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ECOSYSTEM SERVICES AS A BASIS FOR CLIMATE ADAPTATION INDICATORS: A CASE FROM URBAN INDIA

ECOSYSTEM SERVICES AS A BASIS FOR CLIMATE ADAPTATION INDICATORS: A CASE FROM URBAN INDIA

 

Shaila Naaz 1Icon

Description automatically generated, Dr. Nirmita Mehrotra 2

 

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

 

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ABSTRACT

Climate change poses significant threats to urban sustainability, particularly in rapidly growing cities where ecological degradation amplifies vulnerability to extreme weather events. Ecosystem services (ES)—the benefits derived from natural systems—offer a vital framework for developing climate adaptation strategies by linking ecological functions with human well-being. This study explores how ecosystem services can serve as a basis for identifying and evaluating climate adaptation indicators. Through an integrative review of literature and case-based analysis, the research highlights the role of provisioning, regulating, cultural, and supporting services in enhancing adaptive capacity. The final set of indicators was established following a comprehensive data collection process involving surveys and questionnaires administered to key stakeholders. These stakeholders comprised professionals from relevant fields, specifically urban planners, policy makers, architects, urbanists, urban designers, urban foresters, and individuals engaged in the urban infrastructure sector." Indicators such as urban green cover, water retention potential, biodiversity index, carbon sequestration, and social access to green infrastructure are identified as measurable parameters for adaptation assessment. The findings emphasize that embedding ecosystem service-based indicators within urban planning can improve resilience, promote sustainable land-use management, and support evidence-based policy formulation. By positioning ecosystem services at the core of adaptation frameworks, cities can transition from reactive to proactive climate governance that synergizes ecological health with socio-economic sustainability.

 

Received 05 August 2025

Accepted 20 September 2025

Published 31 October 2025

Corresponding Author

Ar. Shaila Naaz, khanshailanaaz@gmail.com 

DOI 10.29121/ijetmr.v12.i10.2025.1687   

Funding: This research received no specific grant from any funding agency in the public, commercial, or not-for-profit sectors.

Copyright: © 2025 The Author(s). This work is licensed under a Creative Commons Attribution 4.0 International License.

With the license CC-BY, authors retain the copyright, allowing anyone to download, reuse, re-print, modify, distribute, and/or copy their contribution. The work must be properly attributed to its author.

 

Keywords: Ecosystem Services, Climate Adaptation, Urban Resilience, Adaptation Indicators, Sustainable Planning, Ecosystem-Based Adaptation

 

 

 

                        


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

Forms response chart. Question title: What strategies should cities adopt to scale up ecosystem-based climate adaptation? (Select all that apply)  . Number of responses: 122 responses.

Figure 1 Strategies for Scaling up Urban ESS

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: Which urban ecosystem services should be prioritized for future climate adaptation?   (Select all that apply)      . Number of responses: 122 responses.

Figure 2 Prioritization of Urban ESS for Future CCA

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: Which technological advancements can enhance urban ecosystem services for climate adaptation? (Select all that apply)  . Number of responses: 122 responses.

Figure 3 Enhancement of Urban ESS for CCA

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: How can urban planning and governance improve the implementation of ecosystem services? (Select all that apply)  . Number of responses: 122 responses.

Figure 4 Implementation of urban ESS

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: Which policy frameworks support urban ecosystem services in your country/city? (Select all that apply)  . Number of responses: 122 responses.

Figure 5 Framework of urban ESS

Source Google Form questionnaire by the Author

 

Urban Green Infrastructure Policies are the most important framework that supports urban ecosystem services.

 Figure 6

Forms response chart. Question title: Are urban ecosystem services adequately integrated into climate adaptation policies?  . Number of responses: 122 responses.

Figure 6 Integration of Urban ESS into CCA Policies

Source Google Form questionnaire by the Author

 

Urban Ecosystem Services are partially integrated into climate change adaptation policies

 Figure 7

Forms response chart. Question title: What are the key barriers to implementing urban ecosystem services in climate adaptation? (Select all that apply)  . Number of responses: 122 responses.

Figure 7 Barriers to implementing urban ESS

Source Google Form questionnaire by the Author

Figure 8

Forms response chart. Question title: What are the most critical climate change challenges in urban areas? (Select all that apply)     . Number of responses: 122 responses.

Figure 8 Critical Climate Change Challenge in Urban ESS

Source Google Form Questionnaire by the Author

 

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

Forms response chart. Question title: Have you observed any specific urban interventions where ecosystem services were used to address climate adaptation?  . Number of responses: 122 responses.

Figure 9 Usage of urban ESS for CCA

Source Google Form questionnaire by the Author

 

More than half of the participants have observed interventions based on ecosystem services in urban areas to address climate change.

Figure 10

Forms response chart. Question title: What role do ecosystem services play in improving urban air quality?  . Number of responses: 122 responses.

Figure 10 Role of urban ESS in addressing CCA

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: Which ecosystem services are most effective in mitigating urban heat stress? (Select all that apply)  . Number of responses: 122 responses.

Figure 11 Urban ESS mitigating Urban Heat Stress

Source Google Form questionnaire by the Author

 

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

Forms response chart. Question title: How effective are wetlands and urban water bodies in flood mitigation?  . Number of responses: 122 responses.

Figure 12 Wetlands and Water Bodies in Flood Mitigation

Source Google Form questionnaire by the Author

 

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

Table 1 Thematic Content Analysis of Urban Ecosystem Services and Climate Adaptation in Dwarka

Theme

Subtheme

Illustrative Quote (Participant)

Interpretation / Adaptation Linkage

Regulating Ecosystem Services

Microclimate regulation; Air purification; Flood mitigation

“The parks around our block keep it cooler, even during the hottest days.” (Resident, Sector 12)

Vegetation and tree canopy reduce urban heat island effects, providing natural cooling and thermal comfort.

“The plantation drives have reduced dust and air pollution near our homes.” (Resident, Sector 10)

Reflects recognition of vegetation’s role in improving air quality and health resilience.

Cultural and Social Ecosystem Services

Recreation and leisure; Stress relief; Community bonding

“Evening walks in the park help me feel calm after a busy day.” (Teacher, Sector 6)

Parks serve as informal adaptation spaces by promoting mental well-being and social cohesion.

“Festivals in the community garden bring everyone together.” (Resident, Sector 5)

Social networks enhanced through green spaces contribute to collective adaptive capacity.

Supporting Ecosystem Services

Biodiversity value; Habitat creation; Soil and water retention

“We have started seeing more birds and butterflies after the new plantation.” (Resident, Sector 9)

Indicates ecological health and biodiversity support, which strengthen long-term adaptation.

Governance and Institutional Factors

Maintenance issues; Policy implementation gaps; Awareness deficit

“Authorities plant trees but don’t maintain them—most dry out after a few months.” (Community member, Sector 23)

Highlights governance and institutional inefficiencies affecting sustainable ecosystem management.

“People don’t know how green areas help during heat waves.” (Planner, DDA)

Suggests the need for environmental literacy and adaptive governance.

Community-Based Adaptation and Participation

Local initiatives; Stewardship; Awareness campaigns

“Our residents’ group cleans the park every Sunday—it’s our responsibility.” (Youth volunteer, Sector 14)

Reflects community-driven adaptation actions that sustain local ecosystems.

“We collect rainwater from rooftops for garden irrigation.” (Resident, Sector 19)

Demonstrates active citizen engagement in small-scale climate resilience measures.

Source: Survey & Interviews by the Author

 

 

 

 

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.

 

CONFLICT OF INTERESTS

None. 

 

ACKNOWLEDGMENTS

None.

 

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