearby properties
  • Consult municipal or online real estate databases of sales prices
Increases in rents for adjacent residential or commercial properties
  • Compare rent charges in adjacent or nearby residential or commercial properties before and after the landscape intervention
(2) Operations and Maintenance SavingsReduction in heating and cooling costs
  • Compare heating and cooling bills from before and after the implementation of a landscape design
  • Compare heating and cooling bills from the property with similar properties that have not had a landscape intervention
  • Use local energy costs to convert energy savings into cost savings a
Reduction in irrigation or potable water costs
  • Calculate the value of water re-used on site
  • Compare use of water on the site to use on a similar site without a sustainable design
  • Compare water bills from before and after design implementation
Reduction in maintenance costs, mowing, fertilizer and others
  • Compare the relevant needs for the landscape before and after the design implementation
Value of volunteer hours
  • Multiply typical value of an hour of labor by the total number of volunteer hours to obtain a value of volunteer contributions
(3) Construction Cost SavingsReduced hauling and/or dumping costs
  • Record the amount of material reused on site that did not then need to be hauled away
  • Calculate the savings associated with avoiding dumping fees by reusing materials
Reduced material purchasing costs
  • Record the amount of materials reused and calculating the cost of purchasing those materials new and transporting them to the site
Reduced installation costs
  • Calculate the savings associated with installing green infrastructure instead of traditional infrastructure
Reduced earthworks costs
  • Consult construction documents to assess the cut/fill operations and determine the savings associated with eliminating purchasing and hauling of fill to the site or disposal of cut from the site
(4) Job CreationNumber of permanent jobs created directly for the operation of the site
  • Consult public data, client records, or other sources to determine the number of park staff, event staff, or other employees that rely directly on the landscape project for their jobs, or can be attributed to the nearby or adjacent landscape project
Number of permanent jobs created for surrounding, related development
Number of temporary jobs created for the construction of the site, seasonal operations, or other temporary needs
  • Contact construction contractors or consult their records to discover the number of man-hours dedicated to a project
  • Estimate the jobs created based on the overall cost of the landscape project
(5) Visitor SpendingRevenue generated by entry fees
  • Review visitor counts or other collected data sources
  • Interview with staff and other personnel who keep records of visitation
Revenue generated through direct sales
  • Review sales records from cafes, gift shops, and other retail establishments affiliated with the project in question
General visitor spending in nearby or adjacent areas
  • Review and analyze data reflecting total visitor spending in the city or region
(6) Increased Tax Base/RevenueIncrease in office, commercial, or residential space or units
  • Map or consult commercial or municipal records to quantify the extent that development has increased the potential tax base
Actual increase in tax revenue
  • Consult government records to ascertain the before and after development amounts of tax revenue collected
Projected increase in tax revenue
  • Project tax revenue by calculating the square footage of different types of space and extrapolating taxes based on those types
(7) Economic DevelopmentIncrease in retail sales
  • Researching retail sales information from public records or through contacting private businesses to determine increases after landscape project completion
Increase in commercial establishments
  • Perform a count of new commercial business directly adjacent to the site or in the larger neighborhood to assess the number of retail establishments whose existence can be linked to the landscape improvements
Decrease in retail vacancies and/or increase in occupancy
  • Consult records to determine if vacancy rates decreased or occupancy rates increased for both commercial and residential spaces following the completion of the landscape project
Revenue generated through project-related events
  • Contact employees of the site or nearby businesses (such as hotels) that cater to those who attend events
a Utilizing a calculating tool such as the Green Roof Energy Calculator from Portland State University or the Center for Neighborhood Technology’s Value of Green Infrastructure Guide [18]
Table
Table 3. Select cases for the top three reported economic benefits categories in the Landscape Architecture Foundation’s Landscape Performance Series.
Table 3. Select cases for the top three reported economic benefits categories in the Landscape Architecture Foundation’s Landscape Performance Series.
ProjectLocationSize (ha)CategoryBenefit
Gary Comer Youth CenterChicago, Illinois0.08Operations and maintenance savingsSaves $250 in annual heating and cooling costs as compared to a conventional roof by moderating heat gain and loss.
Blue Hole Regional ParkWimberley, Texas50.99Construction savingsSaved approximately $230,000 in mulch costs by double-shredding the trunks of invasive cedars removed from the site and using this to cover all designed mulch areas.
Uptown Normal Circle and StreetscapeNormal, Illinois1.97Economic developmentGenerated more than $680,000 of revenue through conferences held in Normal that featured the Uptown Redevelopment.

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MDPI and ACS Style

Wang, Z.; Yang, B.; Li, S.; Binder, C. Economic Benefits: Metrics and Methods for Landscape Performance Assessment. Sustainability 2016, 8, 424. https://doi.org/10.3390/su8050424

AMA Style

Wang Z, Yang B, Li S, Binder C. Economic Benefits: Metrics and Methods for Landscape Performance Assessment. Sustainability. 2016; 8(5):424. https://doi.org/10.3390/su8050424

Chicago/Turabian Style

Wang, Zhen, Bo Yang, Shujuan Li, and Chris Binder. 2016. "Economic Benefits: Metrics and Methods for Landscape Performance Assessment" Sustainability 8, no. 5: 424. https://doi.org/10.3390/su8050424

APA Style

Wang, Z., Yang, B., Li, S., & Binder, C. (2016). Economic Benefits: Metrics and Methods for Landscape Performance Assessment. Sustainability, 8(5), 424. https://doi.org/10.3390/su8050424

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