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Article

Community Quality Evaluation for Socially Sustainable Regeneration: A Study Using Multi-Sourced Geospatial Data and AI-Based Image Semantic Segmentation

1
School of Art and Design, Suzhou City University, Suzhou 215000, China
2
Suzhou Institute of Future City Design, Suzhou City University, Suzhou 215000, China
3
School of Design, Xi’an Jiaotong-Liverpool University, Suzhou 215123, China
4
School of Environmental Science, University of Liverpool, Liverpool L69 3BX, UK
5
School of Architecture and Urban Planning, Suzhou University of Science and Technology, Suzhou 215000, China
6
Faculty of Architecture, The University of Hong Kong, Pokfulam Rd, Hong Kong SAR 999077, China
7
School of Architecture and Urban Planning, Nanjing University, Nanjing 210023, China
8
Key Laboratory of Spatial Intelligent Planning Technology, Ministry of Natural Resources, Beijing 101160, China
9
College of Architecture and Urban Planning, Fujian University of Technology, Fuzhou 350118, China
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
ISPRS Int. J. Geo-Inf. 2024, 13(5), 167; https://doi.org/10.3390/ijgi13050167
Submission received: 22 March 2024 / Revised: 7 May 2024 / Accepted: 15 May 2024 / Published: 20 May 2024

Abstract

:
The Chinese urban regeneration movement underscores a “people-oriented” paradigm, aimed at addressing urban challenges stemming from rapid prior urbanization, while striving for high-quality and sustainable urban development. At the community level, fostering quality through a socially sustainable perspective (SSP) is a pivotal strategy for people-oriented urban regeneration. Nonetheless, explorations of community quality assessments grounded in an SSP have been notably scarce in recent scholarly discourse. This study pioneers a multidimensional quantitative model (MQM) for gauging community quality, leveraging diverse geospatial data sources from the SSP framework. The MQM introduces an evaluative framework with “Patency, Convenience, Comfort, and Safety” as primary indicators, integrating multi-sourced data encompassing the area of interest (AOI), Point of Interest (POI), Weibo check-ins, and Dianping data. The model’s efficacy is demonstrated through a case study in the Gusu district, Suzhou. Furthermore, semantic analysis of the Gusu district’s street view photos validates the MQM results. Our findings reveal the following: (1) AI-based semantic analysis accurately verifies the validity of MQM-generated community quality measurements, establishing its robust applicability with multi-sourced geospatial data; (2) the community quality distribution in Gusu district is notably correlated with the urban fabric, exhibiting lower quality within the ancient town area and higher quality outside it; and (3) communities of varying quality coexist spatially, with high- and low-quality communities overlapping in the same regions. This research pioneers a systematic, holistic methodology for quantitatively measuring community quality, laying the groundwork for informed urban regeneration policies, planning, and place making. The MQM, fortified by multi-sourced geospatial data and AI-based semantic analysis, offers a rigorous foundation for assessing community quality, thereby guiding socially sustainable regeneration initiatives and decision making at the community scale.

1. Introduction

“People-centered” and “socially sustainable development” principles have emerged as paramount guiding principles in global urban regeneration efforts aimed at achieving sustainable urban development [1,2,3]. In China, the 14th five-year national plan transformed urban development’s orientation from “incremental expansion” to “quality improvement”, aiming at improving the quality of life (QoL) through people-oriented urban regeneration [1,4,5]. Against this background, urban regeneration in China stands as a pivotal force driving improvements in urban configuration, components, and the QoL for urban residents [2,3,6]. Upon re-evaluating the conditions of existing residential communities [7], a socially sustainable perspective (SSP) proves indispensable for realizing high-quality urbanization and aiding in regeneration decision making [8,9]. The current urban regeneration practices are predominantly guided by top-down policy making and project-based implementations with similar spatial intervention strategies [10,11]. Unfortunately, these approaches often undervalue aspects such as public participation, social equity, and other critical factors essential for creating socially sustainable communities [12]. A socially sustainable community is characterized by creating livable, inclusive, and equitable environments that cater to all residents’ needs and uphold social justice principles [13,14]. Achieving this requires urban regeneration to be more proactive in enhancing urban quality [15,16,17].
Measuring community quality is a practical approach that significantly contributes to attaining social sustainability in urban regeneration [5]. Developing an assessment-framework-driven multidimensional quantitative model (MQM) proves indispensable for informing community regeneration policies, planning initiatives, and design decision making [18]. However, research on community quality in urban regeneration falls short of comprehensively capturing these intricate dynamics [19,20]. Simultaneously, the qualitative approach to gathering city-wide information about quality measures often poses challenges and lacks generalizability [21]. Furthermore, the absence of a coordinated exploration of quality-influence factors at the community scale hampers accurate quality measurement. The emergence and advancement of information and communication technology have yielded abundant available open and multi-sourced geospatial data, including Point of Interest (POI), area of interest (AOI), Weibo check-ins, Dianping, and other GIS-based data. This technological evolution forms the basis for advancing quantitative research and propels urban studies into an unprecedented era [22,23]. Against this backdrop, this research aims to construct a quantitative measurement model of community quality based on multi-sourced geospatial data, providing a more comprehensive and integrated assessment framework.
Quantifying community quality through integrating diverse data sources at the community level emerges as an effective strategy to explore sustainable land use, bolster land management, and enhance overall sustainability. This approach can potentially assist urban planners and policymakers in advancing socially sustainable urban development, a critical component in pursuing sustainable development goals [19,20]. By leveraging multi-sourced data such as satellite imagery, social media, and community surveys, researchers can capture and analyze various aspects of community quality, such as economic activity, social cohesion, and environmental quality. MQM-based analysis can inform policies and planning decisions prioritizing community well-being and fostering long-term sustainability [18]. The utilization of multi-sourced geospatial data for quantifying community quality catalyzes the promotion of more equitable and sustainable development practices at the community level.
To be more specific, this study focuses on the following research questions:
  • How to form an analysis framework with MQM to evaluate community quality based on the SSP?
  • How to quantitatively weigh the variables’ contribution in multi-sourced geospatial data to measure community quality and verify the MQM assessment?
  • What regeneration planning and design strategies could be implemented based on the MQM analysis results?
The structure of this paper unfolds in the following manner: First, a comprehensive assessment framework centered around the multidimensional quantitative model (MQM) for measuring community quality is introduced, accompanied by a thorough review of the pertinent literature. Secondly, this paper delineates the methods for acquiring relevant data and correlated analytical approaches. Moving forward, the third section delves into the intricacies of the community quality measurement variables, which were judiciously weighed using the Analytic Hierarchy Process (AHP). Subsequently, the quality analysis based on the MQM is introduced and substantiated through an AI-based semantic analysis applied to street view images. Finally, the paper concludes with a detailed exploration of research discussions and a comprehensive summarization of the key conclusions. The relevant contents were added and contend to differentiate between the assessment and strategy formulation stages. In Section 5.1 and Section 5.2, the illustration highlights the role and contributions of the MQM in assessing community quality. In Section 5.3, the proposed regeneration strategies are considered preliminary applications and perspectives based on the assessment results to enhance the research objectives.

2. Literature Review and Conceptual Framework

2.1. Social Sustainability and QoL

As a pivotal measure in the stock development stage, urban regeneration aims to optimize urban morphology, enhance living environments, and foster social equity. It significantly contributes to elevating community quality and improving urban residents’ QoL, thereby serving as an indispensable pathway toward achieving sustainable urban development [3,4]. Early urban regeneration initiatives were predominantly guided by physical planning ideologies, such as the “slum clearance programs” in the UK, the “reconstruction of Paris” in France, Le Corbusier’s “Radiant City”, Chicago’s “City Beautiful Movement”, and “functionalism” [20]. These initiatives perceived dynamic urban regeneration through a static lens, aiming to address urban development challenges and improve residents’ QoL through urban morphological planning. During the post-industrial era, urban regeneration transitioned from formalism towards humanism, advocating for multifunctional and incremental renewal [21]. Building upon this, scholars proposed the “housing and community development” plan, emphasizing the connection between community quality and residents’ QoL on a community-based level [23]. In this process, the collaborative participation of public and private sectors became a fundamental characteristic of urban regeneration.
In the new area, cities are more deeply understood and regarded as dynamic organic entities [24]. Urban regeneration no longer focuses solely on large-scale demolition and construction but shifts towards refined small-scale transformation strategies. This approach emphasizes human-scale improvement design, aiming to enhance the QoL for urban residents, including regenerating and optimizing tiny public spaces and old residential areas [25]. With the strengthening of social participation awareness, urban regeneration has evolved beyond mere physical space reconstruction into a comprehensive process encompassing economic structure optimization, the reshaping of social relationships, and adjustments of spatial functionality. In this process, ensuring community quality and enhancing residents’ QoL have become core concerns in urban regeneration practice.
Meanwhile, social sustainability underscores the dynamic equilibrium among the economy, environment, and society within urban areas [17,24]. It encapsulates a community’s capacity to achieve prolonged stability through interactive collaboration and cultural development while addressing the diverse needs of various groups [14,25]. At the community level, social sustainability pertains to attaining a sustainable QoL, achieved by comprehending people’s needs and fostering a sense of belonging in community quality and management [26,27]. Relevant studies have identified social equity, social participation, and basic needs as pivotal factors for assessing social sustainability at the community level [28,29,30]. However, effective quantitative evaluation indicators and methods for assessing social sustainability remain lacking, given the challenges in defining and quantifying social equity and participation [31,32].
In this research, social sustainability denotes a sustainable and positive QoL rooted in understanding community conditions and fulfilling residents’ aspirations [13,33]. The relationship between social sustainability and QoL at the community level is predicated upon three dimensions, as depicted in Figure 1: housing conditions, social engagement, and neighborhood index, and the metrics are selected as the following [5,34]:
(1)
Housing conditions: the built environment, public space, and infrastructure;
(2)
Social engagement: event organization, communication, public participation, and community activities;
(3)
Neighborhood index: satisfaction, safety, comfort, and employment.
Overall, the housing conditions primarily pertain to objective quantification within the built environment. The “built environment” refers to the objective environment within residential communities, focusing mainly on residential buildings. The four main elements of a community comprise residential buildings, public spaces, infrastructure, and land [21]. Given that the subject of this study primarily involves non-destructive renewal, public spaces, infrastructure, and the built environment are selected as measurement indicators. Additionally, satisfaction, comfort, safety, and employment will be used to assess the perception of the neighborhood environment.
Figure 1. Conceptual diagram of social sustainability and quality of life relationship.
Figure 1. Conceptual diagram of social sustainability and quality of life relationship.
Ijgi 13 00167 g001

2.2. Community Quality Measurement Metrics and Methods Based on SSP

“Urban Quality” emerges from the interactive dynamics between people and their living environments. Key determinants of urban quality encompass the built environment, economic conditions, and social capital [35,36,37]. Investigations into community quality, guided by the SSP, highlight that “social equity” encompasses factors like the built environment, infrastructure, and traffic conditions [38]. “Social participation” entails the network of relationships formed among community residents through communication activities, fostering mutual trust [39,40]. This not only enhances interactions between community residents but also influences their engagement with physical environmental facilities [41,42]. Recognizing residents’ “basic needs” as foundational is crucial for increasing quality and social sustainability [43]. Consequently, this paper proposes a framework for measuring community quality based on social equity, social participation, and basic needs.
Existing measurement methods predominantly revolve around qualitative research based on questionnaires and interviews, characterized by small sample sizes and challenges in research replication [5,44,45,46]. The advent of information and communication technology, coupled with multi-source-data processing methods, has spurred the development of multidimensional quantitative spatial analysis methods. Various urban data, such as Point of Interest (POI) data, Weibo check-ins, and Dianping data, are increasingly applied in urban research [47,48,49,50]. Empirical studies have been conducted, mainly focusing on the analysis of urban network characteristics [51], the measurement of the current status of facilities in pedestrian-scale neighborhoods [52,53,54], the identification and evaluation of urban regeneration regions [55], etc. As urban development transforms into the synergy and optimization of existing areas, advanced technologies and methods based on multi-sourced data become indispensable in urban regeneration studies [56]. Notably, it has been observed that facilities like small catering businesses can effectively enhance regional quality [57], while socio-economic perspectives benefit from POI, Weibo check-ins, and Dianping data with geographic location information in measuring community quality [58].
Verifying the multi-sourced-data evaluation model of urban quality is deemed necessary by quantifying street view images’ elements through image semantic segmentation. Since 2016, street view images have gained popularity as valuable data for studying urban visual environments [59,60]. This urban-spatial-quality analysis and evaluation method proved to be effective and precise [61,62], such as the study of the pedestrian characteristics of the urban visual environment [63], urban streets’ quality evaluation [61], perceived street safety and happiness [64,65], and so on. As a novel perspective, compared to traditional data sources, street view images enable researchers to conduct more large-scale and refined research on a new scale, effectively characterizing urban spatial visual features [66]. Concerning spatial quality evaluation, building consistency, the green canopy, and pedestrians are the major influential factors [67], which will be selected as the variables for this research.

2.3. Research Gaps

In the realm of community spatial quality assessment, critical research gaps persist. Firstly, a comprehensive analytical framework remains elusive, specifically one that integrates the MQM within the context of the SSP to systematically evaluate community quality. This research gap hinders a holistic understanding of various facets of community quality. Secondly, there is a dearth of quantitative assessment methodologies capable of accurately gauging the contribution of multi-source geospatial data variables to community quality measurement, validated through the application of the MQM. A consensus has not been reached on the profound impact of these diverse data variables on community quality. Lastly, a clear delineation of specific regeneration planning and design strategies derived from MQM analysis results is lacking. Addressing these research gaps will provide profound insights into community regeneration, offering robust guidance for practical planning and design endeavors.
Therefore, this study aims to construct a community quality measurement and evaluation system based on applying multi-source data, providing data support for optimizing sustainable urban regeneration, and verifying the measurement results by quantifying the community’s building consistency, green canopy, and pedestrian elements through streetscape images.

3. Research Data and Methods

This research constructs an MQM based on the SSP. Commencing with residents’ demands, the study meticulously organizes measurement methods and content for assessing urban community quality, specifically focusing on social equity, social participation, and basic needs. This process results in the formulation of an MQM-based community quality evaluation system derived from the SSP. The content of this evaluation system is meticulously curated through an extensive literature review. Furthermore, to enrich the evaluation process, an Application Programming Interface (API) and web crawler are utilized to gather emerging data, such as the area of interest (AOI) and Point of Interest (POI). The community’s quality is then evaluated by combining this acquired content. Building upon this foundation, machine learning techniques are applied to conduct image semantic segmentations on street view images surrounding the community. The resulting evaluation outcomes undergo rigorous verification through quantitative analysis. Subsequently, community regeneration strategies are fine-tuned in alignment with the evaluation findings. The research framework of this project, as illustrated in Figure 2, encapsulates the intricate process of integrating the SSP, MQM, and advanced technologies to holistically assess and optimize community quality.

3.1. Study Area

This research selects the Gusu district of Suzhou, Jiangsu Province, as the research case, one of China’s first pilot cities to explore urban regeneration (Figure 3). The exploration of the urban fabric of Gusu district has great reference significance for formulating urban regeneration guidance that will affect future regeneration in China. The rationale for choosing the Gusu district of Suzhou as the focus for applying the MQM is twofold. Firstly, the Gusu district features a concentration of renewal projects in older urban communities with high population densities. This area is a hub of extensive patent activities, commercial outlets, and public facilities, complemented by a vibrant social-media-user community. The geospatial and behavioral data in Gusu district provide the multidimensional data support required to analyze the MQM model. Secondly, Gusu district, serving as the core area of Suzhou, embodies a blend of profound historical and cultural depth with the typical characteristics of modern urban development. This unique combination of traditional and contemporary attributes makes the Gusu district an exemplary urban community model. The insights derived from measuring the community QoL here hold substantial reference value for similar regions nationwide. Moreover, Gusu district is China’s first and only national historical and cultural conservation district, with a lot of architectural heritage, including classical gardens, ancient buildings, and historic streets [68]. Therefore, the regeneration of the physical environment is strictly restricted by laws and regulations, making it an ideal case to explore urban regeneration based on social sustainability.

3.2. Research Data

According to the division method of residential areas identified in the “Planning and Design Standards for Urban Residential Areas (GB50180-2018)” issued by the Ministry of Housing and Urban–Rural Development of the People’s Republic of China, this study selects the “Neighborhood block”, the minor residential area, as the unit [69]. In addition, starting from the neighborhood block, the area within 300 m of it is established as the buffer zone, which serves as the boundary of our data analysis.
The data analyzed in this research mainly include two categories:
  • The first category is the AOI data within the established buffer zone. AOI data are the carriers for the analysis and expression of residential units, and the area of interest is shown in the digital map, with clear geographical boundaries [70];
  • The second category of data is the basic information and indicators. The researchers obtained the AOI data of neighborhood blocks in Gusu district, Suzhou, through the Application Programming Interface (API) provided by Gaode Map.
After the acquired data were corrected using geographic coordinates and deduplicated, 538 residential communities with geographical boundaries were obtained. According to the community quality measurement model proposed in this study, 538 residential communities were evaluated. The data were divided into four categories for analysis, namely patency (including road accessibility and public transport stations), convenience (facility coverage, facility richness, facility entertainment, and work facilities), comfort (housing price, building type, FAR, greening rate, and green area), and safety (building age, households, and road network density) (Figure 4).
Moreover, the relevant point data, including POI data and traffic station data, were obtained through API provided by Gaode Map. The POI data were specific places where people gather and conduct daily activities, which are significant for urban planners to evaluate in terms of their functionalities, vibrancy, and developments [71,72]. After screening and induction, a total of 25,489 relevant POI data were included in the research analysis. The traffic station data include bus and subway stations, and 11,190 traffic station data were included in the research and analysis. Moreover, a total of 15,241 user check-in data in 2022 were obtained through the API provided by Sina Weibo for analysis and research. Based on the public review the API interface to obtain food stores, a total of 88,475 relevant point data were included in the research and analysis after screening and induction; 7422 images from the panorama of street view images captured from Baidu street view were used for quality verification analysis (Table 1).

3.3. Research Methodology

3.3.1. Selection of Measurement Evaluation Indicators

From the SSP, the community quality evaluation system is mainly carried out from three levels: social equity, social participation, and basic needs. The impact of different levels on community quality varies. Therefore, based on the relevant literature, the measurement indicators in the evaluation system are sorted out and coded according to different measurement dimensions. Previous studies have indicated a positive correlation between the number of households and community safety. Communities with more households tend to have more comprehensive security measures, thereby increasing residents’ sense of safety [38]. Additionally, the stability of housing prices is widely regarded as an important indicator for evaluating the quality of community spaces [26,27,28]. The level and fluctuation of housing prices can reflect residents’ satisfaction with their living areas and the overall environmental quality. Furthermore, it can shed light on the combined effects of community safety, educational resources, and transportation convenience. Moreover, road network density is closely associated with both safety and accessibility. From a safety perspective, an appropriate road network density helps disperse traffic and pedestrian flow, reducing congestion and the risk of accidents and enhancing safety. From an accessibility perspective, a dense road network provides more travel route options, improving accessibility between various points within the area, effectively reducing travel time, and enhancing the convenience of commuting or daily life [69]. The specific content is as follows (Table 2):
  • Patency: indicators include road accessibility and public transport stations;
  • Convenience: facility coverage, facility richness, facility entertainment, and facility visits;
  • Comfort: housing prices, building types, FAR, green areas, and greening rate;
  • Safety: building ages, households, and road network density.
Table 2. The constructed index system for quality measurement.
Table 2. The constructed index system for quality measurement.
Primary IndicatorSecondary IndicatorsCalculation FormulaQuantitative Annotation
PatencyRoad Accessibility C 3 = N Q C 3 A n N Q C 3 A n , global integration of spatial syntax
Public Transport Station C 1 = N C 1 N C 1 , number of transportation stations within 300 m around the community
ConvenienceFacility Coverage B 2 = N p o i N p o i , number of POIs within 300 m around the community;
Facility Richness B 3 = i = 1 k n i N ln n i N i k , number of functional categories of POI points; n i , number of Class i functions; N , all POIs in the area
Facility Entertainment D 1 = N m N m , sign in points of Weibo within 300 m around the community
Work Facilities D 3 = N e u N e u , number of companies and enterprises within 300 m around the community
Facility Visits (C6) V 1 = N V 1 N V 1 , total number of visitors to facilities within 300 m
ComfortHousing Price D 2 = P a v e P a v e , community average house price
Building Type A 3 = N f N f , number of floors of the building
FAR A 5 = S b S S b , overall floorage; S , area of the community
Greening rate A 4 = S g S S g , greening area of the community; S , area of the community
Green Area B 1 = S g 1 S g 1 , greenbelt area within 300 m around the community
SafetyBuilding Age A 1 = T A 1 T A 1 , the era of community construction
Households A 2 = N A 2 N A 2 , the number of households in the community
Road network density C 2 = L r S 1 L r , total length of roads in the area; S , total area.

3.3.2. The Weight Setting of the Community Quality Evaluation System

To determine the impact weight of different influencing factors and optimize the constructed community quality measurement model more scientifically, the methods of the Analytic Hierarchy Process (AHP) [73,74] and Fuzzy Comprehensive Evaluation (FCE) [75,76] are adopted to establish a hierarchical structure model according to the updated quality measurement system. The AHP questionnaire includes the primary indicators (patency, convenience, comfort, and safety), and secondary indicators (14 different indicators) are generated. Using the AHP questionnaire, five experts with different backgrounds were invited to make subjective evaluations, and the results of the expert interviews were analyzed to determine the impact weights of different indicators. Among them, the invited experts consist of two urban planning teachers from universities, two designers from urban planning and design companies, and one staff member from the housing construction department of the Chinese government. Different interviewees included vital stakeholders, such as policymakers in urban regeneration and decision makers of regeneration schemes, which were significant in optimizing the effectiveness and science of the proposed measurement model. According to the interview results combined with the AHP analysis to determine the impact weight of different indicators (Appendix A), the final measurement model construction is shown in Figure 5 (Appendix B).

3.4. Community Quality Verification Analysis

This article proposes a Pyramid Scene Parsing Network (PSPNet) recognition of street scenes based on a pyramid pooling module that integrates global contextual information to verify quality (Figure 6). PSPNet can aggregate contextual information from different regions, thereby improving the ability to obtain global information. Experiments have shown that such a prior representation (referring to the PSPNet structure) is effective and performs excellently on multiple datasets. We validate the quality evaluation results mentioned earlier based on the number of people and vehicles identified.
A PSPNet was used to analyze the spatial semantics of the environmental image of the community in Gusu, and verified by identifying the spatial scene, including the buildings, trees, grass, chairs, lamps, boards, lanes, sky, bridges, rivers, and other elements in the image, and generate their percentages. This quality index is usually less than 1; the closer it is to 1, the higher its quality. The research established a 300 m buffer zone for the communities in Gusu district, linked and averaged the street view quality values within the buffer zone, obtained the street view quality index of the community, and ultimately divided it into five categories using the natural discontinuity method. Through this method, the community quality results could be verified by the PSPNet image analysis.
Overall, this research applies artificial intelligence to image semantic segmentation technology, focusing on urban planning. It involves the high-precision analysis of massive urban images and remote sensing data to extract the spatial distribution and structural information of various urban elements such as roads, buildings, green spaces, and water bodies. Though details of an intelligent classification process based on these elements, specific content is isolated and meets the needs of various urban studies. This enables urban planners to make more scientific and detailed decisions based on accurate geospatial data.

4. Results and Findings

4.1. The Measuring Results of Community Quality

4.1.1. Patency

The analysis of patency in this study was conducted using road accessibility and public transport station analyses. The findings revealed a significant correlation between the patency analysis results and the urban fabric in the Gusu district. As shown in Figure 7a, the road accessibility of the communities within the ancient town of Suzhou (delimited by the moat) is mainly in the range of 24.1–35.2, while the road accessibility in the communities outside the ancient town is mostly above 36.8. There are apparent spatial differences in the distribution of the imbalance in road accessibility. Moreover, only a few communities in the ancient town have a road accessibility above 36.8, primarily distributed along the core traffic roads, such as near the south gate in the southern part and the Ganjiang road that connects the eastern and western parts of Gusu district. The analysis of public transport stations revealed that the number of stations inside the ancient town is significantly lower than that outside it, consistent with the results of the road accessibility analysis (Figure 7b). In the eastern part of the study area, at the intersection of Gusu district and the Suzhou Industrial Park district, the index of traffic connection is much higher than 84, making it the highest performance of traffic connection in Gusu district.
Based on the weightings of the various indicators determined by the AHP results shown in Figure 5, the road accessibility and public transport station data were overlaid to obtain the analysis results of patency in Gusu district (Figure 7c). The analysis results show that the patency in the areas outside the Suzhou ancient town is better than that inside it, with a significant difference. From the spatial distribution of patency, the southern and eastern regions in Gusu district have higher patency than the western and northern areas.

4.1.2. Convenience

The convenience analysis in this study comprised facility coverage, richness, entertainment, and work facilities (Figure 8a–e). The findings revealed a significant correlation between the analysis results of convenience and the urban fabric in Gusu district, which is consistent with the analysis results of patency. However, the results of the convenience analysis show that the ancient town of Suzhou (delimited by the moat) is superior to the area outside the ancient town. To be more specific, the facility coverage analysis showed that most communities within the ancient town are more than 227 within a 300 m range buffer zone, while communities outside the ancient town are between 78 and 226 (Figure 8a). The facility richness gradually decreased from the center to the periphery, with only communities with a value higher than 1.44 appearing in the ancient town (Figure 8b). Moreover, the analysis results of facility entertainment showed more facilities inside the ancient town than outside, with only the southern and western regions of Gusu district having distributed facilities outside the ancient town (Figure 8c). Additionally, the analysis of work facilities showed little difference between the ancient town and the area outside it, but work facilities outside the ancient town are mainly distributed in the western and southern parts of Gusu district (Figure 8d). Fewer facilities distributed in the eastern and northern parts supported a significant imbalance in spatial distribution. Most facilities have views of less than 8000, but higher stories may reach 60,000, mainly concentrated in the center of the ancient town (Figure 8e).
The convenience analysis results of the Gusu district were obtained by superimposing the weights of the various indicators based on the AHP results on the four factors that impact convenience (Figure 8f). The analysis results showed that convenience within the ancient town of Suzhou is significantly better than that outside it, with poor convenience in the northern and southwestern areas of the Gusu district.

4.1.3. Comfort

The comfort analysis comprises housing prices, building types, FAR, the greening rate, and green areas (Figure 9). The analysis shows that the housing prices within the ancient town of Suzhou (delimited by the moat) are higher than those outside it, with the high-priced areas mainly distributed near the southern gate and Suzhou railway station in the north (Figure 9a). The analysis of building types shows that the buildings in Suzhou are mainly multi-story buildings of four–six floors, with few high-rise buildings over ten floors, distributed primarily on the outskirts of the ancient town (Figure 9b). In addition, the analysis results show that the FAR within the ancient town is generally lower than that outside it, and most are lower than 1.84. However, the FAR is higher in the western and southern areas outside the ancient town, and most residential communities are above 1.84. The distribution of FAR also affects the result of the greening rate, as shown in Figure 9c. The northern, western, and eastern areas of Suzhou have more green areas, but the distribution of the greening rate within Suzhou is more even due to the influence of FAR (Figure 9d–e).
Based on the weight of each indicator set by the AHP, the five factors affecting comfort were combined to obtain the analysis result of Gusu district (Figure 9f). The analysis results show that the distribution of comfort in Suzhou is relatively even, but the number of communities with poor comfort within the ancient town is small, and the difference in comfort is relatively tiny. However, there is a large difference in comfort among residential communities outside the ancient town, especially in the western area, where the mix of communities with the lowest and highest comfort evaluations is high. This may pose a potential risk of spatial isolation for urban residents and should be given more attention in the process of urban regeneration.

4.1.4. Safety

The safety analysis comprises building ages, households, and road network density (Figure 10). The analysis of building ages shows that residential communities in the ancient town of Suzhou (delimited by the moat) and the west and east sides of the Gusu district mainly were built before 2000, falling within the definition of old residential communities [77]. Residential communities in the north and south areas of the Gusu district were mostly built after 2005. Additionally, the analysis of households shows that residential communities in the ancient town mostly have less than 1000 households and determine an increasing trend from the inside to the outside. The analysis of road network density shows a high degree of consistency with the analysis of households in most areas.
Based on the AHP analysis of the weightings of the indicators, safety was found to have the highest weight, followed by convenience, patency, and comfort. As shown in Figure 11, the comprehensive spatial distribution of the community quality was obtained by processing the results of each indicator analyzed according to the weighting set in Figure 5. The quantified community quality was divided into five levels using the natural break classification method, with Level 1 representing the highest quality and Level 5 representing the lowest quality. The statistical results are presented in Table 3. As shown in Figure 11, the distribution of community quality in the Gusu district is significantly correlated with the urban fabric, with the ancient town of Suzhou serving as the main boundary. The community quality in the ancient town is generally low, with most communities falling into Levels 1–3. Conversely, the communities outside the ancient town present higher quality, with more communities falling into Levels 4 and 5. Additionally, the communities with the highest quality (Level 5) exhibit an aggregated distribution, primarily concentrated in the western and southwestern areas of the Gusu district. However, communities with different quality levels show mixed spatial distributions, with high-quality and low-quality communities coexisting in the same region. This situation is particularly evident in the western and southwestern areas of the district. Another notable spatial distribution characteristic of community quality is that those areas where the Gusu district borders other urban districts exhibit higher community quality. For instance, the areas where the Gusu district connects the southern and eastern regions of the Wuzhong district and the Suzhou Industrial Park demonstrate higher community quality.

4.1.5. Overall Community Quality Results

The statistical results can better demonstrate the analysis results of various indicators of community quality after categorizing it into different levels using the natural break classification method (Table 3). Based on the analysis of measurement categories, communities falling into the second, third, and fourth levels show a higher distribution frequency, with each level accounting for approximately 20–30% of the total number of communities in the study area. Specifically, the analysis of patency reveals a higher number of communities in the second and third levels, accounting for 23.4% and 26.2%, respectively. Additionally, the convenience analysis demonstrates a more even distribution of communities across all levels, with each level comprising approximately 20% of the total number of communities and the lowest level (Level 5) having the least number of communities (95 and accounting for 17.6%). The analysis of comfort reveals a higher number of communities in the third and fourth levels, accounting for 25.5% and 26.4%, respectively, while the number of communities in the first and fifth levels is relatively low, accounting for 12.7% and 15.1%, respectively. The analysis of safety reveals a higher number of communities in the fourth level, accounting for nearly 30%. In contrast, the number of communities in the first and fifth levels is relatively low, accounting for 12.7% and 15.1%, respectively. The analysis indicates relatively few communities with high quality levels in the Gusu district, with only 54 communities (10.0%) falling into the highest level. Most communities fall into the third level, with 158 (29.4%) falling into this category. The numbers of communities in the second and fourth levels are 131 (24.3%) and 158 (25.5%), respectively.

4.2. The Community Quality Verification Based on Street View Image Measurement

This study obtained 7321 street view photos of the Gusu district using the Baidu Open Map API. Based on these images, a machine learning-based semantic segmentation model was constructed to quantify the built environment surrounding the old communities, including the proportions of buildings and greenery, as well as the numbers of pedestrians and motor vehicles. By quantifying these elements of the street view photos, the quality of the communities was evaluated.
The level of community quality in the Gusu district was quantified through the analysis of the street view photos, as shown in Figure 12. A portion of the analysis process was selected and presented in the study to demonstrate the methods used to evaluate community quality based on the quantification of various elements in the street view photos.
The distribution of community quality in the Gusu district is significantly associated with the urban structure, as demonstrated in Figure 13, with the ancient town of Suzhou serving as the primary boundary. Communities within the ancient town areas generally exhibit low quality, with the majority falling into the 1–3 categories. Conversely, communities outside the ancient town exhibit higher quality, with more falling into the 4 and 5 categories. Furthermore, the highest quality communities (category 5) tend to cluster in the western and southern parts of the Gusu district, with an overall bias towards the southern region. However, communities with different quality levels exhibit a mixed spatial distribution, with high- and low-quality communities coexisting in the same area. This situation is particularly pronounced in the western and southwestern parts of the region.
Research has found that quality assessment results based on multivariate data and street view image quality assessment are consistent and differential.
(1)
The consistency is shown in the evaluation results of the central and western regions and the southern regions of the ancient town, which are marked as dashed lines in Figure 11 and Figure 13;
(2)
The differences are mainly concentrated in the northwest and north sides, belonging to the newly developing town of the Gusu district. The urban fabric, block scale, and context differ from the ancient town.
The previous literature has shown that quality verification based on image semantic analysis can accurately identify quality sites in the old urban district [61]. Therefore, in the ancient town context, the consistency between AI-based image semantic analysis and MQM measurement indicates the accuracy of the MQM’s quality measurement.
However, semantic analysis based on street view images has certain limitations in the new urban large block region. It has little effect on measuring invisible elements such as urban infrastructure and services. Therefore, an MQM based on multi-sourced geospatial data has a broader perspective and comprehensive significance.
In sum, the MQM has a greater comprehensive and integrational advantage, as the quality measurement of contemporary cities has gradually shifted from traditional observations and field studies to more comprehensive methods. For example, the comprehensive analysis of accessibility, the mixing degree, the urban form index, and other factors could assess the quality of cities more comprehensively. Among these factors, accessibility refers to the distance between individuals and important urban resources, such as the distance to public transport, commercial areas, and medical facilities. The mixing degree refers to the diversity of urban functions and uses, such as residential, commercial, office, and cultural mixing degrees. The urban form index involves the physical form and spatial organization, such as building heights, land distribution, transportation network, etc. By analyzing these factors comprehensively, the urban quality level can be more accurately evaluated. Therefore, monitoring unobservable spatial elements and people’s mobility based on the MQM is essential to reflect precise and accurate evaluation results.

5. Discussion

5.1. How to Form an Analysis Framework with the MQM to Evaluate Community Quality Based on the SSP

Based on the application of multi-sourced data and the quantitative analysis of street view images, this paper established a community quality evaluation system MQM from the SSP. Previous studies focused on measuring the relationship between urban morphology and community quality [21], such as urban form, urban function, and land use [5,44,45,46], and then used regression to measure the correlation. The MQM proposed in this study comprehensively considers the correlation factors for social sustainability, as well as the integration of multi-sourced data, which enhances the comprehensiveness of measurement methods in urban quality. It can effectively provide scientific data support for urban planning and regeneration, including various factors such as building environments, economic conditions, and social capital. Multi-sourced data are used for the quantitative analysis of community quality, which manifests comprehensive factors such as the QoL, economic development, and social interaction of residents within the community. Community quality could be measured comprehensively and accurately by integrating and analyzing multi-sourced data, such as census, social media, and POI data.
Quantifying community quality using multi-sourced data at the community level effectively explores sustainable land use and strengthens land management and sustainability. Using deep neural networks to analyze streetscape images, including buildings, pedestrians, and greenery, further enhances the evaluation of community quality under multi-sourced data measurement. This approach verifies the evaluation results, quantifies the trend of community quality changes, and predicts future levels of community quality.
It is important to note that the community quality evaluation system is complex and requires continuous improvement and adjustment according to actual situations. This can be achieved through ongoing data collection, the improvement of indicator systems, and the refinement of analytical methods. By continually refining the evaluation system with the MQM, it can become more accurate and useful, providing scientific support for urban planning and regeneration that promotes sustainable land use and management. Such an approach can enable decision-makers to prioritize community well-being, balance economic and environmental considerations, and foster long-term sustainability.

5.2. How to Quantitatively Weigh the Variables’ Contribution in Multi-Sourced Geospatial Data to Community Quality Measurement and Verify the MQM Assessment

This article uses the Analytic Hierarchy Process (AHP) and Fuzzy Comprehensive Evaluation (FCE) methods to weigh each variable’s contribution to the community quality degree and establishes a hierarchical structure model for the updated quality measurement system. The AHP questionnaire includes primary indicators (accessibility, convenience, comfort, and safety) and secondary indicators (14 different indicators). Using the AHP questionnaire, five experts with diverse backgrounds were invited for subjective evaluation, including decision-makers in the urban regeneration process. It had great significance in optimizing the effectiveness and scientific spatial measurement of the proposed MQM. The impact weights of different indicators were determined based on the interview results and AHP analysis. Then, we generated a quality index, which was usually less than 1, and the closer it was to 1, the higher the quality.
Meanwhile, this article established a 300 m buffer zone for the communities in the Gusu district, linked and averaged the street view quality values within the buffer zone, obtained the street view quality index of the community, and ultimately divided it into five categories according to the natural discontinuity method. An AI-based image segmentation technique, PSPNet, was employed to analyze the spatial semantics of the streetscape images around the Gusu community. The validation of the images involved identifying elements such as buildings, trees, grass, chairs, lights, boards, lanes, sky, bridges, rivers, etc. Existing research indicates the absence of a definitive index threshold for assessing built environment quality. However, high-quality built environments in urban streetscapes tend to exhibit specific common characteristics, including the green view ratio, sky ratio, building ratio, and pedestrian flow density.
In this way, the results of community quality can be verified through PSPNet image analysis. The analysis found that safety is considered to have the highest weight, followed by convenience, patency, and comfort. In sum, in the Gusu district, the distribution of community quality is significantly correlated with urban structure, with the ancient town of Suzhou as the main boundary. The community quality of the ancient town is generally low, and most communities belong to Levels 1–3. On the contrary, communities outside the ancient town have higher quality, with more communities belonging to Levels 4 and 5. In addition, the communities with the highest quality (Level 5) exhibit a clustered distribution, mainly concentrated in the western and southern western parts of the Gusu district.

5.3. What Regeneration Planning and Design Strategies could Be Implemented Based on the MQM Analysis Results?

The analysis found that communities with different quality levels exhibit a mixed spatial distribution, with high- and low-quality communities coexisting in the same area. This situation is particularly evident in the region’s western and southern western regions. The classification of different types of communities and their internal characteristics are consistent with the research hypothesis and have a high degree of consistency with related research.
Based on the measurement results of community quality, researchers analyzed communities of different quality levels and discovered distinct features through structured observations within different levels of communities. Among them, communities in Level 5 are mainly located in the northern area of the Gusu district, with incomplete infrastructure and a lack of maintenance for existing facilities. Communities in Level 4 are mostly old communities distributed evenly in various areas of the Gusu district. The main features are a lack of public space in the community and surrounding areas, a single facility, and residents mainly composed of relocated residents. Level 3 communities have diverse types of residents, basic infrastructure, and public space within and surrounding the community, but design and maintenance need to be improved. Communities in Level 2 have diverse populations, complete support facilities, convenient transportation, a good community environment, and strong external attraction. The highest-level communities have superior ecological environments, comprehensive public facilities, high housing prices, and strong external attraction. This aligns with the current studies; for instance, previous studies compared the quality in several Chinese cities and found that both typology and density matter for quality [21], and highly vital areas generally have the following characteristics: compact streets, diverse architectural forms, and multi-functional land uses [78]. In response to these phenomena, based on the evaluation system of social sustainability, the following strategies are proposed from the perspectives of safety, convenience, comfort, and patency to promote the improvement of urban quality.
Based on the community quality measurement results, the regeneration strategies should be closely integrated with specific community conditions, particularly in addressing identified weaknesses or areas for improvement. Several urban regeneration strategies can be proposed to improve the quality of different types of communities:
(1)
Strategies for Level 1—the highest-quality communities:
Based on the superior community environment, community-related activities should be a potential intervention strategy for the next step. For instance, community-led initiatives and events that promote social cohesion and a sense of belonging should be engaged. Diverse transportation options and a pedestrian-friendly environment should be shaped to encourage sustainable activities around the community;
(2)
Strategies for Level 2—The high-quality communities:
Improve the pedestrian infrastructure to make it safer and more convenient for walking. Upgrade and diversify the local economy to create more job opportunities and increase the community’s resilience. Enhance the design and quality of public space to create more comfortable and healthy living environments;
(3)
Strategies for Level 3—The moderate-quality communities:
Facilitate partnerships between local businesses, community groups, and government agencies to promote economic development and job creation. Implement traffic calming measures, such as speed limits and traffic circles, to reduce accidents and improve pedestrian safety. Provide financial incentives and support for property owners to improve the condition and appearance of their buildings and public spaces;
(4)
Strategies for Level 4—The low-quality communities:
Target blighted areas for public investment and redevelopment to improve the quality of the built environment and attract new investment. Support the development of small-scale, community-based businesses to create local job opportunities and foster entrepreneurship. Establish programs and services that address social and economic challenges, such as poverty, unemployment, and a lack of access to basic services. Additionally, there will be an emphasis on comprehensive considerations for overall community functionality improvement, ensuring that regeneration strategies are not limited to solving singular issues but are dedicated to creating a new urban space that is ecologically livable, resource-efficient, and socially harmonious;
(5)
Strategies for Level 5—The lowest-quality communities:
Prioritize targeted public investment to address the most pressing infrastructure and service needs, such as community parks and public transport stations, to improve infrastructure. For inadequate green spaces, specific and targeted solutions could be proposed in response to the issue, such as expanding green space construction, optimizing green space layout, and encouraging green roofs and vertical greening.
One regeneration project from the east side of the Gusu district in Suzhou was introduced here, and the community is currently undergoing adaptive transformation. According to the MQM evaluation, this community belongs to Level 2, and the regeneration strategies are consistent with government policies; the community focuses on improving its spatial quality and creating a more comfortable environment. The project renovation list is divided into two categories: basic renovation and improvement renovation, including 42 items such as exterior facade renovation, road renovation, and the improvement of convenient service facilities. Nevertheless, the regeneration of such communities should include adding more small and micro-cultural industries to increase the diversity in daily life and local culture (Figure 14).

6. Conclusions

This research introduces an evaluation system utilizing an MQM based on the SSP to assess community quality across four key dimensions: patency, convenience, comfort, and safety. The results of GIS-based quality evaluations are scrutinized and validated through AI-based street view image segmentation, thereby enhancing the accuracy of measurement outcomes. This addresses a gap in measuring urban quality at the community level on a regional scale, providing both a theoretical foundation and a practical paradigm for community quality assessment.
This study makes significant contributions to urban regeneration grounded in social sustainability, with the community as the fundamental unit of analysis. Firstly, a conceptual framework for social sustainability is established, centered around the community, linking social equity, social participation, and basic needs to the quality of life. Secondly, by reviewing various factors influencing quality of life, the study establishes connections between social sustainability and quality of life using quantifiable multi-sourced geospatial data (housing conditions, social participation, and community indicators). A quantitative measurement model, spanning 14 categories of influencing factors, is proposed. This model is composed of four dimensions: patency, convenience, comfort, and safety, and is tested using the Suzhou Gusu district as a pilot case study.
While the previous literature extensively qualitatively discusses the impact of factors included in the MQM on community quality, this study innovatively advances a methodological approach and quantitatively measures community quality. Introducing the Analytic Hierarchy Process (AHP) to assign weights to individual factors influencing community quality, with distinct weights for different influencing factors, is a notable methodological contribution. This quantitative approach is a departure from the limited quantitative measures in prior studies on community quality.
Furthermore, this study’s measurement of community quality from the SSP enables urban planners and designers to analyze urban areas’ sustainability and quality concretely. Analyzing the spatial distribution and classification of community quality measurement results offers a foundation for planners and governments to prioritize urban renewal in diverse areas, proposing targeted design interventions.
Despite the effectiveness of utilizing multi-sourced data to quantify quality at the community level, the proposed measurement model’s limitations should be acknowledged. On one hand, the model’s testing was confined to the Gusu district, and broader applicability needs validation in more extensive and complex environments in future studies. On the other hand, the model relies on data, such as Weibo check-ins, POI data, and housing price information, collected quarterly or yearly. This temporal limitation hinders the real-time assessment of changes in community quality, posing challenges for meeting operational needs during urban regeneration processes. Additionally, this research acknowledges inherent challenges with the datasets used, such as delays in updates or incomplete coverage in Areas of Interest (AOI) and POI data. Social media data like Weibo Check-in data and reviews from platforms like Dianping might suffer from uneven user participation and sample biases. Additionally, the availability and completeness of government data can be constrained by issues related to public accessibility and timeliness. Despite these challenges, our study centers on “community” and employs multidimensional data to enhance the model and its application on a larger scale. However, the inherent inaccuracies in the data still pose limitations. Future studies could continue to refine the model and address these data issues in subsequent phases of the research, aiming to optimize its accuracy and practical utility.
In conclusion, considerable potential exists for expanding the measurement of community quality based on multi-sourced geospatial data. Future research can explore the introduction of geographic tagging data to delve deeper into community quality and adapt to the rapidly evolving dynamics of communities. Furthermore, the next phase of our research will establish a dynamic assessment mechanism that allows for the real-time monitoring of community development and adjustments to governance models, investigating whether key indicators such as safety, comfort, convenience and accessibility exhibit significant correlations. This approach can be expanded to various urban levels, enhancing adaptability across different scales of city management. Simultaneously, the research methods could be diversified to enhance residents’ well-being and health by integrating data collected from various sensors, such as temperature, humidity, air quality, noise, and organic pollutants in the built environment. Integrated environmental data will provide a more comprehensive foundation for decision making to improve the quality of urban life. Despite these limitations, leveraging diverse data sources to quantify community quality remains a valuable tool for promoting sustainable land use and management, supporting urban planning and policymaking, and ultimately enhancing the well-being of local communities.

Author Contributions

Conceptualization, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan and Ning Liu; Data curation, Jinliu Chen, Pengcheng Li and Haoqi Wang; Formal analysis, Jinliu Chen, Xiaoxin Zhao and Ning Liu; Funding acquisition, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan and Ning Liu; Investigation, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan, Haoqi Wang and Di Yang; Methodology, Jinliu Chen, Pengcheng Li, Wenquan Gan, Haoqi Wang and Di Yang; Project administration, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan and Ning Liu; Resources, Jinliu Chen and Xiaoxin Zhao; Software, Jinliu Chen, Pengcheng Li and Haoqi Wang; Supervision, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan and Ning Liu; Validation, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan, Haoqi Wang and Di Yang; Visualization, Jinliu Chen, Pengcheng Li, Wenquan Gan and Haoqi Wang; Writing—original draft, Jinliu Chen, Wenquan Gan, Pengcheng Li and Haoqi Wang; Writing—review and editing, Jinliu Chen, Xiaoxin Zhao, Wenquan Gan and Ning Liu. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by [Youth Program of National Natural Science Foundation of China], grant number [52208062]. [Advance Research Program of National Level Projects in Suzhou City University], grant number [2023SGY009]; [National Social Science Foundation of China], grant number [22BH148]; [General Projects of Philosophy and Social Science Research at Colleges and Universities in Jiangsu Province], grant number [2022SJYB0006]; [Key Laboratory of Spatial Intelligent Planning Technology, Ministry of Natural Resources, China], grant number [20230303]; and [Natural Science Foundation of Fujian Province, China], grant number [2022J05193].

Data Availability Statement

The data that support the findings of this study are available from the author, Jinliu Chen, upon reasonable request.

Conflicts of Interest

The authors declare no conflicts of interest.

Appendix A

Appendix A.1. Expert 1

BACD C1C2C3C4C5 B1B2B3B4B5 D1D2D3
B 221/4C1 3435B1 1/21/221/3D1 1/21/3
A 21/3C2 1/21/41/2B2 233D2 1
C 1/3C3 1/23B3 11/2D3 A2A1
D C4 4B4 1/3 A2 1/3
C5 B5 A1

Appendix A.2. Expert 2

BACD C1C2C3C4C5 B1B2B3B4B5 D1D2D3
B 221/4C1 21/225B1 221/22D1 1/21/3
A 21/3C2 1/21/21/2B2 21/31/2D2 1
C 1/3C3 13B3 1/21/2D3 A2A1
D C4 2B4 1/2 A2 1/2
C5 B5 A1

Appendix A.3. Expert 3

BACD C1C2C3C4C5 B1B2B3B4B5 D1D2D3
B 1/21/21/2C1 3224B1 1/31/333D1 1/31/2
A 21/2C2 1/31/21/3B2 232D2 3
C 1/4C3 1/23B3 32D3 A2A1
D C4 3B4 2 A2 1/3
C5 B5 A1

Appendix A.4. Expert 4

BACD C1C2C3C4C5 B1B2B3B4B5 D1D2D3
B 231/2C1 3232B1 1/31/231/2D1 1/21/3
A 1/31/3C2 1/31/31/3B2 562D2 1/2
C 1/4C3 23B3 31/2D3 A2A1
D C4 3B4 1/2 A2 1/3
C5 B5 A1

Appendix A.5. Expert 5

BACD C1C2C3C4C5 B1B2B3B4B5 D1D2D3
B 241/2C1 3225B1 1/21/231/4D1 1/21/2
A 11/2C2 1/21/31/2B2 351/2D2 2
C 1/3C3 1/33B3 21/2D3 A2A1
D C4 4B4 1/2 A2 1/3
C5 B5 A1
Note: patency (A), road accessibility (A1), public transport station (A2); convenience (B), facility coverage (B1), facility richness (B2), facility entertainment (B3), work facilities (B4), facilities visits (B5); comfort (C), housing price (C1), building type (C2), FAR (C3), greening rate (C4), green area (C5); safety (D), building age (D1), households (D2), road network density (D3).

Appendix B

Appendix B.1. Community Quality, Consistency Ratio: 0.0687; Weight of ‘Decision Objectives’: 1.0000; λ Max: 4.1833

QualityConveniencePatencyComfortSafetyWi
Convenience1.00002.00002.00000.25000.2106
Patency0.50001.00002.00000.33330.1580
Comfort0.50000.50001.00000.33330.1123
Safety4.00003.00003.00001.00000.5192

Appendix B.2. Convenience Consistency Ratio: 0.0639; Weight of ‘Decision Objectives’: 0.2106; λ Max: 4.1707

ConvenienceFacility CoverageFacility RichnessFacility EntertainmentWork FacilitiesFacilities VisitsWi
Facility Coverage1.00000.50000.50002.00000.33330.1251
Facility Richness2.00001.00002.00003.00003.00000.3714
Facility Entertainment2.00000.50001.00001.00000.50000.1525
Work Facilities0.50000.33331.00001.00000.33330.0977
Facilities Visits3.00000.33332.00003.00001.00000.2533

Appendix B.3. Consistency Ratio: 0.0000; Weight of ‘Decision Objectives’: 0.1580; λ Max: 2.0000

PatencyPublic Transport StationRoad AccessibilityWi
Public Transport Station1.00000.33330.2500
Road Accessibility3.00001.00000.7500

Appendix B.4. Comfort Consistency Ratio: 0.0729; Weight of ‘Decision Objectives’: 0.1123; λ Max: 5.3268

ComfortHousing PriceBuilding TypeFARGreening RateGreen AreaWi
Housing Price1.00003.00004.00003.00005.00000.4515
Building Type0.33331.00000.50000.25000.50000.0752
FAR0.25002.00001.00000.50003.00000.1456
Greening Rate0.33334.00002.00001.00004.00000.2466
Green Area0.20002.00000.33330.25001.00000.0811

Appendix B.5. Safety Consistency Ratio: 0.0176; Weight of ‘Decision Objectives’: 0.5192; λ Max: 3.0183

SafetyBuilding AgeHouseholdsRoad Network DensityWi
Building Age1.00000.50000.33330.1692
Households2.00001.00001.00000.3874
Road Network Density3.00001.00001.00000.4434

References

  1. The State Council. The 14th Five Year Plan. Available online: http://www.gov.cn/xinwen/2021-03/13/content_5592681.htm (accessed on 1 December 2023).
  2. The State Council. Urban Regeneration Makes People’s Lives Better. Available online: http://www.gov.cn/xinwen/2021-03/08/content_5591359.htm (accessed on 1 December 2023).
  3. The State Council. Wang Menghui: Implementing Urban Renewal Action. Available online: http://www.gov.cn/xinwen/2020-12/29/content_5574417.htm (accessed on 1 December 2023).
  4. Wang, X.-R.; Hui, E.C.-M.; Choguill, C.; Jia, S.-H. The new urbanization policy in China: Which way forward? Habitat Int. 2015, 47, 279–284. [Google Scholar] [CrossRef]
  5. Chen, J.; Pellegrini, P.; Wang, H. Comparative residents’ satisfaction evaluation for socially sustainable regeneration—The case of two high-density communities in Suzhou. Land 2022, 11, 1483. [Google Scholar] [CrossRef]
  6. Awad, J.; Jung, C. Extracting the planning elements for sustainable urban regeneration in Dubai with AHP (analytic hierarchy process). Sustain. Cities Soc. 2022, 76, 103496. [Google Scholar] [CrossRef]
  7. Pocock, J.; Steckler, C.; Hanzalova, B. Improving socially sustainable design and construction in developing countries. Procedia Eng. 2016, 145, 288–295. [Google Scholar] [CrossRef]
  8. Li, S.; Fu, M.; Tian, Y.; Xiong, Y.; Wei, C. Relationship between urban land use efficiency and economic development level in the Beijing–Tianjin–Hebei region. Land 2022, 11, 976. [Google Scholar] [CrossRef]
  9. Rao, Y.; Zhang, J.; Xu, Q.; Wang, S. Sustainability assessment of road networks: A new perspective based on service ability and landscape connectivity. Sustain. Cities Soc. 2018, 40, 471–483. [Google Scholar] [CrossRef]
  10. Hu, J.; Chen, J.; Li, P.; Yan, J.; Wang, H. Systematic Review of Socially Sustainable and Community Regeneration: Research Traits, Focal Points, and Future Trajectories. Buildings 2024, 14, 881. [Google Scholar] [CrossRef]
  11. Liu, X. Discussion on Refined Planning Strategy of Community Public Service Facilities from the Perspective of Mixed Use. Urban Dev. Stud. 2021, 28, 31–37. [Google Scholar] [CrossRef]
  12. Pacione, M. Urban environmental quality and human wellbeing—A social geographical perspective. Landsc. Urban Plan. 2003, 65, 19–30. [Google Scholar] [CrossRef]
  13. Bramley, G.; Dempsey, N.; Power, S.; Brown, C.; Watkins, D. Social sustainability and urban form: Evidence from five British cities. Environ. Plan. A 2009, 41, 2125–2142. [Google Scholar] [CrossRef]
  14. Dempsey, N.; Bramley, G.; Power, S.; Brown, C. The social dimension of sustainable development: Defining urban social sustainability. Sustain. Dev. 2011, 19, 289–300. [Google Scholar] [CrossRef]
  15. Besleme, K.; Mullin, M. Community indicators and healthy communities. Natl. Civ. Rev. 1997, 86, 43–53. [Google Scholar] [CrossRef]
  16. Yang, Y.-R.; Chang, C.-H. An urban regeneration regime in China: A case study of urban redevelopment in Shanghai’s Taipingqiao area. Urban Stud. 2007, 44, 1809–1826. [Google Scholar] [CrossRef]
  17. Zhai, B.; Ng, M.K. Urban regeneration and social capital in China: A case study of the Drum Tower Muslim District in Xi’an. Cities 2013, 35, 14–25. [Google Scholar] [CrossRef]
  18. Custance, J.; Hillier, H. Statistical issues in developing indicators of sustainable development. J. R. Stat. Soc. Ser. A (Stat. Soc.) 1998, 161, 281–290. [Google Scholar] [CrossRef]
  19. Yuan, Q.; Qian, T.; Guo, Y. Reconstructing Social Capital to Promote Urban Renewal: A Case Study of Lianjiao Area, Nanhai. Urban Plan. Rev. 2015, 39, 64–73. [Google Scholar] [CrossRef]
  20. Huang, J.; Cui, Y.; Chang, H.; Obracht-Prondzyńska, H.; Kamrowska-Zaluska, D.; Li, L. A City Is Not a Tree: A Multi-City Study on Street Network and Urban Life. Landsc Urban Plan 2022, 226. [Google Scholar] [CrossRef]
  21. Ye, Y.; Li, D.; Liu, X. How block density and typology affect urban vitality: An exploratory analysis in Shenzhen, China. Urban Geogr. 2018, 39, 631–652. [Google Scholar] [CrossRef]
  22. Wang, Y.; Zou, Q.; Li, G. Public Space Construction of Urban Resettlement Community Based on Analysis of Vitality Characteristics: Taking the 6 Resettlement Communities of Suzhou as Examples. Sci. Geogr. Sin. 2018, 38, 747–754. [Google Scholar] [CrossRef]
  23. Paköz, M.Z.; Yaratgan, D.; Şahin, A. Re-mapping urban vitality through Jane Jacobs’ criteria: The case of Kayseri, Turkey. Land Use Policy 2022, 114, 105985. [Google Scholar] [CrossRef]
  24. Chen, J.; Pellegrini, P.; Yang, Z.; Wang, H. Strategies for Sustainable Urban Renewal: Community-Scale GIS-Based Analysis for Densification Decision Making. Sustainability 2023, 15, 7901. [Google Scholar] [CrossRef]
  25. Eizenberg, E.; Jabareen, Y. Social sustainability: A new conceptual framework. Sustainability 2017, 9, 68. [Google Scholar] [CrossRef]
  26. Felce, D.; Perry, J. Quality of life: Its definition and measurement. Res. Dev. Disabil. 1995, 16, 51–74. [Google Scholar] [CrossRef] [PubMed]
  27. Hunt, S. The problem of quality of life. Qual. Life Res. 1997, 6, 205–212. [Google Scholar] [PubMed]
  28. Zakus, J.D.L.; Lysack, C.L. Revisiting community participation. Health Policy Plan. 1998, 13, 1–12. [Google Scholar] [CrossRef] [PubMed]
  29. Nieusma, D.; Riley, D. Designs on development: Engineering, globalization, and social justice. Eng. Stud. 2010, 2, 29–59. [Google Scholar] [CrossRef]
  30. Zhao, M.; Liu, N.; Chen, J.; Wang, D.; Li, P.; Yang, D.; Zhou, P. Navigating Post-COVID-19 Social–Spatial Inequity: Unravelling the Nexus between Community Conditions, Social Perception, and Spatial Differentiation. Land 2024, 13, 563. [Google Scholar] [CrossRef]
  31. Shigetomi, Y.; Chapman, A.; Nansai, K.; Matsumoto, K.i.; Tohno, S. Quantifying lifestyle based social equity implications for national sustainable development policy. Environ. Res. Lett. 2020, 15, 084044. [Google Scholar] [CrossRef]
  32. Verba, S.; Nie, N.H. Participation in America: Political Democracy and Social Equality; University of Chicago Press: Chicago, IL, USA, 1987. [Google Scholar]
  33. Forrest, R.; Kearns, A. Social cohesion, social capital and the neighbourhood. Urban Stud. 2001, 38, 2125–2143. [Google Scholar] [CrossRef]
  34. Han, L.; Shi, L.; Yang, F.; Xiang, X.; Gao, L. Method for the evaluation of residents’ perceptions of their community based on landsenses ecology. J. Clean. Prod. 2021, 281, 124048. [Google Scholar] [CrossRef]
  35. Lu, S.; Shi, C.; Yang, X. Impacts of built environment on urban vitality: Regression analyses of Beijing and Chengdu, China. Int. J. Environ. Res. Public Health 2019, 16, 4592. [Google Scholar] [CrossRef] [PubMed]
  36. Araya, R.; Dunstan, F.; Playle, R.; Thomas, H.; Palmer, S.; Lewis, G. Perceptions of social capital and the built environment and mental health. Soc. Sci. Med. 2006, 62, 3072–3083. [Google Scholar] [CrossRef] [PubMed]
  37. Liu, S.; Zhang, L.; Long, Y.; Long, Y.; Xu, M. A new urban vitality analysis and evaluation framework based on human activity modeling using multi-source big data. ISPRS Int. J. Geo-Inf. 2020, 9, 617. [Google Scholar] [CrossRef]
  38. Zimmerman, R. Social Equity and Environmental Risk 1. Risk Anal. 1993, 13, 649–666. [Google Scholar] [CrossRef]
  39. Piškur, B.; Daniëls, R.; Jongmans, M.J.; Ketelaar, M.; Smeets, R.J.; Norton, M.; Beurskens, A.J. Participation and social participation: Are they distinct concepts? Clin. Rehabil. 2014, 28, 211–220. [Google Scholar] [CrossRef] [PubMed]
  40. Phillips, D.L. Social participation and happiness. Am. J. Sociol. 1967, 72, 479–488. [Google Scholar] [CrossRef] [PubMed]
  41. Hsu, H.-C. Does social participation by the elderly reduce mortality and cognitive impairment? Aging Ment. Health 2007, 11, 699–707. [Google Scholar] [CrossRef]
  42. Dahan-Oliel, N.; Gelinas, I.; Mazer, B. Social participation in the elderly: What does the literature tell us? Crit. Rev. Phys. Rehabil. Med. 2008, 20, 159–176. [Google Scholar] [CrossRef]
  43. Chen, J.; Wang, H.; Yang, Z.; Li, P.; Ma, G.; Zhao, X. Comparative Spatial Vitality Evaluation of Traditional Settlements Based on SUF: Taking Anren Ancient Town’s Urban Design as an Example. Sustainability 2023, 15, 8178. [Google Scholar] [CrossRef]
  44. Williamson, C. Questionnaires, individual interviews and focus groups. In Research Methods: Information, Systems, and Contexts; Tilde University Press: Victoria, Australia, 2013; pp. 349–372. [Google Scholar]
  45. Richman, W.L.; Kiesler, S.; Weisband, S.; Drasgow, F. A meta-analytic study of social desirability distortion in computer-administered questionnaires, traditional questionnaires, and interviews. J. Appl. Psychol. 1999, 84, 754. [Google Scholar] [CrossRef]
  46. Chen, J.; Pellegrini, P.; Xu, Y.; Ma, G.; Wang, H.; An, Y.; Shi, Y.; Feng, X. Evaluating residents’ satisfaction before and after regeneration. The case of a high-density resettlement neighbourhood in Suzhou, China. Cogent Soc. Sci. 2022, 8, 2144137. [Google Scholar] [CrossRef]
  47. Zhang, L.; Ye, Y.; Zeng, W.; Chiaradia, A. A systematic measurement of street quality through multi-sourced urban data: A human-oriented analysis. Int. J. Environ. Res. Public Health 2019, 16, 1782. [Google Scholar] [CrossRef] [PubMed]
  48. Huang, J.; Obracht-Prondzynska, H.; Kamrowska-Zaluska, D.; Sun, Y.; Li, L. The image of the City on social media: A comparative study using “Big Data” and “Small Data” methods in the Tri-City Region in Poland. Landsc. Urban Plan. 2021, 206, 103977. [Google Scholar] [CrossRef]
  49. Huang, J.; Hao, T.; Wang, Y.; Jones, P. A Street-Scale Simulation Model for the Cooling Performance of Urban Greenery: Evidence from a High-Density City. Sustain Cities Soc. 2022, 82, 103908. [Google Scholar] [CrossRef]
  50. Chang, H.; Huang, J.; Yao, W.; Zhao, W.; Li, L. How Do New Transit Stations Affect People’s Sentiment and Activity? A Case Study Based on Social Media Data in Hong Kong. Transp Policy 2022, 120, 139–155. [Google Scholar] [CrossRef]
  51. Sun, G.; Wallace, D.; Webster, C. Unravelling the impact of street network structure and gated community layout in development-oriented transit design. Land Use Policy 2020, 90, 104328. [Google Scholar] [CrossRef]
  52. Zhao, J.; Sun, G.; Webster, C. Walkability scoring: Why and how does a three-dimensional pedestrian network matter? Environ. Plan. B Urban Anal. City Sci. 2021, 48, 2418–2435. [Google Scholar] [CrossRef]
  53. Pan, L.; Gan, W.; Chen, J.; Ren, K. An Integrated Model for Constructing Urban Ecological Networks and Identifying the Ecological Protection Priority: A Case Study of Wujiang District, Suzhou. Sustainability 2023, 15, 4487. [Google Scholar] [CrossRef]
  54. Chen, J.; Tian, W.; Xu, K.; Pellegrini, P. Testing Small-Scale Vitality Measurement Based on 5D Model Assessment with Multi-Source Data: A Resettlement Community Case in Suzhou. ISPRS Int. J. Geo-Inf. 2022, 11, 626. [Google Scholar] [CrossRef]
  55. Bryson, J.R.; Andres, L.; Mulhall, R. A Research Agenda for Regeneration Economies: Reading City-Regions; Edward Elgar Publishing: Northampton, MA, USA, 2018. [Google Scholar]
  56. Guo, M.; Lin, Y.; Shyu, R.-J.; Huang, J. Characterizing Environmental Pollution with Civil Complaints and Social Media Data: A Case of the Greater Taipei Area. J. Environ. Manag. 2023, 348, 119310. [Google Scholar] [CrossRef]
  57. Jiang, Y.; Han, Y.; Liu, M.; Ye, Y. Street vitality and built environment features: A data-informed approach from fourteen Chinese cities. Sustain. Cities Soc. 2022, 79, 103724. [Google Scholar] [CrossRef]
  58. Long, Y.; Huang, C. Does block size matter? The impact of urban design on economic vitality for Chinese cities. Environ. Plan. B Urban Anal. City Sci. 2019, 46, 406–422. [Google Scholar] [CrossRef]
  59. Tong, M.; She, J.; Tan, J.; Li, M.; Ge, R.; Gao, Y. Evaluating Street Greenery by Multiple Indicators Using Street-Level Imagery and Satellite Images: A Case Study in Nanjing, China. Forests 2020, 11, 1347. [Google Scholar] [CrossRef]
  60. Zhang, F.; Zu, J.; Hu, M.; Zhu, D.; Kang, Y.; Gao, S.; Zhang, Y.; Huang, Z. Uncovering inconspicuous places using social media check-ins and street view images. Comput. Environ. Urban Syst. 2020, 81, 101478. [Google Scholar] [CrossRef]
  61. Wang, M.; Vermeulen, F. Life between buildings from a street view image: What do big data analytics reveal about neighbourhood organisational vitality? Urban Stud. 2021, 58, 3118–3139. [Google Scholar] [CrossRef]
  62. Wu, C.; Ye, Y.; Gao, F.; Ye, X. Using street view images to examine the association between human perceptions of locale and urban vitality in Shenzhen, China. Sustain. Cities Soc. 2023, 88, 104291. [Google Scholar] [CrossRef]
  63. Rundle, A.G.; Bader, M.D.; Richards, C.A.; Neckerman, K.M.; Teitler, J.O. Using Google Street View to audit neighborhood environments. Am. J. Prev. Med. 2011, 40, 94–100. [Google Scholar] [CrossRef] [PubMed]
  64. Wang, R.; Yuan, Y.; Liu, Y.; Zhang, J.; Liu, P.; Lu, Y.; Yao, Y. Using street view data and machine learning to assess how perception of neighborhood safety influences urban residents’ mental health. Health Place 2019, 59, 102186. [Google Scholar] [CrossRef] [PubMed]
  65. Pringle, S.; Guaralda, M. Images of Urban Happiness: A Pilot Study in the Self-representation of Happiness in Urban Spaces. Int. J. Image 2017, 8, 97. [Google Scholar] [CrossRef]
  66. Hao, T.; Chang, H.; Liang, S.; Jones, P.; Chan, P.W.; Li, L.; Huang, J. Heat and Park Attendance: Evidence from “Small Data” and “Big Data” in Hong Kong. Build. Environ. 2023, 234, 110123. [Google Scholar] [CrossRef]
  67. Yang, F.; Qian, F.; Lau, S.S. Urban form and density as indicators for summertime outdoor ventilation potential: A case study on high-rise housing in Shanghai. Build. Environ. 2013, 70, 122–137. [Google Scholar] [CrossRef]
  68. Yu, Z. Impllementation optimization strategy for Suzhou Old Town protection and regeneration: From a perspective of government’s behavior and role. Coity Plan. Rev. 2022, 46, 13–20. [Google Scholar]
  69. Huang, J.; Cui, Y.; Li, L.; Guo, M.; Ho, H.C.; Lu, Y.; Webster, C. Re-examining Jane Jacobs’ doctrine using new urban data in Hong Kong. Environ. Plan. B Urban Anal. City Sci. 2023, 50, 76–93. [Google Scholar] [CrossRef]
  70. Hu, Y.; Gao, S.; Janowicz, K.; Yu, B.; Li, W.; Prasad, S. Extracting and understanding urban areas of interest using geotagged photos. Comput. Environ. Urban Syst. 2015, 54, 240–254. [Google Scholar] [CrossRef]
  71. Hao, T.; Zhao, Q.; Huang, J. Optimization of Tree Locations to Reduce Human Heat Stress in an Urban Park. Urban For. Urban Green. 2023, 86, 128017. [Google Scholar] [CrossRef]
  72. Yue, Y.; Zhuang, Y.; Yeh, A.G.; Xie, J.-Y.; Ma, C.-L.; Li, Q.-Q. Measurements of POI-based mixed use and their relationships with neighbourhood vibrancy. Int. J. Geogr. Inf. Sci. 2017, 31, 658–675. [Google Scholar] [CrossRef]
  73. Vaidya, O.S.; Kumar, S. Analytic hierarchy process: An overview of applications. Eur. J. Oper. Res. 2006, 169, 1–29. [Google Scholar] [CrossRef]
  74. Saaty, R.W. The analytic hierarchy process—What it is and how it is used. Math. Model. 1987, 9, 161–176. [Google Scholar] [CrossRef]
  75. Feng, S.; Xu, L.D. Decision support for fuzzy comprehensive evaluation of urban development. Fuzzy Sets Syst. 1999, 105, 1–12. [Google Scholar] [CrossRef]
  76. Wu, X.; Hu, F. Analysis of ecological carrying capacity using a fuzzy comprehensive evaluation method. Ecol. Indic. 2020, 113, 106243. [Google Scholar] [CrossRef]
  77. Li, X.; Zhang, T. Place identity and older residents’ coping strategies while ageing in declining neighbourhoods of urban China. J. Environ. Psychol. 2021, 78, 101692. [Google Scholar] [CrossRef]
  78. Zhang, A.; Li, W.; Wu, J.; Lin, J.; Chu, J.; Xia, C. How can the urban landscape affect urban vitality at the street block level? A case study of 15 metropolises in China. Environ. Plan. B Urban Anal. City Sci. 2021, 48, 1245–1262. [Google Scholar] [CrossRef]
Figure 2. Research framework with multidimensional quantitative model and image semantic verification.
Figure 2. Research framework with multidimensional quantitative model and image semantic verification.
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Figure 3. The location of the study area—Gusu district in Suzhou, China.
Figure 3. The location of the study area—Gusu district in Suzhou, China.
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Figure 4. Urban quality MQM with detailed categories and variables based on the social sustainability perspective.
Figure 4. Urban quality MQM with detailed categories and variables based on the social sustainability perspective.
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Figure 5. The indicator weight setting results with the AHP.
Figure 5. The indicator weight setting results with the AHP.
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Figure 6. AI-based image semantic with PSPNet analysis process.
Figure 6. AI-based image semantic with PSPNet analysis process.
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Figure 7. The spatial analysis results of multiple indicators of patency: (a) road accessibility; (b) public transport station; and (c) overall analysis results of patency.
Figure 7. The spatial analysis results of multiple indicators of patency: (a) road accessibility; (b) public transport station; and (c) overall analysis results of patency.
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Figure 8. The spatial analysis results of multiple indicators of convenience: (a) facility coverage; (b) facility richness; (c) facility entrainment; (d) work facilities; (e) road density; and (f) overall analysis results of convenience.
Figure 8. The spatial analysis results of multiple indicators of convenience: (a) facility coverage; (b) facility richness; (c) facility entrainment; (d) work facilities; (e) road density; and (f) overall analysis results of convenience.
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Figure 9. The spatial analysis results of multiple indicators of comfort; (a) housing price; (b) building type; (c) FAR; (d) greening rate; (e) green area; and (f) overall analysis results of comfort.
Figure 9. The spatial analysis results of multiple indicators of comfort; (a) housing price; (b) building type; (c) FAR; (d) greening rate; (e) green area; and (f) overall analysis results of comfort.
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Figure 10. The spatial analysis results of multiple indicators of safety: (a) building age; (b) households; (c) road network density; and (d) overall analysis results of safety.
Figure 10. The spatial analysis results of multiple indicators of safety: (a) building age; (b) households; (c) road network density; and (d) overall analysis results of safety.
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Figure 11. The measuring results of the community quality of the Gusu district are based on the MQM analysis (the ellipse represents areas in the Gusu district with higher community quality).
Figure 11. The measuring results of the community quality of the Gusu district are based on the MQM analysis (the ellipse represents areas in the Gusu district with higher community quality).
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Figure 12. Vector analysis of street view images.
Figure 12. Vector analysis of street view images.
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Figure 13. The results of community quality of the Gusu district via AI-based street view image semantic analysis (the ellipse represents areas in the Gusu district with higher community quality).
Figure 13. The results of community quality of the Gusu district via AI-based street view image semantic analysis (the ellipse represents areas in the Gusu district with higher community quality).
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Figure 14. A regeneration project sample in the Gusu district, source: https://www.suzhou.gov.cn (accessed on 18 January 2024).
Figure 14. A regeneration project sample in the Gusu district, source: https://www.suzhou.gov.cn (accessed on 18 January 2024).
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Table 1. A detailed description of the data sources used in this research.
Table 1. A detailed description of the data sources used in this research.
ItemSourceQuantity
Basic informationAnjuke website in Suzhou. Accessed from https://suzhou.anjuke.com/sale, accessed on 24 August 2022538 basic community messages
AOI and POI data of Gusu communityThe data acquisition source is Gaode Map, accessed from https://lbs.amap.com/, accessed on 24 August 202236,679 points, 236 areas
Weibo check-in dataAccessed from https://weibo.com/, accessed on 24 August 202215,241 points
Road dataAccessed from http://www.openstreetmap.org/, accessed on 24 August 2022-
Dazhong Dianping dataAccessed from https://www.dianping.com/suzhou/, accessed on 24 August 202288,475 points
Baidu street view dataAccessed from https://map.baidu.com/, accessed on 24 August 20227422 images
Table 3. The statistics of community quality measuring results.
Table 3. The statistics of community quality measuring results.
Dimensions
Category
PatencyConvenienceComfortSafetyCommunity Quality
NumberPercentageNumberPercentageNumberPercentageNumberPercentageNumberPercentage
Level 5 (low)7413.8%9517.6%8115.1%6912.7%5810.8%
Level 410319.1%11020.4%13725.5%15128.1%13725.5%
Level 314126.2%11621.6%14226.4%12423.1%15829.4%
Level 212623.4%10820.1%11821.9%11321.0%13124.3%
Level 1 (high)9417.5%10920.3%6011.1%8115.1%5410.0%
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Chen, J.; Gan, W.; Liu, N.; Li, P.; Wang, H.; Zhao, X.; Yang, D. Community Quality Evaluation for Socially Sustainable Regeneration: A Study Using Multi-Sourced Geospatial Data and AI-Based Image Semantic Segmentation. ISPRS Int. J. Geo-Inf. 2024, 13, 167. https://doi.org/10.3390/ijgi13050167

AMA Style

Chen J, Gan W, Liu N, Li P, Wang H, Zhao X, Yang D. Community Quality Evaluation for Socially Sustainable Regeneration: A Study Using Multi-Sourced Geospatial Data and AI-Based Image Semantic Segmentation. ISPRS International Journal of Geo-Information. 2024; 13(5):167. https://doi.org/10.3390/ijgi13050167

Chicago/Turabian Style

Chen, Jinliu, Wenquan Gan, Ning Liu, Pengcheng Li, Haoqi Wang, Xiaoxin Zhao, and Di Yang. 2024. "Community Quality Evaluation for Socially Sustainable Regeneration: A Study Using Multi-Sourced Geospatial Data and AI-Based Image Semantic Segmentation" ISPRS International Journal of Geo-Information 13, no. 5: 167. https://doi.org/10.3390/ijgi13050167

APA Style

Chen, J., Gan, W., Liu, N., Li, P., Wang, H., Zhao, X., & Yang, D. (2024). Community Quality Evaluation for Socially Sustainable Regeneration: A Study Using Multi-Sourced Geospatial Data and AI-Based Image Semantic Segmentation. ISPRS International Journal of Geo-Information, 13(5), 167. https://doi.org/10.3390/ijgi13050167

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