Richard Sharp’s research while affiliated with World Wildlife Fund and other places

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Publications (40)


Global hotspots of impacts differ across ecosystem service and biodiversity metrics
The eight maps on the right indicate the 10% of land area with the highest values for each of four ecosystem service metrics (top) and four biodiversity metrics (bottom). For coastal risk reduction and Key Biodiversity Areas, this includes all areas with values greater than zero. These individual metric maps were combined to create each of the two ecosystem service and biodiversity hotspot maps on the left, showing which land areas fall within the top 10% for one or more ecosystem service or biodiversity metrics.
Company-level ecosystem service and biodiversity impacts vary across and within sectors
Impacts are shown for three ecosystem service metrics (coastal risk reduction, nitrogen retention, sediment retention) and four biodiversity metrics (habitat for endemic species, habitat for threatened and endangered species, total species richness, and Key Biodiversity Areas). The top row shows the total impact per company, which is affected by the number, size, and location of each companies’ physical assets. The middle row shows impact adjusted by company revenue. The bottom row shows total impact adjusted by the total area (km²) of physical assets. A higher impact per km² indicates a company’s assets are located in areas with great ecosystem service or biodiversity values. The values for each metric should be interpreted as indices; values are comparable within a metric but not between different metrics. For each boxplot, the midline indicates the median, with boxes extending from the 25th to 75th percentiles and whiskers extending to 1.5 times the interquartile range. Outliers beyond 1.5 times the interquartile range are indicated as dots. Note the log scale of y-axes. See Table 1 for information on the number of companies and assets included per sector and the size of their footprint.
Within the materials sector, company impacts vary across and within industries
Impacts are shown for three ecosystem service metrics (coastal risk reduction, nitrogen retention, sediment retention) and four biodiversity metrics (habitat for endemic species, habitat for threatened and endangered species, total species richness, and Key Biodiversity Areas). The values for each metric should be interpreted as indices; values are comparable within a metric but not between different metrics. For each boxplot, the midline indicates the median, with boxes extending from the 25th to 75th percentiles and whiskers extending to 1.5 times the interquartile range. Outliers beyond 1.5 times the interquartile range are indicated as dots. Note the log scale of y-axes. The top row shows the total impact, which is affected by the number, size, and location of each companies’ physical assets. The middle row shows impact adjusted by company revenue. The bottom row shows total impact adjusted by the total area (km²) of physical assets. A higher impact per km² indicates a company’s assets are located in areas with great ecosystem service or biodiversity values. See Table 2 for information on the number of companies and assets included per industry and the size of their footprint.
Both mine size and location are important drivers of variation in estimated impacts
The estimated impact of 23 lithium mines based on high-spatial-resolution, mine-specific footprints is shown on the y-axis, compared to the estimated impact using median mine area on the x-axis. Footprints were generated from 2023 first quarter imagery and associated with 2022 production. a compares estimates of total impact, while panel b compares ranks. A rank of 1 corresponds to the greatest impact for a given metric. The 1:1 line is shown in solid black. Using the median mine area substantially underestimates the impacts of the highest impact mines as compared to using a mine specific-footprint. Comparing ranked impacts (b), the median area-based approach differentiates higher and lower impact mines for nitrogen retention, sediment retention, and nature access, but not for endemic species, Red List species, or species richness. No mines were located in coastal areas or near Key Biodiversity Areas, so coastal risk reduction and KBA metrics were omitted.
Patterns of change in mine impact vary over time and among ecosystem service and biodiversity metrics
a shows the footprint of the Greenbushes, Australia lithium mine mapped from satellite imagery across three time periods (2016, 2019, and 2023). b shows the change in mine impact over time relative to 2016 in terms of total impact, impact per tonne lithium produced, and impact per km² of mine footprint. Footprints were generated from first quarter imagery in each year and associated with the previous year’s production. Values for impacts to coastal risk reduction and Key Biodiversity Areas (KBAs) are zero across all years, and so these metrics are not shown.

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An open-source approach for measuring corporate impacts on ecosystem services and biodiversity
  • Article
  • Full-text available

October 2024

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150 Reads

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1 Citation

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Andrew Shea

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Emily Soth

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[...]

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Mayur Patel

Existing approaches to evaluating companies on sustainability-related issues include limited accounting of impacts on nature and its contributions to human well-being. Here we present an approach for quantifying the direct impacts of companies’ physical assets on nature based on global maps for eight ecosystem service and biodiversity metrics. We apply this approach to a set of over 2000 global, publicly traded companies with 580,000 mapped physical assets and find that companies in utility, real estate, materials, and financial sectors have the largest impacts on average, with substantial variation within all sectors. Using high-spatial-resolution satellite imagery to map individual mine footprints, we compare a set of active lithium mines and find that impacts vary substantially among mines and change over time. By using open-source models and drawing on the growing availability of high-spatial-resolution satellite imagery, this approach could provide more transparent measures of corporate impacts to nature for nature-related reporting.

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Differences between modeled and reference air temperatures (°C) for the Paris region for daytime and nighttime simulations pre- and post-calibration.
Differences between modeled and reference air temperatures (°C) for the Twin Cities region for daytime and nighttime simulations pre- and post-calibration.
Cooling service (°C) during daytime resulting from the greening scenario as simulated by InVEST and by the TEB/SURFEX model (reference data).
Calibrated
Calibrating and validating the Integrated Valuation of Ecosystem Services and Tradeoffs (InVEST) urban cooling model: case studies in France and the United States

June 2024

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72 Reads

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5 Citations

Understanding the cooling service provided by vegetation in cities is important to inform urban policy and planning. However, the performance of decision-support tools estimating heat mitigation for urban greening strategies has not been evaluated systematically. Here, we further develop a calibration algorithm and evaluate the performance of the urban cooling model developed within the open-source InVEST (Integrated Valuation of Ecosystem Services and Tradeoffs) software. The urban cooling model estimates air temperature reduction due to vegetation based on four predictors, shade, evapotranspiration, albedo, and building density, and was designed for data-rich and data-scarce situations. We apply the calibration algorithm and evaluate the model in two case studies (Paris, France, and Minneapolis–St Paul, USA) by examining the spatial correlation between InVEST predictions and reference temperature data at a 1 km horizontal resolution. In both case studies, model performance was high for nighttime air temperatures, which are an important indicator of human wellbeing. After calibration, we found medium performance for surface temperatures during daytime but low performance for daytime air temperatures in both case studies, which may be due to model and data limitations. We illustrate the model adequacy for urban planning by testing its ability to simulate a green infrastructure scenario in the Paris case study. The predicted air temperature change compared well to that of an alternative physics-based model (r2=0.55 and r2=0.85 for daytime and nighttime air temperatures, respectively). Finally, we discuss opportunities and challenges for the use of such parsimonious decision-support tools, highlighting their importance to mainstream ecosystem services information for urban planning.


Global trends and scenarios for terrestrial biodiversity and ecosystem services from 1900 to 2050

April 2024

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1,389 Reads

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70 Citations

Science

Based on an extensive model intercomparison, we assessed trends in biodiversity and ecosystem services from historical reconstructions and future scenarios of land-use and climate change. During the 20th century, biodiversity declined globally by 2 to 11%, as estimated by a range of indicators. Provisioning ecosystem services increased several fold, and regulating services decreased moderately. Going forward, policies toward sustainability have the potential to slow biodiversity loss resulting from land-use change and the demand for provisioning services while reducing or reversing declines in regulating services. However, negative impacts on biodiversity due to climate change appear poised to increase, particularly in the higher-emissions scenarios. Our assessment identifies remaining modeling uncertainties but also robustly shows that renewed policy efforts are needed to meet the goals of the Convention on Biological Diversity.




Percentage of global land area required to provide different levels of NCP
Prioritized areas for nature’s contributions to people (NCP) (blue squares) with species targets included (red circles) and with protected areas (PAs) and other effective area-based mechanisms (OECM) sites locked in (orange diamonds). Vertical dashed lines correspond to 30 and 50% of global land area. The horizontal dashed line corresponds to 90% of NCP.
Prioritized areas for nature’s contributions to people (NCP) and biodiversity
a Combined prioritization results for all species representation targets and NCP targets ranging from 5% (dark blue) to 90% (light yellow). b Combined prioritization results for NCP and species with the World Database of Protected Areas (WDPA) and other effective area-based conservation mechanisms (OECM) sites locked in to prioritization results. In all cases, dark blue areas represent areas required to achieve targets in the least amount of area. Collectively, dark blue to light yellow areas provide 90% of all ten NCP and meet species representation targets in the least amount of area. Prioritized areas achieve all species representation targets (see main text); only the level of NCP achieved varies.
Prioritized areas for nature’s contributions to people (NCP) only (90% of current levels of NCP, in blue), prioritized areas for both NCP (90% of current levels) and that also meet all species targets (red), and areas of overlap (purple)
Prioritized areas overlap over 33% of global land area (representing 94% of areas prioritized for NCP alone, or 75% of areas prioritized for NCP and species).
Prioritized areas for nature’s contributions to people and biodiversity (NCP) that also have high development potential across several economic sectors
a Prioritized areas (blue) represent areas providing 90% of current levels of NCP while also achieving all species targets. Areas with high and very high development potential (orange) and areas of overlap (green). b Prioritized areas with high development potential (areas of overlap), by economic sector. Sectors include agriculture (crops and biofuels expansion) (green); mining (metallic, non-metallic, and coal) (pink); oil and gas (conventional and unconventional) (yellow); renewable energy (concentrated solar power, photovoltaic solar, wind, and hydropower) (red); urban expansion (light blue), and “multiple sectors” where sectors overlap (dark blue).
Mapping the planet’s critical areas for biodiversity and nature’s contributions to people

January 2024

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850 Reads

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38 Citations

Meeting global commitments to conservation, climate, and sustainable development requires consideration of synergies and tradeoffs among targets. We evaluate the spatial congruence of ecosystems providing globally high levels of nature’s contributions to people, biodiversity, and areas with high development potential across several sectors. We find that conserving approximately half of global land area through protection or sustainable management could provide 90% of the current levels of ten of nature’s contributions to people and meet minimum representation targets for 26,709 terrestrial vertebrate species. This finding supports recent commitments by national governments under the Global Biodiversity Framework to conserve at least 30% of global lands and waters, and proposals to conserve half of the Earth. More than one-third of areas required for conserving nature’s contributions to people and species are also highly suitable for agriculture, renewable energy, oil and gas, mining, or urban expansion. This indicates potential conflicts among conservation, climate and development goals.


(a) Global total number of people impacted annually historically (1992), under the current climate (2020), and with climate change (SSP585 in 2050). The colors indicate the degree of protection by coastal ecosystems, while the gray color indicates non-protection. (b) The global proportion of people protected historically (1992), under the current climate (2020), and with climate change (SSP585 in 2050), and the different factors influencing these changes including loss of coastal ecosystems, population changes, compounding effects of the latter two, and climate change. Note that ‘compounded’ refers to the change in protection that occurs if coastal ecosystems and population exposure are varied simultaneously, i.e. in addition to the changes in protection based on the two factors individually.
(a) Population in the low-elevation coastal zone impacted by tropical cyclones (TC) globally under current conditions. Each point represents an exposure point impacted by TC, while the color shows the number of people impacted per exposure point annually. Note the logarithmic scale. (b) Population in the low elevation coastal zone protected from TC by coastal ecosystems globally under current conditions. The color refers to the degree of protection by nearby coastal ecosystems. Note that only exposure points with a non-zero average annual impact are plotted, i.e. the coastal ecosystem protective rank is only mapped for points impacted by tropical cyclones.
(a) Proportion of people protected (%) from tropical cyclones by coastal ecosystems across different regions. The colors indicated the degree of protection (very high to low). In both panels, the top bar shows the historical numbers (1992), while the bottom bar shows the current baseline numbers (2020). (b) Absolute number of people impacted annually per region. The colors show the Saffir-Simpson wind speed category. Note the log-scale on the x-axis.
Global increases in the proportion of people protected for the mangrove restoration and reforestation scenarios. The top bar represents the increase in total protection, i.e. changes from non-protection in the baseline to protection under the restoration scenario. The lower bar represents the increase in the degree of protection for areas which already receive some level of protection in the baseline. The x-axis indicates the increases in absolute numbers of people protected annually, the percentages within the bar chart indicate the increase in the share of people protected. The increase in the degree of protection is higher than the total increase in protection, which indicates that the mangrove restoration scenario mainly causes an increase in the ranking of areas already receiving some degrees of protection.
Global protection from tropical cyclones by coastal ecosystems—past, present, and under climate change

November 2023

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244 Reads

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10 Citations

Coastal ecosystems have the potential to contribute to disaster risk reduction and adaptation to climate change. While previous studies have estimated the value of current coastal ecosystems for reducing coastal risk, there have been relatively few studies that look at changes in ecosystem service provision, in the past and under climate change. We employ the probabilistic, event-based CLImate ADAptation platform (CLIMADA) to quantify the protection from tropical cyclones (TCs) provided by coastal ecosystems, modeling the number of beneficiaries in the past and under future climate change. We also investigate the potential of nature-based solutions (NbS), such as mangrove restoration. We find that currently, one in five (21%) of all people impacted annually by TCs in the global low-elevation coastal zone is within the protection distance of coastal ecosystems. Over the last 30 years, the share of protected people has decreased by approximately 2%, due to ecosystem loss. With climate change, the average annual number of people impacted will increase by 40%. Simultaneously, the proportion of people protected by coastal ecosystems with climate change decreases due to changes in TC distribution (−1%). The importance of current coastal protection, and the potential for increasing protection by NbS, varies widely between countries. While the number of people protected globally only increases slightly with mangrove restoration, the share of people protected in individual countries can increase by up to 39%. Our findings provide a basis for NbS planning and adaptation policy, by highlighting areas which will be crucial for coastal protection services in a world altered by climate change.


Calibrating and validating the InVEST urban cooling model: Case studies in France and the United States

September 2023

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249 Reads

Understanding the cooling service provided by vegetation in cities is important to inform urban policy and planning. However, the performance of decision-support tools estimating heat mitigation for urban greening strategies is not systematically evaluated. Here, we develop a calibration algorithm and evaluate the performance of the Urban Cooling model developed within the open-source InVEST (Integrated Valuation of Ecosystem Services and Tradeoffs) software. The Urban Cooling model estimates air temperature reduction due to vegetation based on four predictors: shade provision, evapotranspiration, albedo, and building density and was designed for data-rich and data-scarce situations. We apply the calibration algorithm and evaluate the model in two case studies (Paris, France, and Minneapolis-St Paul, USA) by examining the spatial correlation between InVEST predictions and reference temperature data at 1-km horizontal resolution. In both case studies, model performance was high for nighttime air temperatures, which is an important indicator of human wellbeing. After calibration, we found a medium performance for surface temperatures during daytime but a low performance for daytime air temperatures in both case studies, which may be due to model and data limitations. We illustrate the model adequacy for urban planning by testing its ability to simulate a green infrastructure scenario in the Paris case study. The predicted air temperature change compared well with that of an alternative physics-based model (r2=0.55 and r2=0.85, for air daytime and nighttime temperatures, respectively). Finally, we discuss opportunities and challenges for the use of such parsimonious decision-support tools, highlighting their importance to mainstream ecosystem services information in urban planning.


Global coastal protection benefits of ecosystems - past, present, and under climate change

June 2023

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91 Reads

Coastal ecosystems have the potential to contribute to disaster risk reduction and adaptation to climate change. While previous studies have estimated the value of current coastal ecosystems for reducing coastal risk, there have been relatively few studies that look at changes in ecosystem service provision, in the past and under climate change. We employ the probabilistic, event-based CLIMADA platform to quantify the protection from tropical cyclones provided by coastal ecosystems, modeling the number of beneficiaries in the past and under future climate change. We also investigate the potential of Nature-based Solutions (NbS), such as mangrove restoration. We find that currently, one in five (21%) of all people impacted annually by tropical cyclones in the global low-elevation coastal zone is within the protection distance of coastal ecosystems. Over the last 30 years, the share of protected people has decreased by approximately 2%, due to ecosystem loss. With climate change, the average annual number of people impacted will increase by 40%. Simultaneously, the proportion of people protected by coastal ecosystems with climate change decreases due to changes in tropical cyclone distribution (-1%). The importance of current coastal protection, and the potential for increasing protection by NbS, varies widely between countries. While the number of people protected globally only increases slightly with mangrove restoration, protection in individual countries can increase by up to 39%. Our findings provide a basis for NbS planning and adaptation policy, by highlighting areas which will be crucial for coastal protection services in a world altered by climate change.


Figure 3
Optimising global conservation, restoration, and agriculture for people and nature

June 2023

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521 Reads

The Kunming-Montreal Global Biodiversity Framework is a worldwide plan to urgently address and reverse biodiversity loss, intending to achieve a harmonious relationship between humanity and nature by 2050. This paper seeks to contribute to operationalising the framework, specifically concerning biodiversity conservation and nature's contributions to people. Using a global analytical approach, we identify optimised areas for conservation, restoration and agriculture, considering food production, urban expansion, population growth, and climate change projections. By formulating scenarios for increasing natural areas enabled by improvements in agricultural productivity and trade, and considering local and global constraints on restoration actions, we analyse potential outcomes for biodiversity and people. Our findings demonstrate that an optimised spatial allocation of land use could substantially mitigate projected negative impacts and even surpass the current situation, leading to significant socio-environmental gains. However, the best global scenarios for nature and people require integrated planning that considers mitigating climate change, reducing human pressure on natural habitats, increasing trade, and changing human behaviour. Aligning efforts to protect and restore nature with broader sustainability goals through coordinated and transformative action is central to implement the Global Biodiversity Framework and delivery of a more sustainable future.


Citations (28)


... Finally, we acknowledge the general need to test the sensitivity of the ES models to changes in parameter values and to validate the models based on local data. The InVEST urban cooling model, for example, has been validated with observational data from case studies and showed generally good model performance, increasing confidence in model outcomes (Bosch et al. 2021;Hamel et al. 2024). Other models, such as the flood control model, use a common method to project runoff in non-urban environments but have not yet been widely applied and tested in the urban context . ...

Reference:

Assessing multiple ecosystem services in 708 European urban areas
Calibrating and validating the Integrated Valuation of Ecosystem Services and Tradeoffs (InVEST) urban cooling model: case studies in France and the United States

... Anthropogenic climate change is rapidly altering Earth's environmental conditions, exacerbating the effects of land use change and habitat loss on global biodiversity decline and further threatening the persistence of many species 1,2 . To track fast-changing environments, organisms can relocate to more suitable areas, respond via phenotypic plasticity, or undergo rapid adaptation [3][4][5] . ...

Global trends and scenarios for terrestrial biodiversity and ecosystem services from 1900 to 2050
  • Citing Article
  • April 2024

Science

... The NDVI is actively used to determine land cover, monitor agricultural land quality and changes over time, and estimate yields (Emery et al. 2024). The lowest NDVI value (0.55) was obtained under rainfed conditions, while the highest value (0.78) was obtained under irrigated conditions. ...

Leveraging satellite observations to reveal ecological drivers of pest densities across landscapes
  • Citing Article
  • March 2024

The Science of The Total Environment

... With the global loss of biodiversity, Nature's Contributions to People (NCP) are expected to be jeopardized too (Ramel et al. 2020;Reid et al. 2006;IPBES 2019). As our society relies on nature for ecosystem services (MEA 2005) such as food provisioning, the societal consequences of species loss and ecosystem degradation have become increasingly raising concerns among scientists and policy makers (Moreira et al. 2024;Neugarten et al. 2024). Yet, the benefits of plant species to people and therein the risks to societies due to biodiversity loss remain poorly quantified on a species-specific basis. ...

Mapping the planet’s critical areas for biodiversity and nature’s contributions to people

... These estimates hint at large potential socioeconomic impacts resulting from climatemodified disturbance regime. Indeed, more than 775 million people are currently estimated to be highly dependent on coastal ecosystems 18 , and the number of people depending on protection by coastal ecosystems is expected to increase further under climate change 36 . Financially, loss of mangrove protective functions could contribute to accelerating losses under climate change, since even under current conditions mangroves provide flood protection benefits beyond US$ 65 billion annually 1 . ...

Global protection from tropical cyclones by coastal ecosystems—past, present, and under climate change

... Meeting these targets raises a clear challenge-how can policy objectives at the global level translate into effective national action? 4 . Spatially identifying intact natural areas is a key component of any strategy designed to meet global conservation challenges and turn policy into action 11 . Numerous projects have set themselves the challenge of mapping human influence and identifying the remaining wild areas (see for example, refs. ...

Mapping the planet’s critical natural assets

Nature Ecology & Evolution

... There is a large body of literature giving recommendations on the aggregation of a set of ES (Langhans et al., 2014), delineating ES-bundles and looking at synergies and trade-offs with a set of methods (Martín-López et al., 2012;Mouchet et al., 2014;Raudsepp-Hearne et al., 2010;Vallet et al., 2018), the inclusion of stakeholder's or societal values (Manning et al., 2018;Martín-López et al., 2012), or calculating multifunctionality indices (Hölting et al., 2019;Manning et al., 2018;Tanács et al., 2023). This further, complementary step is needed to show the individual ES in relation to each other, e.g., on a hotspot map, defining priority areas for protection or restoration (Chaplin-Kramer et al., 2021;Mitchell et al., 2021). Interpreting the obtained complex indicators, correlation matrices, or hot-spot maps, is also challenging, specifically to recognise differences between correlations and causation (Bennett et al., 2009;Sugihara et al., 2012;Vallet et al., 2018). ...

Mapping the planet’s critical natural assets for people

... Compared with the above CS models, InVEST requires fewer types of data, is easy to obtain and operate, has fast computation and high accuracy in quantitative assessment, is capable of spatial and temporal visualization, and is more suitable for spatial analysis of CS triggered by changes in LUCC [40]. However, CS within the same LUCC type will show different attribute characteristics and spatial-temporal characteristics due to changes in the natural and economic and social environments [39], and their spatial compositions and the historical changes in LUCC [41,42] will be significantly different, and the conflict between LUCC and CS and economic and social development will arise. LUCC conflict is the external manifestation of the competition for spatial resources [43]. ...

Spatial heterogeneity in forest carbon storage affects priorities for reforestation

... InVEST has been successfully applied in various contexts to estimate biophysical and economic metrics, offering a valuable approach for assessing complex ecosystem dynamics and trade-offs (Polasky et al., 2012;Jiang et al., 2017). Studies using InVEST have shown that spatial patterns of ecosystem services are influenced by a range of factors, including land use and elevation (Salata et al., 2017), and have highlighted the importance of spatial information in supporting environmental management and policy decisions (Hamel et al., 2021;Ismaili Alaoui et al., 2023). For instance, research has demonstrated how urbanization, agricultural expansion, and land use changes influenced ecosystem services supply such as: carbon sequestration, water provision, and food production . ...

Mapping the benefits of nature in cities with the InVEST software

npj Urban Sustainability

... Current assessment methods often fall short in capturing this complexity, as they focus narrowly on specific performance metrics, such as peak flow reduction or pollutant removal rates, without considering broader contextual factors or the integrated benefits of green infrastructure. As a result, there is a pressing need for a comprehensive framework that can systematically evaluate the effectiveness of green infrastructure in managing urban stormwater while accounting for its multifaceted impacts (Griffin et al., 2020). ...

Including Additional Pollutants into an Integrated Assessment Model for Estimating Nonmarket Benefits from Water Quality
  • Citing Article
  • November 2020

Land Economics