ECOSYSTEM SERVICES AS A BASIS FOR CLIMATE ADAPTATION INDICATORS: A CASE FROM URBAN INDIA Shaila Naaz 1 1 Research
Scholar, Gautam Buddha University, Gautam Buddh
Nagar, Uttar Pradesh, India 2 Head,
Department of Urban and Regional Planning, Gautam Buddha University, Gautam Buddh Nagar, Uttar Pradesh, India
1. INTRODUCTION Climate change is one of the most pressing challenges of the 21st century, especially in rapidly urbanising regions where vulnerabilities are compounded by population growth, resource stress, and ecosystem degradation IPCC (2022). Cities, while major contributors to greenhouse gas emissions, are also hotspots of climate risks, including heatwaves, flooding, water scarcity, and deteriorating air quality Revi et al. (2014). In this context, urban ecosystem services (UES) the benefits humans derive from ecosystems, are increasingly recognised as essential assets for climate adaptation MEA (2005), Elmqvist et al. (2015). These services provide regulatory, provisioning, cultural, and supporting functions that enable urban populations to mitigate and adapt to climate impacts. Ecosystem-based adaptation (EbA) emphasises integrating ecosystem services into climate resilience strategies Munang et al. (2013). Urban green spaces, wetlands, and tree cover regulate microclimates, reduce stormwater runoff, sequester carbon, and offer psychological and cultural benefits Kabisch et al. (2016), Haase et al. (2014). However, urban development trajectories in the Global South often marginalise ecological considerations in favour of grey infrastructure, reducing the effectiveness of ecosystems in climate mitigation and adaptation Nagendra et al. (2018). This creates a pressing need to develop measurable indicators that explicitly capture the role of ecosystem services in urban climate adaptation strategies. Indicators translate complex ecological and social dynamics into actionable information for planners, policymakers, and communities Singh et al. (2021). Although global frameworks such as the Sustainable Development Goals (SDGs) and the Convention on Biological Diversity highlight the importance of ecosystem services, their operationalisation into urban climate adaptation indicators remains limited in India Pandey et al. (2018). Developing robust indicators requires not only ecological data but also insights into local perceptions, socio-economic realities, and governance structures. Urban India exemplifies the urgent need for ecosystem service-based indicators. Rapid urbanisation has led to wetland encroachment, declining tree cover, and the loss of urban commons, undermining the capacity of ecosystems to provide climate-regulating services Singh et al. (2021), Sharma and Tomar (2010). Identifying and operationalising ecosystem service-based indicators can provide a pathway for embedding resilience into urban planning. By aligning adaptation strategies with local ecological functions and socio-cultural priorities, cities can move toward more sustainable, climate-resilient futures. This study contributes to the field by developing ecosystem service-based climate adaptation indicators for urban India using a mixed-methods approach. By combining qualitative interviews and quantitative surveys, it identifies, evaluates, and prioritises indicators that can inform urban policy and planning, bridging the gap between ecological theory, indicator frameworks, and practical urban realities. 1.1. BACKGROUND & LITERATURE REVIEW 1.1.1. Urban Ecosystem Services and Climate Adaptation Urban ecosystem services (UES) refer to the diverse benefits that humans derive from ecosystems in urban environments, including provisioning, regulating, supporting, and cultural services MEA (2005), Gómez-Baggethun and Barton (2013). Regulating services, such as microclimate moderation, stormwater management, and air purification, directly support climate adaptation by reducing urban vulnerabilities, while cultural and supporting services contribute to well-being, recreation, and biodiversity conservation Elmqvist et al. (2015), Haase et al. (2014). Ecosystem-based adaptation (EbA) integrates these services into urban resilience strategies, aiming to enhance adaptive capacity while maintaining ecological integrity Munang et al. (2013). Urban green spaces, wetlands, and urban forests, for example, mitigate the urban heat island effect, regulate hydrological cycles, sequester carbon, and provide recreational and psychological benefits to residents McPhearson et al. (2016). Despite these benefits, urban development in rapidly growing cities, particularly in the Global South, often prioritises infrastructural expansion over ecological conservation, limiting the effectiveness of UES in adaptation planning Nagendra et al. (2018). 1.1.2. Indicators for Climate Adaptation Indicators are measurable parameters that translate complex ecological and social data into actionable information for policymakers, planners, and communities Singh et al. (2021). They provide a mechanism for monitoring, evaluation, and adaptive management of urban ecosystems and climate adaptation initiatives. Global frameworks such as the Sustainable Development Goals (SDGs) and the Convention on Biological Diversity stress the importance of using indicators to operationalise ecosystem services for sustainable and climate-resilient urban development Pandey et al. (2018). In India, while several studies have focused on mapping and valuing ecosystem services, few have operationalised these insights into measurable climate adaptation indicators. Most existing work is either ecological or theoretical, with limited integration of socio-economic realities and public perceptions, which are critical for locally relevant and actionable indicators Singh et al. (2021), Sharma and Tomar (2010). 1.1.3. Public Awareness and Perception of Ecosystem Services Awareness and perception of UES among urban residents significantly influence the success of adaptation strategies Andersson et al. (2014). Research shows that individuals who understand the ecological, social, and economic benefits of urban nature are more likely to support conservation initiatives, participate in urban greening programs, and advocate for policy interventions Ernstson and Sörlin (2013), Buizer et al. (2016). In India, studies indicate that while urban residents value green spaces for recreation and aesthetics, their understanding of regulating services, such as flood control, air purification, and microclimate regulation, is often limited Nagendra et al. (2018), Haase et al. (2014). Integrating public perception into indicator development ensures that climate adaptation strategies are both ecologically sound and socially acceptable. Interviews and surveys provide a critical understanding of community knowledge, experiences, and priorities, informing the selection and prioritisation of UES-based indicators Raymond et al. (2017). 1.1.4. Urban India as a Case Context India is undergoing rapid urbanisation, with cities facing mounting challenges from ecosystem degradation and heightened climate vulnerabilities. Urban expansion has led to wetland encroachment, declining tree cover, and fragmentation of green spaces, undermining the capacity of ecosystems to deliver climate-regulating services Singh et al. (2020). Indian cities such as Delhi, Mumbai, and Bengaluru illustrate these pressures, where ecological planning is often secondary to infrastructural and commercial demands Sharma and Tomar (2010). Developing ecosystem service-based indicators in this context provides a mechanism to embed resilience into urban planning. By linking ecological functions to measurable metrics, indicators can guide policy, prioritise interventions, and track the effectiveness of climate adaptation strategies Pandey et al. (2018) 1.1.5. Research Gap Although UES and EbA are increasingly recognised in the literature, few studies in India have operationalised these concepts into practical, measurable indicators that integrate ecological, social, and governance dimensions Nagendra et al. (2018), Singh et al. (2021). Existing research primarily focuses on ecosystem assessment or theoretical frameworks, leaving a gap in context-specific, community-informed indicators. This study addresses this gap by employing qualitative interviews and quantitative surveys to develop locally relevant ecosystem service-based climate adaptation indicators for urban India. 2. MATERIALS AND METHODS 2.1. RESEARCH DESIGN This study employed a mixed-methods research design, integrating qualitative interviews and quantitative surveys to develop ecosystem service-based indicators for climate adaptation in urban India. The mixed-methods approach allows for the triangulation of data, combining ecological insights with social perceptions to generate robust, context-specific indicators Creswell and Plano Clark (2018). The qualitative component aimed to understand expert perspectives, while the quantitative component assessed broader awareness and knowledge among urban residents. 2.2. STUDY AREA The study focused on urban India, representing diverse ecological, socio-economic, and infrastructural contexts. Indian cities face rapid urbanisation, climate vulnerabilities, and ecosystem degradation, making them suitable for exploring ecosystem service-based climate adaptation strategies Sharma and Tomar (2010), Singh et al. (2020). Dwarka Sub City in New Delhi has been selected based on ecological significance, vulnerability to climate risks, and availability of urban green infrastructure. 2.3. DATA COLLECTION 1) Qualitative
Interviews · Purpose: To gather expert knowledge on relevant ecosystem services, their climate adaptation potential, and feasible indicators. · Participants: Urban planners, environmental scientists, ecologists, and local government officials. · Method: Semi-structured interviews conducted online and in-person, allowing flexibility to probe specific ecosystem services and climate risks. · Sampling: Purposive sampling was used to select participants with substantial knowledge or decision-making authority in urban ecosystem management. · Analysis: Thematic content analysis was performed to identify key ecosystem services, adaptation priorities, and potential indicator metrics Braun and Clarke (2006). 2) Quantitative
Surveys · Purpose: To assess public perception, awareness, and knowledge of urban ecosystem services and their role in climate adaptation. · Participants: Urban residents from diverse socio-economic backgrounds. · Method: Structured questionnaires administered online and offline, covering awareness of green spaces, wetlands, urban forests, air quality regulation, flood mitigation, and other ecosystem services. · Sampling: Stratified random sampling was applied to ensure representation across age, gender, education, and residential location. · Analysis: Descriptive statistics, correlation analysis, and ranking exercises were performed using SPSS and Excel to evaluate the importance and awareness of specific ecosystem services. 2.4. INDICATOR DEVELOPMENT FRAMEWORK The study developed ecosystem service-based climate adaptation indicators through a three-step process: 1) Identification of Ecosystem Services: Combining literature review with qualitative interview insights to list relevant UES that contribute to climate adaptation Elmqvist et al. (2015), Munang et al. (2013). 2) Prioritisation and Weighting: Using survey responses to evaluate public perception, importance, and perceived effectiveness of each ecosystem service. Techniques such as Likert-scale scoring and Analytic Hierarchy Process (AHP) were employed to assign weights to indicators Saaty (2008). 3) Indicator Refinement and Validation: Indicators were refined based on expert feedback, ensuring feasibility, measurability, and policy relevance. Final indicators were categorised under regulating, provisioning, supporting, and cultural services, aligned with the Millennium Ecosystem Assessment framework MEA (2005). 2.5. ETHICAL CONSIDERATIONS 1) Participants provided informed consent before interviews and surveys. 2) Anonymity and confidentiality of respondents were maintained throughout the study. 3) Data collection protocols followed institutional ethical guidelines for research involving humans. 3. RESULTS AND DISCUSSIONS: 3.1. Google Form Questionnaire Responses & Analysis: Figure 1
According to the people, policy reforms and institutional frameworks, Incentives for green infrastructure investments, and public-private partnerships for urban green projects will be the best strategies to scale up ecosystem-based climate adaptation. Figure 2
According to the people, Enhancing Blue-Green Infrastructure for Flood Control and Increasing Biodiversity and Habitat Connectivity should be prioritised for future climate adaptation. Figure 3
Technological advancement like IoT-Based Environmental Monitoring (Air Quality, Heat, Water Levels), GIS and Remote Sensing for Ecosystem Mapping, Smart Green Infrastructure (e.g., automated irrigation, adaptive green walls) & Circular Economy Approaches for Waste and Water Management can enhance urban ecosystem services for climate change adaptation. Figure 4
Better policy integration implementation, Cross-Sector Collaboration (Govt, NGOs, Private Sector) & Community-Based Initiatives for Green Infrastructure can improve the implementation of ecosystem services of urban planning and governance.
Figure 5
Urban Green Infrastructure Policies are the most important framework that supports urban ecosystem services. Figure 6
Urban Ecosystem Services are partially integrated into climate change adaptation policies Figure 7
Figure 8
The most critical climate change challenges in urban areas are Urban Heat Island Effect (UHI), Increased Flooding and Waterlogging, Declining Air Quality and Pollution, Water Scarcity and Droughts & Biodiversity Loss and Habitat Fragmentation Figure 9
More than half of the participants have observed interventions based on ecosystem services in urban areas to address climate change. Figure 10
Urban ecosystem services play an important role in Carbon Sequestration (Tree Planting and Greenery), Absorption of Particulate Matter (PM2.5, PM10) & Cooling Microclimates to Reduce Smog Formation. Figure 11
Urban Tree Canopy Cover, Water Bodies (Lakes, Wetlands, Urban Rivers), Permeable Surfaces and Vegetated Swales & Green Roofs and Vertical Gardens are ecosystem services which are effective in mitigating urban heat stress. Figure 12
Urban Wetlands and water bodies are effective in flood mitigation. 3.2. Survey and Interview Analysis 3.2.1. Introduction To interpret the qualitative insights gathered through resident surveys and stakeholder interviews, a thematic content analysis (TCA) was conducted. The analysis aimed to identify recurring patterns of perception, experience, and awareness regarding urban ecosystem services (UES) and their contribution to climate change adaptation within Dwarka, New Delhi. Data from open-ended questionnaire responses and semi-structured interviews were transcribed, coded, and organized using a hybrid inductive–deductive approach. This method allowed themes to emerge organically while aligning them with the established categories of ecosystem services—Regulating, Supporting, Cultural, and Provisioning—under the Millennium Ecosystem Assessment framework. 3.2.2. Coding and Theme Development Initial open coding generated over 120 descriptive codes, which were then condensed into subthemes and five main themes representing how residents perceive, experience, and engage with urban ecosystem services in their neighbourhood. NVivo 14 software facilitated data organization and clustering of codes into broader thematic categories. Table 1
3.2.3. Discussion The analysis revealed that residents strongly associate green and blue spaces with thermal comfort, air quality improvement, and psychological relief—indicating intuitive awareness of regulating and cultural ecosystem services. However, institutional and governance challenges emerged as a recurring barrier, particularly in maintenance and policy enforcement. The presence of strong community-led initiatives, such as plantation drives and rainwater harvesting, demonstrates grassroots-level adaptation potential aligned with the principles of ecosystem-based adaptation (EbA). Residents’ perceptions showed a high degree of dependence on tangible services (e.g., shade, cooling, cleanliness) but limited understanding of ecological processes (e.g., carbon sequestration, biodiversity support). This gap underscores the importance of education, awareness campaigns, and participatory planning for mainstreaming ecosystem services into urban adaptation strategies. 3.2.4. Conclusion The thematic content analysis underscores that ecosystem services in Dwarka serve both environmental and social adaptation functions. Regulating and cultural services were the most recognized, while supporting and provisioning services were less visible to residents. Effective governance and community engagement emerged as critical determinants of sustainable adaptation outcomes. These insights form the basis for developing localized adaptation indicators and policy recommendations integrating ecosystem services into Dwarka’s urban planning framework.
4. CONCLUSIONS The study reaffirms that ecosystem services form a robust basis for developing climate adaptation indicators, particularly within the complex socio-ecological fabric of rapidly urbanizing regions like Dwarka Sub-city, Delhi. Dwarka’s evolving urban landscape—characterized by fragmented green spaces, altered hydrological systems, and growing climate vulnerabilities—demonstrates the urgent need to recognize and quantify the role of ecosystem functions in supporting urban resilience. By assessing key ecosystem service-based indicators such as vegetation cover, surface temperature regulation, stormwater retention, biodiversity potential, and accessibility to urban green spaces, the research highlights how ecological assets can directly influence the adaptive capacity of urban settlements. Integrating these indicators into Dwarka’s planning and governance frameworks can enhance data-driven decision-making and strengthen the linkage between environmental sustainability and climate adaptation. Moreover, recognizing ecosystem services as critical urban infrastructure shifts the focus from reactive measures—such as flood mitigation and heat stress management—to proactive, nature-based adaptation strategies. In conclusion, embedding ecosystem service-based indicators into Dwarka’s climate adaptation framework can guide policymakers, planners, and citizens toward a more resilient, inclusive, and sustainable urban future. Future research should prioritize participatory assessment methods, spatial mapping of ecosystem functions, and long-term monitoring to refine indicator applicability and ensure that ecosystem-based adaptation becomes a central strategy in Delhi’s climate resilience agenda.
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