Public Perceptions of Climate Change Trends in the Entre Douro e Minho Region (Northern Portugal): A Comprehensive Survey Analysis
Abstract
1. Introduction
- To quantify the multidimensional nature of climate change perceptions among residents of the Entre Douro e Minho region, examining the relationships between awareness, attribution beliefs, risk perception, and behavioral intentions.
- To identify demographic and spatial predictors of climate change perceptions, test theoretical models of perception formation, and provide insights for targeted communication strategies.
- To assess the role of direct experience with extreme weather events in shaping climate change attribution beliefs, contributing to the understanding of experiential learning processes in climate perception.
- To evaluate public preferences for adaptation measures and their alignment with scientific recommendations, informing evidence-based adaptation planning.
- To develop a comprehensive framework for understanding regional climate change perceptions that can be applied to other Mediterranean and Atlantic European contexts.
- To provide actionable recommendations for climate communication, education, and adaptation policy that account for demographic heterogeneity and local environmental contexts.
2. Materials and Methods
2.1. Study Area
2.2. Survey Design and Instrument
2.3. Sampling Design and Procedures
2.3.1. Primary Stratification
2.3.2. Secondary Stratification
2.3.3. Tertiary Stratification
2.3.4. Sample Size Calculation
2.3.5. Quality Control Procedures
2.3.6. Participant Recruitment Procedures
- Facebook Groups and LinkedIn: Recruitment was conducted through several district-specific Facebook groups and the researcher’s personal connections. Posts were shared on Facebook and LinkedIn, including a brief study description, participation incentive information, and a direct survey link.
- Snowball Sampling: Participants were encouraged to share the survey with family members, friends, and colleagues residing in the target region. This approach was particularly effective for reaching older adults and rural populations who might have limited social media presence.
- Recruitment Timeline and Monitoring: Recruitment was monitored on a weekly basis to ensure balanced representation across districts and demographic groups. When underrepresentation was identified in specific segments (e.g., older adults, rural residents), targeted recruitment efforts were intensified through appropriate channels.
- Response Rate Calculation: The overall response rate of 82.0% was calculated based on 2136 individuals who initiated the survey, with 1749 completing all required questions. Incomplete responses (n = 387) were primarily due to technical issues (45%), time constraints (32%), or voluntary withdrawal (23%). The high completion rate reflects the survey’s appropriate length and user-friendly design.
2.4. Ethical Considerations and Data Protection
2.4.1. Informed Consent Procedures
2.4.2. Data Protection and Privacy Measures
2.5. Psychometric Properties and Instrument Validation
2.5.1. Internal Consistency Reliability
2.5.2. Test–Retest Reliability
2.5.3. Construct Validity
2.5.4. Convergent and Discriminant Validity
2.6. Data Preparation and Analysis
2.6.1. Statistical Analysis
2.6.2. Qualitative Data Analysis and Thematic Coding
- Response Volume and Characteristics: Q13 (territorial planning) received 1247 responses (71.3% response rate) with an average length of 47 words (range: 3–156 words). Q15 (additional suggestions) received 892 responses (51.0% response rate) with an average length of 32 words (range: 2–98 words). The lower response rate for Q15 reflected its optional nature and the effects of survey fatigue.
- Coding Framework Development: An inductive thematic analysis approach was employed, following Braun and Clarke’s six-phase framework. The primary researcher conducted initial code development through careful reading of 200 randomly selected responses (100 from each question). This process identified recurring themes and concepts, leading to the development of a preliminary coding framework with 12 primary categories for Q13 and 9 for Q15.
- Inter-Rater Reliability Procedures: To ensure coding consistency, a second researcher independently coded a subsample of 350 responses (20% of total responses, stratified by district and response length). Inter-rater reliability was assessed using Cohen’s kappa coefficient, achieving substantial agreement for Q13 (κ = 0.78) and Q15 (κ = 0.81). Disagreements were resolved through discussion and consensus, leading to refinement of coding definitions.
- Coding Process and Time Investment: The complete coding process required approximately 180 h of researcher time, distributed by 40 h to framework development and pilot coding, 95 h to primary coding of all responses, 25 h to inter-rater reliability assessment, and 20 h to consensus discussions and code refinement.
- Q13 on Territorial Planning identified six primary themes from responses: Infrastructure Adaptation, comprising 34.2% of responses and including flood defenses, drainage systems, and climate-resilient buildings; Land Use Restrictions at 28.7%, involving building limitations in risk areas and zoning modifications; Green Infrastructure at 24.1%, encompassing urban forests, green corridors, and permeable surfaces; Coastal Management at 18.9%, featuring sea walls, dune restoration, and managed retreat; Risk Assessment Integration at 15.3%, incorporating hazard mapping and vulnerability assessments; and Community Participation at 12.8%, involving public consultation and local knowledge integration.
- Q15 on Additional Suggestions identified five primary themes from responses: Technology Solutions, comprising 31.4% of responses and including renewable energy, smart systems, and early warning; Policy Recommendations at 27.8%, involving regulations, incentives, and enforcement mechanisms; Community Initiatives at 23.6%, encompassing local action groups and neighborhood projects; Education Programs at 19.2%, featuring awareness campaigns, school curricula, and training; and Economic Instruments at 16.7%, incorporating subsidies, tax incentives, and green financing.
- Quality Assurance Measures: Coding quality was maintained through regular team meetings, ongoing calibration exercises, and systematic documentation of coding decisions. A coding manual was developed with detailed definitions, examples, and decision rules for each category. Random quality checks were conducted throughout the process, with 5% of coded responses re-examined for consistency.
- Quantitative Integration: Thematic frequencies were calculated and integrated with quantitative findings to provide comprehensive insights. Chi-square tests were conducted to examine associations between demographic variables and thematic preferences, revealing significant relationships between education level and policy-oriented suggestions (χ2 = 23.4, p < 0.001) and between coastal residence and infrastructure-focused responses (χ2 = 18.7, p < 0.01).
2.6.3. Perception–Reality Correspondence Analysis
- Objective Climate Data Sources: Climate trend data were obtained from multiple authoritative sources, for daily temperature and precipitation records from the existing meteorological stations across the study region; annual burned area statistics and fire frequency data at municipal level; coastal erosion data along the Entre Douro e Minho coastline; and the stream flow and drought indices for major river basins in the study area.
- Trend Calculation Methodology: For each climate variable, objective trends were calculated using standardized approaches: temperature trends involved linear regression analysis of annual maximum temperature days (>35 °C) and heatwave frequency (≥3 consecutive days >35 °C) for the period 1990–2024, with trends expressed as percentage change per decade; wildfire trends included calculating annual burned area per 1000 inhabitants for each municipality, with trends assessed using Mann–Kendall trend analysis due to non-normal distributions and results expressed as percentage change over the 2000–2024 period; precipitation trends entailed identifying extreme precipitation events (>20 mm/day and >40 mm/day) and calculating trends using Poisson regression to account for count data characteristics, with trends expressed as percentage change in event frequency per decade; and coastal erosion trends consisted of linear retreat rates calculated from annual shoreline position measurements, with trends expressed as meters per year averaged across monitoring points within each district.
- Individual-Level Correlation Analysis: Step 1—Geographic Matching, each survey respondent was assigned objective climate trend values based on their municipality of residence, with inverse distance weighting used to interpolate values for municipalities without direct measurements for variables measured at meteorological stations; in Step 2—Perception Quantification, individual perception responses were converted to numerical scales, using binary responses (observed/not observed) for extreme weather phenomena (Q9) and retaining the original 1–5 scale values for Likert-scale questions (Q6–Q8, Q10–Q11); in Step 3—Correlation Calculation, Spearman rank correlations were calculated between individual perception scores and corresponding objective trend values, an approach that accounts for the ordinal nature of perception data and non-normal distributions in climate trends; and in Step 4—Aggregation Analysis, to validate individual-level correlations, district-level aggregated correlations were also calculated using mean perception rates and mean objective trends for each district.
- Correlation Results and Interpretation: The analysis revealed strong correlations between public perceptions and objective climate trends across various phenomena: for temperature-related phenomena, the individual-level correlation between heatwave perception (Q9) and objective heatwave trend was r = 0.78 (p < 0.001, n = 1749), while the district-level correlation was r = 0.94 (p = 0.22, n = 3), showing high correlation but non-significant due to small sample size; for wildfire activity, the individual-level correlation between wildfire perception (Q9) and municipal burned area trends was r = 0.82 (p < 0.001, n = 1749), with the district-level correlation at r = 0.89 (p = 0.31, n = 3); for precipitation events, the individual-level correlation between storm perception (Q9) and extreme precipitation trends was r = 0.54 (p < 0.001, n = 1749), and the district-level correlation was r = 0.67 (p = 0.52, n = 3); finally, for coastal erosion, the individual-level correlation between erosion perception (Q9) and shoreline retreat rates was r = 0.31 (p < 0.001, n = 1749), which increased to r = 0.58 (p < 0.001) among coastal residents only (n = 423) but dropped to r = 0.18 (p < 0.001) for inland residents (n = 1326).
- Methodological Considerations: The weaker correlation for coastal erosion reflects differential exposure patterns, as confirmed by separate analysis of coastal versus inland residents. The moderate correlation for precipitation events likely reflects the complex nature of precipitation trends, where total amounts remain stable while intensity patterns change. Strong correlations for temperature and wildfire phenomena suggest these provide clear, memorable signals that accurately inform public perceptions.
- Validation Procedures: Correlation robustness was assessed through bootstrap resampling to generate confidence intervals. Sensitivity analyses examined the impact of different geographic matching approaches and temporal windows. Results remained consistent across methodological variations, supporting the reliability of the perception–reality correspondence findings.
3. Results
3.1. Sample Characteristics
3.2. Climate Change Awareness and Attribution
3.3. Extreme Weather Phenomena Perception
3.4. Demographic Influences on Climate Perceptions
3.5. Adaptation Measure Preferences
3.6. Internal Consistency and Scale Reliability
4. Discussion
4.1. High Levels of Climate Change Awareness and Attribution
4.2. Comparison with European Climate Perception Research
4.3. Correspondence with Objective Climate Trends and Media Influence
4.3.1. Wildfire Validation
4.3.2. Temperature Validation
4.3.3. Precipitation Validation:
4.3.4. Coastal Erosion Context
4.4. Demographic Influences and Social Differentiation
4.5. Extreme Weather Phenomena and Risk Perception
4.6. Adaptation Preferences and Policy Implications
4.7. Methodological Considerations and Limitations
4.8. Implications for Climate Communication and Policy
4.9. Study Limitations and Implications for Future Research
4.9.1. Methodological Limitations
4.9.2. Measurement and Analytical Limitations
4.9.3. Sampling and Generalizability Constraints
4.9.4. Implications for Future Research
5. Conclusions
Supplementary Materials
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Characteristic | Category | n | Percentage (%) |
---|---|---|---|
District | Porto | 1000 | 57.2 |
Braga | 537 | 30.7 | |
Viana do Castelo | 212 | 12.1 | |
Age Group | 18–24 | 185 | 10.6 |
25–34 | 240 | 13.7 | |
35–44 | 311 | 17.8 | |
45–54 | 345 | 19.7 | |
55–64 | 385 | 22 | |
65+ | 282 | 16.1 | |
Gender | Female | 920 | 52.6 |
Male | 801 | 45.8 | |
Prefer not to say | 28 | 1.6 | |
Education Level | Basic Education | 506 | 28.9 |
Secondary Education | 652 | 37.3 | |
Bachelor’s Degree | 210 | 12 | |
Master’s Degree | 210 | 12 | |
PhD | 94 | 5.4 | |
Other | 77 | 4.4 |
Variable | District | n | Mean | CI_Lower | CI_Upper |
---|---|---|---|---|---|
General Climate Change Awareness | Overall | 1749 | 3.87 | 3.82 | 3.92 |
General Climate Change Awareness | Viana do Castelo | 212 | 3.92 | 3.79 | 4.06 |
General Climate Change Awareness | Braga | 537 | 3.9 | 3.82 | 3.98 |
General Climate Change Awareness | Porto | 1000 | 3.85 | 3.79 | 3.91 |
Drought Frequency Perception | Overall | 1749 | 3.89 | 3.84 | 3.94 |
Drought Frequency Perception | Viana do Castelo | 212 | 3.95 | 3.82 | 4.08 |
Drought Frequency Perception | Braga | 537 | 3.93 | 3.85 | 4.01 |
Drought Frequency Perception | Porto | 1000 | 3.85 | 3.79 | 3.91 |
Heavy Rainfall Frequency Perception | Overall | 1749 | 3.77 | 3.72 | 3.82 |
Heavy Rainfall Frequency Perception | Viana do Castelo | 212 | 3.82 | 3.69 | 3.95 |
Heavy Rainfall Frequency Perception | Braga | 537 | 3.8 | 3.72 | 3.88 |
Heavy Rainfall Frequency Perception | Porto | 1000 | 3.75 | 3.69 | 3.81 |
Attribution to Climate Change | Overall | 1749 | 3.82 | 3.77 | 3.87 |
Attribution to Climate Change | Viana do Castelo | 212 | 3.89 | 3.76 | 4.02 |
Attribution to Climate Change | Braga | 537 | 3.84 | 3.76 | 3.92 |
Attribution to Climate Change | Porto | 1000 | 3.8 | 3.74 | 3.86 |
Daily Impact Perception | Overall | 1749 | 3.32 | 3.27 | 3.37 |
Daily Impact Perception | Viana do Castelo | 212 | 3.47 | 3.34 | 3.60 |
Daily Impact Perception | Braga | 537 | 3.31 | 3.23 | 3.39 |
Daily Impact Perception | Porto | 1000 | 3.29 | 3.23 | 3.35 |
Extreme Weather Phenomenon | n | Percentage (%) | 95% CI |
---|---|---|---|
Wildfires | 1353 | 77.4 | 72.7–82.1% |
Heatwaves | 1234 | 70.6 | 65.9–75.3% |
Intense Storms | 904 | 51.7 | 47.0–56.4% |
Coastal Erosion | 617 | 35.3 | 30.6–40.0% |
Unusual Snow Events | 192 | 11 | 6.3–15.7% |
Demographic Variable | Climate Variable | Spearman ρ | p-Value | Significant | Effect Size |
---|---|---|---|---|---|
Education Level | Climate Attribution (Q10) | 0.279 | <0.001 | Yes | Small |
Education Level | Daily Impact (Q11) | 0.094 | <0.001 | Yes | Negligible |
Age | Climate Attribution (Q10) | −0.255 | <0.001 | Yes | Small |
Age | Daily Impact (Q11) | −0.002 | 0.926 | No | Negligible |
Gender (Female) | Climate Attribution (Q10) | 0.05 | 0.037 | Yes | Negligible |
Gender (Female) | Daily Impact (Q11) | −0.045 | 0.058 | No | Negligible |
Adaptation Measure | n | Percentage (%) | 95% CI |
---|---|---|---|
Reforestation and Forest Management | 1351 | 77.3 | 72.6–82.0% |
Flood/Drought Resistant Infrastructure | 1131 | 64.7 | 60.0–69.4% |
Public Education and Awareness | 967 | 55.3 | 50.6–60.0% |
Emission Reduction Policies | 844 | 48.3 | 43.6–53.0% |
Coastal Protection | 778 | 44.5 | 39.8–49.2% |
Sustainable Agriculture | 769 | 44 | 39.3–48.7% |
Green Urban Planning | 629 | 36 | 31.3–40.7% |
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Nunes, L.J.R. Public Perceptions of Climate Change Trends in the Entre Douro e Minho Region (Northern Portugal): A Comprehensive Survey Analysis. Climate 2025, 13, 196. https://doi.org/10.3390/cli13090196
Nunes LJR. Public Perceptions of Climate Change Trends in the Entre Douro e Minho Region (Northern Portugal): A Comprehensive Survey Analysis. Climate. 2025; 13(9):196. https://doi.org/10.3390/cli13090196
Chicago/Turabian StyleNunes, Leonel J. R. 2025. "Public Perceptions of Climate Change Trends in the Entre Douro e Minho Region (Northern Portugal): A Comprehensive Survey Analysis" Climate 13, no. 9: 196. https://doi.org/10.3390/cli13090196
APA StyleNunes, L. J. R. (2025). Public Perceptions of Climate Change Trends in the Entre Douro e Minho Region (Northern Portugal): A Comprehensive Survey Analysis. Climate, 13(9), 196. https://doi.org/10.3390/cli13090196