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Urban Social Sustainability Assessment: A Case Study of Phnom Penh, Cambodia

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22 December 2024

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24 December 2024

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Abstract
The world is rapidly urbanizing. By 2050, 2.5 billion people will gradually shift from rural to urban areas, with close to 90% of this shift taking place in Africa and Asia. In Southeast Asia, Cambodia’s Phnom Penh capital city is rapidly growing, making its development concerned with sustainability and inclusiveness, hereafter called “social sustainability”. Hence, this research aims to assess the social sustainability of the Phnom Penh capital city, to find out the strengths and weaknesses of its districts (14 khans), and then provide recommendations on improvement potentials for each district. This research developed an urban social sustainability assessment framework based on national development priorities, the New Urban Agenda, SDG11 (sustainable cities), and other SDGs that incorporated human wellbeing, such as SDGs1-6, SDG8, SDG10, and SDG12. The standard variable model was applied to standardize indicators before comparison to obtain high accuracy, and the data were sourced from the Phnom Penh capital socio-economic data (commune database). The results showed that the most sustainable district was Chamkarmon, followed by Boeng Keng Kang and Doun Penh. Prek Pnov was found to be weak in income generation and welfare while Kamboul was weak in structured gender equality. Prampir Makara was more resilient to vulnerability while Sen Sok was weak in this dimension. Boeng Keng Kang was strong in welfare and sanitation while Kamboul was weak in sanitation. Doun Penh was strong in clean water supply while Mean Chey was weak in this dimension.
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1. Introduction

In the United Nations Conference on Sustainable Development, known as the Rio+20 Earth Summit [1], which was a follow-up to the 1992 Rio Earth Summit and the 2002 Rio+10 Earth Summit [2], the UN member states agreed to launch a process to formulate a set of sustainable development goals (SDGs) [1]. This was one of the global agendas to address global issues, which urbanization is known as the major issue since the world is rapidly urbanizing. The UN statistics showed that more than half of the world population has lived in urban areas [3]. The UN projected that nearly 70 percent of the world population is expected to live in urban areas by 2050 [4,5]. The projection showed that with the gradual shift of population from rural to urban areas, 2.5 billion people will possibly be added to urban areas by 2050, with close to 90 percent of this shift occurring in Asia and Africa [4]. This can be elaborated that rapid urbanization is mostly occurring in developing countries. Particularly, in Southeast Asia, rapid urbanization is occurring in Cambodia and six other countries, such as Indonesia, Malaysia, Philippines, Singapore, Thailand, and Vietnam, according to the Martin Prosperity Institute, and this region’s urban population was expected to grow by another 100 million people by 2030, adding to the current population of 280 million people [6]. Therefore, improving the quality of urban life and urban inclusion and sustainability are needed for these countries in Southeast Asia, including Cambodia.
In 2015, the Sustainable Development Goals (SDGs) were adopted by 193 countries towards ending poverty and creating continuous peace and prosperity for the people and planet, which set to be achieved by the year 2030 [7,8]. In particular, SDG11 aims to make cities and human settlements inclusive, safe, resilient, and sustainable, known in short as sustainable cities and communities [9]. Especially, Target 11.a was set to support positive economic, social, and environmental links between urban, peri-urban, and rural areas by strengthening national and regional development planning [10]. Specifically, the New Urban Agenda (NUA), adopted by 167 countries in 2016, is aimed for setting a new global standard for planning, management, and living in cities [11]. The NUA has served as an important tool for sustainable development of cities in both developed and developing countries by offering a series of sustainable urban development standards that aim at offering basic services for all citizens and ensuring that all citizens have access to equal opportunities and face no discrimination [12,13]. The basic services provided includes the access to adequate housing, nutritious food, clean water and sanitation, healthcare, education, and family planning while ensuring that all citizens have equally access to opportunities and face no discrimination (everyone has the right to benefit from what their cities offer, while calling on city authorities to take into account the inclusiveness) [12]. This means the NUA is significantly addressing SDG4 (quality education) [14] and SDG5 (gender equality) [15].
Literature showed that education significantly has a direct influence on environmental attitudes and an indirect influence on environmental behavior [16,17,18]. Consequently, education is a core component of pro-environmental behavior and influences the long-term development of sustainable cities and communities. According to OECD [19], improved gender equality in decision-making and the professions related to urban planning have also contributed to the optimization of settlements and urban infrastructure investments to meet the needs of all people, achieved social inclusion, particularly underrepresented groups. Moreover, since urban children’s populations have rapidly increased, there is a strong commitment, globally, in promoting child-friendly cities and communities [3]. The UNICEF has developed a framework for action to build child-friendly cities and communities, which outlined the steps to build a governance system [20,21]. Especially, UNICEF produced a guide book, setting building blocks for developing child-friendly cities and communities, providing good practices and lessons learned to guide the city governments and relevant stakeholders [22]. This brings local stakeholders together with the UNICEF to create cities and communities to offer safe, inclusive, and responsive conditions for children [23,24,25], which is the indicator for a successful city for everyone [26].
In Cambodia, the government successfully implemented the Triangular Strategy (1998–2003) and the Rectangular Strategy in four distinct phases (2004–2023), with significant achievements in all areas, including economy, society, and politics, enabling Cambodia to proudly return its image of the last 25 years with full peace, territorial integrity, and national unity achieved through a win–win policy [27]. This has significantly contributed to a positive socioeconomic development in the country [28,29]. The notable results are (i) Cambodia obtained a lower-middle-income status in 2015 (World Bank [30]) and became a New Tiger Economy in Asia in 2016 (ADB [31]). With its Rectangular Strategy, the government identified four priority areas for the development, which set people (human resource) as the first priority, followed by road, electricity, and water [32]. Thus, the government has increased the national budget for the education sector. The education budget has increased from 278.87 million in 2015 to 724.80 million USD in 2020 [33], and kept growing in the following years. Moreover, literature also showed that the first key priority of the finance strategy for archiving SDGs in Cambodia was also the education sector, including gender mainstreaming [34].
By realizing the past 25 years of achievements, especially global and regional trend assessments, and for the next 25-year prognostications, the government upgraded its Rectangular Strategy to a new strategy, namely Pentagonal Strategy. The Pentagonal Strategy Phase I (2023-2028) has set the national development priorities centered on the themes of growth, employment, equity, efficiency, and sustainability [35]. The main objective of this new strategy is to obtain an upper-middle-income status in 2030 and to realize the Cambodia Vision 2050, become a high-income country, toward meeting its people’s aspirations. Thus, the strategy aims to boost growth, create jobs, ensure equity, increase efficiency, and maintain sustainability [24]. This strategy serves as a guideline to direct activities of all relevant stakeholders to continue to maintain peace and the momentum and accumulation of past achievements, as well as to build the foundation towards accelerating medium- and long-term development through targeted reforms across all sectors [36]. In particular, the objective of the “Pentagon 4” is for “resilient, sustainable, and inclusive development” in which the “priority 4” is aimed at strengthening urban management, focusing on existing urban areas in the capital city and provinces, to ensure safety, beauty, good environment, and well-being of people, as well as socio-economic efficiency [35].
The summary above showed that literature in the field and global agendas, SDGs and NUA, especially national development priorities of Cambodia centered around sustainability and inclusiveness as important for sustainable urban development and management. This research reflects these aspects with the development of the Cambodia’s Phnom Penh capital city. Currently, the Phnom Penh capital city has a population of more than two million and faces rapid urban development issues [37,38,39] and challenges in improving the quality of life and in achieving sustainable development goals on social dimensions [9]. In this regard, the assessment of this capital city, particularly its 14 capital districts (known in Khmer as capital khans) based on social sustainability dimensions would find out its strengths and weaknesses, especially the improvement potential. Hence, this research aims to assess the social sustainability of the Phnom Penh capital city, to find out the strengths and weaknesses of its districts (14 khans), and then provide recommendations on improvement potentials for each district. This research developed an urban social sustainability assessment framework based on the national development priorities, the New Urban Agenda, SDG11 (sustainable cities), and other SDGs that incorporated human well-being, such as SDGs1-6, SDG8, SDG10, and SDG12. The standard variable model was applied to standardize indicators before comparison to obtain high accuracy, and the data were sourced from the Phnom Penh capital socio-economic data (commune database). This research is also the update and expansion of the article “Assessing urban sustainability and the potential to improve the quality of education and gender equality in Phnom Penh” [11], which is the latest series of the following studies: development and prioritization of sustainable city indicators for Cambodia (2019) [40,41]; sustainability of the capital and emerging cities of Cambodia (2020) [42]; child-friendly urban development in Phnom Penh, Cambodia (2021) [5]; urban quality assessment of Cambodia’s Phnom Penh capital khans (2022) [43].

2. Methodology

2.1. Assessment Framework

As summarized in the above section, this research developed an urban social sustainability assessment framework based on existing literature, the global sustainable urban development agenda (NUA), and SDGs such as SDG11 (sustainable cities and communities), and other SDGs that incorporated human well-being, including SDGs1-6, SDG8, SDG10, and SDG12. Especially, the framework was based on the national development priorities of Cambodia indicated in the Pentagonal Strategy, particularly the “Pentagon 4—Resilient, Sustainable, and Inclusive Development” and its priority 4—strengthening urban management, focusing on existing urban areas in the capital city and provinces, to ensure safety, beauty, good environment, and well-being of people, as well as socio-economic efficiency [44].
The assessment framework was so-called Urban Sustainability and Inclusiveness (USI) integration as shown in Figure 1. The first cycle “U” referred to the national development priorities for cities/urban areas indicated in the Pentagonal Strategy, particularly the “Pentagon 4—resilient, sustainable, and inclusive development” and its priority 4—strengthening urban management, focusing on existing urban areas in the capital city and provinces, to ensure safety, beauty, good environment, and well-being of people, as well as socio-economic efficiency. The second cycle “S” referred to the sustainable development goal 11 (SDG11—make cities and human settlements inclusive, safe, resilient, and sustainable) [45,46] and the New Urban Agenda (NUA—offering basic services for all citizens and ensuring that all citizens have access to equal opportunities and face no discrimination) [12,13]. The third cycle “I” referred to the other SDGs that incorporated human well-being and social inclusion, which included SDG1 (end poverty in all its forms everywhere), SDG2 (end hunger, achieve food security and improved nutrition and promote sustainable agriculture), SDG3 (ensure healthy lives and promote well-being for all at all ages), SDG4 (ensure inclusive and equitable quality education and promote lifelong learning opportunities for all), SDG5 (achieve gender equality and empower all women and girls), SDG6 (ensure availability and sustainable management of water and sanitation for all), SDG8 (promote sustained, inclusive, and sustainable economic growth, full and productive employment, and decent work for all), SDG10 (reduce inequality within and among countries), and SDG12 (ensure sustainable consumption and production patterns) [47].
Furthermore, the crosscutting sections are U-S (integrated urban national priorities and SDG11 and NUA), U-I (integrated urban national priorities and SDGs1-6, SDG8, SDG10, and SDG12), and S-I (integrated SDGs1-6, SDG8, SDG10, and SDG12 and SDG11 and NUA). Thus, urban social sustainability assessment index was the USI set of indicators. Based on this assessment framework and data availability from the Phnom Penh capital city’s socio-economic data (commune database) [48], this research consequently obtained 32 indicators for urban social sustainability assessment of the Phnom Penh capital city’s 14 districts. These indicators are divided into 8 categories “income, gender, welfare, education, vulnerability, clean water, sanitation, and safety, as shown in Table 1.

2.2. Indicator Weighting Analysis

This research analyzed the weights of urban social sustainability indicators in order to find out their relative weight which is very important to improve the accuracy of the comparative assessment. Therefore, the analytic hierarchy process (AHP) was used to analyze their relative weight. AHP is widely known as a structured technique for organizing and analyzing complex decisions based on mathematics and psychology. It was founded by Thomas L. Saaty in the 1970s [49,50], who partnered with Ernest Forman to develop Expert Choice in 1983 and has been extensively studied and improved since then [51,52]. It represents a valid method for weighing analysis of any criteria or indicators. Individual experts’ experiences are utilized to estimate the relative magnitudes of factors through pairwise comparisons while these pairwise comparisons must be consistent [49,51]. Therefore, the consistency ratio must be less than or equal to 0.1 (CR ≤ 0.1 or CR ≤ 10%). The AHP structure of the urban social sustainability assessment indicators (32 indicators) classified by 8 categories are shown in Figure 2.
The weights of all indicators were analyzed by calculating the principal eigenvector through the AHP matrix. Its consistency was assessed through the consistency index (CI) and the consistency ratio (CR), as shown in the following Equations (1) and (2):
C I = λ m a x n n 1
and
C R = C I R I
Where, λmax corresponds to the maximum eigenvalue of the pairwise comparison matrix; n is the number of the pairwise-comparison indicators demonstrated in table above; and RI is a random consistency index that depends on the number of pairwise-comparison indicators. More importantly, the consistency ratio (CR) must be lower than or equal to 0.1 (CR ≤ 0.1) [49,51].
In particular, this research followed the theories and practical applications of Soldatou et al. (2022) [52] and Dongmin et al. (2020) [53], as well as AHP-based research [54,55], to analyze the weights of indicators by the AHP technique since the author has applied this technique extensively in analyzing the weights of urban sustainability indicators in Cambodia. Therefore, the relative weights of urban social sustainability assessment indicators (Table 2) were analyzed based on the author’s experiences and his practical applications in the following series of research publications: Chan and Lee 2019 [40]; Chan and Lee 2019a [41]; Chan 2020 [42]; Chan 2021 [5]; Chan 2022 [56]; and Chan et al. 2023 [11]. In summary, the survey obtained 102 consistent respondents from the offline (face-to-face) interview, mainly with the government officials, and online surveys through E-mail, Facebook, and LinkedIn. The surveyed respondents were experienced in working in the fields of sustainable cities and community planning, development, management, and assessment in Cambodia.

2.3. Standardizing Variables

Standardizing variables is a statistical technique that makes different variables more comparable, which can be useful for a number of reasons, including: Ensuring equal contribution (standardization ensures that all variables contribute evenly to a scale when items are added together), revealing essential findings (standardization can help reveal essential findings that you would otherwise miss), determining which variable is most important (standardization can help determine which variable is the most important), comparing regression coefficients (when variables have the same variances, it is easier to compare the relative magnitudes of different regression coefficients), and simplifying computation (standardization simplifies the computation of sample covariances and correlations) [57,58]. There are some ways to standardize variables. For example, subtracting the mean from the value for each case and dividing the difference between the individual’s score and the mean by the standard deviation. Based on these reasons, this research consequently standardized variables, values of indicators, before the comparison.
Therefore, comparative assessments by standardizing variables, values of indicators, and using indicator weights were found to be a significant approach to improve the accuracy of the comparison, especially for this research of comparative urban social sustainability assessment of Phnom Penh’s 14 capital khans (14 districts). Based on the normal distribution model, statistical standard variables, or Z-values, or standard scores defined the number of standard deviations with the value of a raw score (for example, the indicator values or data observed) being higher or lower than the mean value of what was observed or measured [42]. The above-average raw scores or raw values resulted in positive standard scores, while the below-average scores or values resulted in negative standard scores, as shown in Figure 3.
Furthermore, the Z-values were calculated by subtracting the mean of population from each raw score (variable), and then dividing the difference by the deviation from the population (variables). The process of converting raw scores into standardized scores is termed normalization; however, normalization can refer to a wide range of ratios. Calculating the Z-values requires the specification of a mean value (average), and the standard deviation of the full population (variables) with which the data points were associated. If only a sample of population observations is available, then approximation with the sample mean value (average) and standard deviation gives the T-statistic [61].
Kreyszig [62] claimed that the analyzed population mean value and standard deviation of raw score X was converted into a standard score by the following formula, with μ standing for the mean of the population, and σ representing the standard deviation of the population:
Z = X μ σ
The absolute value of Z represents the distance between the raw score X and the population mean in units of standard deviation; Z is negative when the raw score is below the average, and positive when it is above the average. The standard normal distribution tables developed by Claude et al. in 2016, and revised by Claude in 2017 [60], were to provide probability values (P-values). According to the developed tables [60], Z values (values in the left column and on the top row) are points on the horizontal scale, whereas probabilities (values in the body of the table) are the regions bounded by the normal curve and horizontal scale.
In this research after obtaining the Z values, Phnom Penh’s 14 capital khans (14 districts) were then classified ranks based on the probability values (P-values). Since there were 14 districts, the ranking has been resulted in between 1 and 14. Furthermore, the scoring scales were then made based on the ranking, which means that the 1st rank received 14 scores, 2nd rank got 13 scores, and 3rd rank got 12 scores; this continued till the 13th rank got 2 scores, and 14th (last) rank got 1 score. After obtaining the scores of all 14 districts by each indicator, this research subsequently analyzed the weighted values (W-values) by multiplying the ranked scores by the total weights of urban social sustainability assessment indicators.

2.4. Data Source and Analysis

As mentioned in the above section, this research comparatively assessed urban social sustainability of the 14 districts (khans) of Phnom Penh, the capital and largest city of Cambodia with a total population of 2,129,371 in 2019 [63]. The Phnom Penh capital is located at the intersection of four rivers (locally called four-face river), namely Sap River (Tonle Sap), Upper Mekong River, Lower Mekong River, and Bassac River. Figure 4 below illustrates the capital map with the location and population of each district.
The data by each indicator of all 14 districts that have been used in this research were sourced from the Phnom Penh Capital Socio-Economic Data in 2019 (the government’s source), which was prepared and published by Phnom Penh Capital Department of Planning under the Ministry of Planning of Cambodia [48]. The data used for all urban social sustainability indicators were verified and translated from the Cambodian language, and calculated based on the required unit of each indicator.
By using the standard variable model to comparatively assess urban social sustainability of Phnom Penh’s 14 districts allowed this research to find out the strengths and weaknesses of each capital district by each urban social sustainability indicator. According to the first and second clean city contests conducted by the National Committee for Clean City Assessment [64], many capital districts have been awarded Clean City Romduol III (1st rank) and Romduol II (2nd rank). Especially, each of these capital districts has its own strong level or strong point by each indicator. Therefore, developing a standard based on their good levels or strong points of indicators would be much appropriate to assess other districts and/or its peers to reveal the potential for urban social sustainability improvement in the Cambodia context and the preference of Cambodian people. Accordingly, this research developed a standard level for each assessment indicator based on the average of strong levels of very good districts. Finally, this research applied this standard to find out the strong and weak points of each district and demonstrate the potential for improvement of each district.

3. Results and Discussion

3.1. Income Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “income-generation indicators” showed that Chamkarmon was found to be the strongest khan (1.9892), followed by Doun Penh (1.5644) and Boeng Keng Kang (1.5481). Furthermore, the ratio of employees working in production and services per 1,000 populations was found to be highest in Chamkarmon, followed by Doun Penh and Boeng Keng Kang, while the ratio of populations, aged 18-35, has joined vocational training per 1,000 populations was found to be highest in Prampir Makara, followed by Chamkarmon and Mean Chey. Moreover, the percentage of households living in quality houses was found to be highest in Chamkarmon, Pou Senchey, and Boeng Keng Kang, while the percentage of main and secondary non-agricultural jobs by women was found to be highest in Kamboul, followed by Chamkarmon and Pou Senchey (see Figure 5).

3.2. Gender-Inclusive Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “gender-inclusive indicators” showed that Doun Penh was found to be the strongest khan (1.2891), followed by Chbar Ampov (1.1634) and Boeng Keng Kang (1.1332). Furthermore, the ratio of female students to male students studied at high schools and universities was found to be highest in Doun Penh, Tuol Kouk, Dangkao, Sen Sok, Prek Pnov, Chbar Ampov, and Boeng Keng Kang, while the percentage of female teachers taught at primary and secondary schools was found to be highest in Prampir Makara, followed by Tuol Kouk and Chamkarmon. Moreover, the ratio of female employees to total employees in production and services was found to be highest in Chroy Changvar, followed by Mean Chey and Doun Penh, while the percentage of commune’s and district’s council members as women was found to be highest in Kamboul, followed by Doun Penh and Boeng Keng Kang, as shown in Figure 6.

3.3. Welfare Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “welfare indicators” showed that Boeng Keng Kang was found to be the strongest (1.5254), followed by Prampir Makara (1.4363) and Doun Penh (1.4206). Furthermore, the ratio of the number of households without violence (family violence) per 1,000 households was found to be highest in Boeng Keng Kang, followed by Tuol Kouk, and Doun Penh, while the ratio of pharmacy and clinics per 100,000 populations was found to be highest in Boeng Keng Kang, followed by Doun Penh and Prampir Makara. Moreover, the percentage of children have joined childcare/kindergarten programs aged 3-5 was found to be highest in Tuol Kouk, followed by Boeng Keng Kang and Prampir Makara, as well as Doun Penh and Chamkarmon, while the ratio of under-five survivals per 1,000 births was found to be highest in Doun Penh, Prampir Makara, and Boeng Keng Kang, as shown in Figure 7.

3.4. Education Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “education indicators” showed that Chamkarmon was found to be the strongest (1.9307), followed by Boeng Keng Kang (1.6225) and Kamboul (1.5371). Furthermore, the percentage of children studied at primary schools aged 6-11 was found to be highest in Chamkarmon and Kamboul, while the percentage of children studied at secondary schools aged 12-14 was found to be highest in Kamboul, followed by Chamkarmon and Prampir Makara. Moreover, the percentage of literate youth aged 15-24 was found to be highest in Chamkarmon, Boeng Keng Kang, Prampir Makara, Pou Senchey, and Kamboul, while the percentage of literate adults and middle-aged groups (25-45) was found to be highest in Chamkarmon, followed by Boeng Keng Kang, Prampir Makara, Pou Senchey, and Kamboul, as shown in Figure 8.

3.5. Vulnerability Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “vulnerability indicators” showed that Prampir Makara was found to be the most resilient (1.2233), followed by Chamkarmon (1.1817) and Tuol Kouk (1.0970). Furthermore, the ratio of vulnerable groups (orphans, homeless, disables, and elders) per 1,000 population was found to be the slightest in Chamkarmon (high score), followed by Russey Keo and Tuol Kouk, while the ratio of households living on public land (informal/illegal settlements) per 1,000 households was found to be the slightest in Doun Penh (high score), followed by Prampir Makara and Kamboul. Moreover, the ratio of land conflict cases per 1,000 households was found to be the slightest in Prampir Makara and Boeng Keng Kang (high score), followed by Tuol Kouk and Kamboul, while the ratio of households’ members with drug abuse per 1,000 households was found to be slightest in Boeng Keng Kang (high score), followed by Tuol Kouk, and Chamkarmon (see Figure 9).

3.6. Sanitation Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “sanitation indicators” showed that Boeng Keng Kang was found to be the strongest (1.2585), followed by Prampir Makara (1.2557) and Chamkarmon (1.2506). Furthermore, the percentage of households accessible to waste collection services was found to be highest in Tuol Kouk, followed by Russey Keo and Doun Penh, while the percentage of households that have not been affected by environmental pollutions was found to be highest in Prampir Makara, followed by Chamkarmon and Chbar Ampov. Moreover, the ratio of primary, secondary, and high schools that have installed proper toilets per one hundred students was found to be highest in Prek Pnov, followed by Boeng Keng Kang and Prampir Makara, while the percentage of households that have installed proper toilets was found to be highest in Doun Penh, followed by Boeng Keng Kang, Chamkarmon, and Pou Senchey, as shown in Figure 10.

3.7. Clean Water Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “clean water indicators” showed that Doun Penh was found to be the strongest (1.6919) followed by Prek Pnov (1.6191) and Tuol Kouk (1.4789). Furthermore, the percentage of households with potable water drinking and consuming habits was found to be highest in Doun Penh, Tuol Kouk, Chroy Changvar, Prek Pnov, and Kamboul, while the percentage of households close to water sources (less than 150 meters) was found to be highest in Russey Keo, followed by Mean Chey and Pou Senchey. Moreover, the percentage of primary, secondary, and high schools accessible potable water to use/drink was found to be highest in Chamkarmon, Doun Penh, Prampir Makara, Russey Keo, Sen Sok, Pou Senchey, Chroy Changvar, Prek Pnov, Boeng Keng Kang, and Kamboul, while the percentage of households accessible potable water to use/drink was found to be highest in Chamkarmon, Doun Penh, Prampir Makara, Tuol Kouk, Russey Keo, Prek Pnov, Chbar Ampov, and Boeng Keng Kang, as shown in Figure 11.

3.8. Safety Indicators

The results of the urban social sustainability assessments of the Phnom Penh’s 14 capital khans (districts) of “safety indicators” showed that Mean Chey was found to be the strongest khan (1.8914) followed by Chamkarmon (1.8159) and Prampir Makara (1.7726). Furthermore, the ratio of criminal cases per 100,000 populations was found to be the slightest (highest score) in Chamkarmon, Doun Penh, Prampir Makara, Mean Chey, Pou Senchey, Chroy Changvar, and Boeng Keng Kang, while the ratio of households affected by floods per 1,000 households was found to be the slightest (highest score) in Chamkarmon, Doun Penh, Tuol Kouk, Mean Chey, Sen Sok, Pou Senchey, Prek Pnov, and Boeng Keng Kang. Moreover, the ratio of deaths by diseases, such as malarias, dengue fevers, and tuberculosis, per 100,000 populations was found to be the slightest (highest score) in Tuol Kouk, Mean Chey, and Chroy Changvar, while the ratio of deaths by traffic accidents per 100,000 populations was found to be the slightest (highest score) in Doun Penh, followed by Chamkarmon and Prampir Makara, as shown in Figure 12.

3.9. Comparative Urban Assessment Results of 14 Districts by Categories

Urban income was assessed through the following indicators: employees in both production and services (Careers), skilled populations (Training), income impacts on housing and settlements (Housing), and women’s incomes of both main and secondary nonagricultural jobs (W-jobs). The most sustainable khan for urban income was Chamkarmon (1.9892) whereas the last rank was Prek Pnov (0.4077).
Urban gender-inclusive was assessed through the following indicators: female students have studied until high-school or university levels (Students), female teachers have taught at primary or secondary schools (Teachers), female technical trained or skilled workers in production and services (T-workers), and female council members at commune or district levels that have roles in making decision (M-decision). The most sustainable khan for gender-inclusive was Doun Penh (1.2891) whereas the last rank was Kamboul (0.5203).
Urban welfare was assessed through the following indicators: family violence (F-violence), sufficiency and closeness of healthcare clinics or pharmacy within a district (Healthcare), children have joined childcare or kindergarten programs (Childcare), and survivals of newborns to under-five babies (Newborn). The most sustainable khan for urban welfare was Boeng Keng Kang (1.5254) whereas the last rank was Prek Pnov (0.3228). The comparative assessment results of all khans by categories are shown in Figure 13.
Urban education was assessed through the following indicators: enrolled primary education aged 6-11 (Primary), enrolled secondary education aged 12-14 (Secondary), youth literacy aged 15-24 (Y-literacy), and adults and middle-aged group literacy aged 25-45 (A-literacy). The most sustainable khan for urban education was Chamkarmon (1.9307) whereas the last rank was Sen Sok (0.3495).
Urban vulnerability was assessed through the following indicators: vulnerable groups of orphans, homeless, disables, and elder populations (V-groups), informal settlements on the public land (I-settlements), land conflicts (L-conflicts), and households who have members with drug abuse (D-abuse). The most sustain-able khan (low vulnerability) was Prampir Makara (1.2233) whereas the last rank was Sen Sok (0.4626).
Urban sanitation was assessed through the following indicators: household waste collection (Wastes), households affected by polluted environments (Polluted), schools have installed proper toilets (School) and households have installed proper toilets (Home). The most sustainable khan for urban sanitation was Boeng Keng Kang (1.2585) whereas the last rank was Kamboul (0.3430).
Urban clean water was assessed through the following indicators: accessible and close to water sources (Access), schools that have potable water to use/drink (S-water), households that have potable water to use/drink (H-water), and potable water drinking/consuming habits (Habit). The most sustainable khan for urban clean water was Doun Penh (1.6919) whereas the last rank was Mean Chey (0.5022).
Urban safety and security were assessed through the following indicators: criminal cases (Crimes), households that have been affected by floods (Floods), the ratio of the deaths by diseases (Diseases), and the ratio of the deaths by traffic accidents (Accidents). The most sustainable khan for urban safety was Mean Chey (1.8914) whereas the last rank was Chbar Ampov (0.4725).
The top-five khans were Chamkarmon (10.7896), Boeng Keng Kang (10.6996), Doun Penh (10.6766), Prampir Makara (10.6553), and Tuol Kouk (9.2817), respectively, whereas the fourteenth (last) rank was Dangkao (5.1188). Chamkarmon got the first rank because this khan obtained the first rank for two categories (Income and Education) that these categories had high relative weights. More than that, this khan also obtained the second rank for two categories (Safety and Resilience), as well as the third rank for one category (Sanitation). Boeng Keng Kang got the second rank because this khan obtained the first rank for two categories (Welfare and Sanitation) that these categories had upper-middle relative weights. Furthermore, this khan also obtained the second rank for one category (Education), as well as the third rank for two categories (Income and Gender-inclusive). Doun Penh got the third rank because this khan obtained the first rank for two categories (Gender-inclusive and Clean Water) that one of these categories had the upper-middle relative weight. Moreover, this khan also obtained the second rank for one category (Income), as well as the third rank for one category (Welfare). All urban social sustainability ranks of 14 districts (khans) are shown in Figure 14.

3.10. Strong and Weak Points of Each District by Urban Social Sustainability Indicators

By standardizing variables (indicators’ values) to comparatively assess urban social sustainability of 14 capital khans (14 districts) of the Cambodian capital, Phnom Penh, this research obtained a standard to measure the strong and weak points of each capital khan by each urban social sustainability assessment indicator. According to the first and second clean city contests conducted by the National Committee for Clean City Assessment [64], many capital districts have been awarded Clean City Romduol III (1st rank) and Romduol II (2nd rank). Especially, each of these capital districts has its own strong level or strong point by each indicator. Therefore, developing a standard based on their good levels or strong points of indicators would be much appropriate to assess other districts and/or its peers to reveal the potential for urban social sustainability improvement in the Cambodia context and the preference of Cambodian people.
Therefore, this research obtained the standard level (orange color), which was significant to find out the strong and weak points ‘current level’ (blue color) of each district by each assessment indicator. Based on the consolidated assessment results of urban social sustainability indicators, this research also revealed urban improvement potential ‘weakness’ as demonstrated in the following pages’ paragraphs and figures.
Towards achieving urban social sustainability of each district, particularly the national development priorities, the New Urban Agenda, SDG11, and other SDGs that incorporated human wellbeing, such as SDGs1-6, SDG8, SDG10, and SDG12, the indicators that are lower than the standard need to be improved. This improvement can be made based on the (strong) districts’ achievements and/or best practices.
According to Figure 15, in the case of Chamkarmon, improvement potentials for urban social sustainability indicators were on eight (8) indicators, especially on clean water and gender-inclusive categories. This research strongly suggests improving the following indicators: clean water drinking/consuming habits, accessibility and closeness to water sources, female technical or skilled workers in production and services, and female council members at commune or district level that have roles in making decision.
According to this figure again, in the case of Doun Penh, improvement potentials for urban social sustainability indicators were on seven (7) indicators, especially on the vulnerability category. This research strongly suggests improving the following indicators: vulnerable groups of orphans, homeless, disables, and elder populations, land conflicts, and households that have members with drug abuse.
According to Figure 16, in the case of Prampir Makara, improvement potentials for urban social sustainability indicators were on five (5) indicators, especially on the income category. This research strongly suggests improving the following indicators: income impacts on housing conditions, and women’s income of both main and secondary nonagricultural jobs.
According to this figure again, in the case of Tuol Kouk, improvement potentials for urban social sustainability indicators were on twelve (12) indicators, especially on gender-inclusive and sanitation categories. This research strongly suggests improving the following indicators: female students has studied until high-school/university level, female teachers has taught at primary/secondary schools, households who have been affected by polluted environments, and schools has installed proper toilets.
According to Figure 17, in the case of Dangkao, improvement potentials for urban social sustainability indicators were on twenty-four (24) indicators, especially all clean water indicators and three indicators for each of other categories, except the vulnerability category (two indicators). This research strongly suggests improving the following indicators: clean water indicators (potable water drinking/consuming habits, accessibility or closeness to water sources, schools that have potable water to use/drink, and households that have potable water to use/drink); and the income indicators (employees in both production and services, skilled populations, and income impacts on housing conditions).
According to this figure again, in the case of Mean Chey, improvement potentials for urban social sustainability indicators were on twenty-one (21) indicators, especially all indicators of education and sanitation categories, as well as three indicators for each of clean water and vulnerability categories. This research strongly suggests improving education indicators (primary education, secondary education, youth literacy, and adults and middle-aged group literacy); and sanitation indicators (household waste collection, households who have been affected by polluted environments, schools have installed proper toilets, and households have installed proper toilets.
According to Figure 18, in the case of Russey Keo, improvement potentials for urban social sustainability indicators were on eighteen (18) indicators, especially on income, welfare, vulnerability, and safety categories. This research strongly suggests improving income indicators (employees in both production and services, skilled populations, and income impacts on housing conditions); safety indicators (criminal cases, households affected by floods, and deaths by diseases); and welfare indicators (sufficiency/closeness of clinics/ pharmacy, children joined childcare/kindergarten programs, and survivals of newborns to under-five baby).
According to this figure again, in the case of Sen Sok, improvement potentials for urban social sustainability indicators were on twenty-one (21) indicators, especially on all indicators of education and three indicators for each of gender-inclusive, vulnerability, sanitation, and clean water categories. This research strongly suggests improving the following education indicators (primary education, secondary education, youth literacy, and adults and middle-aged group literacy).
According to Figure 19, in the case of Pou Senchey, improvement potentials for urban social sustainability indicators were on fourteen (14) indicators, especially on gender-inclusive and income indicators. This research strongly suggests improving the following indicators: gender-inclusive indicators (female students have studied until high school/university level, female teachers taught at primary/secondary schools, and female council members at commune/district level with having roles in making decision); and income indicators (employees in both production and services, and skilled populations).
According to this figure again, in the case of Chroy Changvar, improvement potentials for urban social sustainability indicators were on seventeen (17) indicators, especially on welfare indicators. This research strongly suggests improving the following indicators: family violence, sufficiency/closeness of healthcare clinics and pharmacy within a district or khan, children have joined childcare/kindergarten programs, and survivals of newborns to under-five babies.
According to Figure 20, in the case of Prek Pnov, improvement potentials for urban social sustainability indicators were on twenty-two (22) indicators, especially on income, gender, welfare, education, vulnerability, sanitation, and safety categories. This research highly suggests improving the following income and welfare indicators (employees in both production and services, skilled populations, and income impacts on housing conditions, family violence, sufficiency/closeness of healthcare clinics and pharmacy within a district or khan, and children have joined childcare/kindergarten programs).
According to this figure again, in the case of Chbar Ampov, improvement potentials for urban social sustainability indicators were on twenty-four (24) indicators, especially on income, education, vulnerability, and safety categories. This research strongly suggests improving the following high-weight income and safety indicators (employees in both production and services, skilled populations, income impacts on housing conditions, women’s income of both main and secondary nonagricultural jobs, criminal cases, households affected by floods, deaths by diseases, and deaths by traffic accidents).
According to Figure 21, in the case of Boeng Keng Kang, improvement potentials for urban social sustainability indicators were on seven (7) indicators, especially on income and gender-inclusive categories. This research strongly suggests improving the following indicators: women’s income of both main and secondary jobs, accessibility to water sources/reservoirs, and deaths by traffic accidents).
According to this figure again, in the case of Kamboul, improvement potentials for urban social sustainability indicators were on twenty (20) indicators, especially the vulnerability category (all indicators), as well as gender-inclusive, sanitation, and safety categories (three indicators for each). This research strongly suggests improving the following vulnerability indicators (vulnerable groups of orphans, homeless, disables, and elder populations, informal/illegal settlements on public land, land conflicts, and households that have members with drug abuse); and the high-weight safety indicators (criminal cases, households have been affected by floods, and deaths by traffic accidents).

4. Conclusions

This research developed an urban social sustainability index based on national development priorities demonstrated in the Pentagonal Strategy, particularly Pentagon 4—resilient, sustainable, and inclusive development and its Priority 4—strengthening urban management, focusing on existing urban areas in the capital city and provinces, to ensure safety, beauty, good environment, and well-being of people, as well as socio-economic efficiency; SDG11 (make cities inclusive, safe, resilient, and sustainable), New Urban Agenda (providing basic services and ensuring that all citizens have access to equal opportunities), and other SDGs that incorporated human wellbeing, such as SDGs1-6, SDG8, SDG10, and SDG12. By standardizing variables (weighted indicators’ values) to comparatively assess urban social sustainability of 14 khans (14 districts) of the Cambodian capital, Phnom Penh, this research obtained a standard to measure the strong and weak points of each capital district by each urban social sustainability assessment indicator.
The results showed that Chamkarmon was found to be the strongest district in social sustainability, followed by Boeng Keng Kang and Doun Penh, whereas Prampir Makara and Tuol Kouk were ranked fourth and fifth, respectively. The strongest district for urban income was Chamkarmon whereas Prek Pnov was found to be the weakest. The strongest district for urban gender-inclusive was Doun Penh whereas Kamboul was found to be the weakest. The strongest district for urban welfare was Boeng Keng Kang whereas Prek Pnov was found to be the weakest. The strongest district for urban education, excluding vocational training, was Chamkarmon whereas Sen Sok was found to be the weakest. The strongest district for urban resilience, less vulnerable, was Prampir Makara whereas Sen Sok was found to be the weakest. The strongest district for urban sanitation was Boeng Keng Kang whereas Kamboul was found to be the weakest. The strongest district for urban clean water supply and consumption habit was Doun Penh whereas Mean Chey was found to be the weakest. The strongest district for urban safety was Mean Chey whereas Chbar Ampov was the weakest.
The findings showed that Chamkarmon got the first rank because this district obtained the first rank for income and education, that these categories had high relative weights. Furthermore, Chamkarmon obtained the second rank for safety and resilience categories as well. This district also obtained the third rank for sanitation. Subsequently, Boeng Keng Kang got the second rank because this district obtained the first rank for welfare and sanitation, that these categories had upper-middle relative weights. Moreover, Boeng Keng Kang obtained the second rank for education as well. This district also obtained the third rank for income and gender-inclusive, excluding vocational training. Consequently, Doun Penh got the third rank because this district obtained the first rank for clean water and gender-inclusive, but only one of these two categories had an upper-middle relative weight. This district also obtained the second rank for income and the third rank for welfare.
This research considered technical and vocational trainings as skilled labor-force indicators and included them in the income category. Therefore, the education and gender-inclusive indicators in this research did not cover technical and vocational training indicators. In this case, the weighted and/or ranked assessment results might be slightly different if these indicators were included in education and gender-inclusive categories, not in the income category. Furthermore, this research considered the income had impacts on housing conditions, which mean if households were living in poor quality houses, ex. palm-leaf or less-than-20-zinc houses, their income would be low. However, not all households with good incomes spent their money on house upgrading or development, but this ratio was very low and would not impact much on the results.
In this regard, future research exploring these aspects in detail would be more interesting and further improving the understanding of income-spending behaviors of Phnom Penh residents, particularly in each of the 14 districts. In addition, gender-inclusive in decision making in this research was limited to the management levels of public administration. Therefore, this gender-inclusive assessment results could not reflect the management levels of non-governmental organizations, private companies, development partners, and/or civil societies in each district. The future research taking these aspects into account could contribute to a wider understanding of gender-inclusive in decision making across those organizations.

Funding

This research received no external funding.

Acknowledgments

The author expresses his gratitude to the Asia Research Center and CHEY Institute for Advanced Studies for a small grant to support this research.

Conflicts of Interest

The author declares no conflict of interest.

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Figure 1. Urban social sustainability assessment framework.
Figure 1. Urban social sustainability assessment framework.
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Figure 2. AHP structured urban social sustainability index.
Figure 2. AHP structured urban social sustainability index.
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Figure 3. Standardizing variable approach before comparison. Source: Chan 2020 [42], adapted from Ward and Murray and Claude et al. 2016 [59,60].
Figure 3. Standardizing variable approach before comparison. Source: Chan 2020 [42], adapted from Ward and Murray and Claude et al. 2016 [59,60].
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Figure 4. Populations of 14 capital districts (khans) and their location on the Phnom Penh capital map.Source: Chan 2022 [43], adapted from Sovan Dara and capital socio-economic data [48].
Figure 4. Populations of 14 capital districts (khans) and their location on the Phnom Penh capital map.Source: Chan 2022 [43], adapted from Sovan Dara and capital socio-economic data [48].
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Figure 5. Urban social sustainability assessment results of income indicators.
Figure 5. Urban social sustainability assessment results of income indicators.
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Figure 6. Urban social sustainability assessment results of gender-inclusive indicators.
Figure 6. Urban social sustainability assessment results of gender-inclusive indicators.
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Figure 7. Urban social sustainability assessment results of welfare indicators.
Figure 7. Urban social sustainability assessment results of welfare indicators.
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Figure 8. Urban social sustainability assessment results of education indicators.
Figure 8. Urban social sustainability assessment results of education indicators.
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Figure 9. Urban social sustainability assessment results of vulnerability/resilience indicators.
Figure 9. Urban social sustainability assessment results of vulnerability/resilience indicators.
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Figure 10. Urban social sustainability assessment results on sanitary aspects.
Figure 10. Urban social sustainability assessment results on sanitary aspects.
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Figure 11. Urban social sustainability assessment results of clean water indicators.
Figure 11. Urban social sustainability assessment results of clean water indicators.
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Figure 12. Urban social sustainability assessment results of safety indicators.
Figure 12. Urban social sustainability assessment results of safety indicators.
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Figure 13. Comparative urban assessment results of all districts by categories.
Figure 13. Comparative urban assessment results of all districts by categories.
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Figure 14. Urban social sustainability ranking of 14 capital districts.
Figure 14. Urban social sustainability ranking of 14 capital districts.
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Figure 15. Urban social sustainability assessment results of Chamkarmon and Doun Penh districts.
Figure 15. Urban social sustainability assessment results of Chamkarmon and Doun Penh districts.
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Figure 16. Urban social sustainability assessment results of Prampir Makara and Tuol Kouk districts.
Figure 16. Urban social sustainability assessment results of Prampir Makara and Tuol Kouk districts.
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Figure 17. Urban social sustainability assessment results of Dangkao and Mean Chey districts.
Figure 17. Urban social sustainability assessment results of Dangkao and Mean Chey districts.
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Figure 18. Urban social sustainability assessment results of Russey Keo and Sen Sok districts.
Figure 18. Urban social sustainability assessment results of Russey Keo and Sen Sok districts.
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Figure 19. Urban social sustainability assessment results of Pou Senchey and Chroy Changvar districts.
Figure 19. Urban social sustainability assessment results of Pou Senchey and Chroy Changvar districts.
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Figure 20. Urban social sustainability assessment results of Prek Pnov and Chbar Ampov districts.
Figure 20. Urban social sustainability assessment results of Prek Pnov and Chbar Ampov districts.
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Figure 21. Urban social sustainability assessment results of Boeng Keng Kang and Kamboul districts.
Figure 21. Urban social sustainability assessment results of Boeng Keng Kang and Kamboul districts.
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Table 1. Urban social sustainability assessment indicators.
Table 1. Urban social sustainability assessment indicators.
No. Indicator Category
1 Careers Ratio of employees in production-services per 1,000 populations Income
2 Training Ratio of populations with vocational training per 1,000 populations
3 Housing Percentage of households living in poor quality houses
4 W-jobs Percentage of main and secondary nonagricultural jobs by Women
5 Students Ratio of female to male students at high school and university (+) Gender
6 Teachers Percentage of female teachers taught at primary-secondary schools
7 T-workers Ratio of female Technical employees to the total in production and services
8 M-decision Percentage of commune/district council members (decision Makers) as women
9 F-violence Ratio of numbers of households/Families with violence per 1,000 households Welfare
10 Healthcare Ratio of pharmacy and clinics per 100,000 populations
11 Childcare Percentage of children joining childcare/kindergarten (aged 3-5)
12 Newborn Ratio of under-five mortality per 1,000 births
13 Primary Percentage of children studying at primary schools (aged 6-11) Education
14 Secondary Percentage of children studying at secondary schools (aged 12-14)
15 Y-literacy Percentage of illiterate Youth (aged 15-24)
16 A-literacy Percentage of illiterate Adults and middle-aged groups (25-45)
17 V-groups Ratio of Vulnerable people per 1,000 population Vulnerability
18 I-settlement Ratio of households living Informally on public land per 1,000 households
19 L-conflicts Ratio of Land conflict cases per 1,000 households
20 D-abuse Ratio of household has Drug-abuse members per 1,000 households
21 Wastes Percentage of households accessing to waste collection services Sanitation
22 Polluted Percentage of households affected by environmental pollutions
23 School Ratio of schools installed proper toilets per 100 students
24 Home Percentage of households installed proper toilets
25 Habit Percentage of households with potable water consuming habits Water
26 Access Percentage of households close to water sources (less than 150 m)
27 S-water Percentage of Schools having potable water to use/drink
28 H-water Percentage of Households having potable water to use/drink
29 Crimes Ratio of criminal cases per 100,000 populations Safety
30 Floods Ratio of households affected by floods per 1,000 households
31 Diseases Ratio of deaths by diseases per 100,000 populations
32 Accidents Ratio of deaths by traffic accidents per 100,000 populations
Table 2. Relative weights of urban social sustainability assessment indicators.
Table 2. Relative weights of urban social sustainability assessment indicators.
Category Cate. Weight Indicator Indic. Weight Relative Weight Rank
Income 0.1448 Careers 0.4771 0.0691 1
Training 0.1382 0.0200 21
Housing 0.2564 0.0371 11
W-jobs 0.1282 0.0186 22
Gender 0.1061 Students 0.3263 0.0346 13
Teachers 0.1632 0.0173 25
T-workers 0.3620 0.0384 10
M-decision 0.1485 0.0158 27
Welfare 0.1166 F-violence 0.1202 0.0140 30
Healthcare 0.2020 0.0235 19
Childcare 0.4566 0.0532 4
Newborn 0.2212 0.0258 18
Education 0.1413 Primary 0.4017 0.0568 2
Secondary 0.3350 0.0473 7
Y-literacy 0.1572 0.0222 20
A-literacy 0.1061 0.0150 28
Vulnerability 0.1069 V-groups 0.2800 0.0299 16
I-settlement 0.4687 0.0501 6
L-conflicts 0.1152 0.0123 32
D-abuse 0.1361 0.0145 29
Sanitation 0.1128 Wastes 0.2802 0.0316 15
Polluted 0.3625 0.0409 8
School 0.1197 0.0135 31
Home 0.2375 0.0268 17
Water 0.1260 Habit 0.4380 0.0552 3
Access 0.1443 0.0182 23
S-water 0.1274 0.0161 26
H-water 0.2904 0.0366 12
Safety 0.1454 Crimes 0.2336 0.0340 14
Floods 0.3645 0.0530 5
Diseases 0.2777 0.0404 9
Accidents 0.1242 0.0181 24
Total 1.0000 - 8.0000 1.0000 -
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