Urban Park Mobility Analysis
Aimed at analyzing park accessibility via pedestrian and cycling routes in NYC, Boston and Washington DC
Introduction
Literature Review
Parks and green spaces are highly valued urban destinations, enhancing the quality of life for city residents (El Murr, Boisjoly, & Waygood, 2023). These spaces contribute significantly to well-being (El Murr, Boisjoly, & Waygood, 2023), environmental health (Haase et al., 2014), social cohesion (Peters, Elands, & Buijs, 2010), and economic prosperity (Hoshino & Kuriyama, 2010). Consequently, accessibility to parks and green spaces is considered a crucial component of life quality (Cracu, Schvab, Prefac, Popescu, & Sîrodoev, 2024).
Ensuring equitable access to these areas is essential for fostering inclusive urban environments. By prioritizing accessibility, urban planners can ensure that all residents, regardless of their socio-economic status or background, benefit from the physical and mental health advantages provided by green spaces. This focus supports a more sustainable and livable urban environment, contributing to overall urban resilience and community well-being.
However, the accessibility of urban greenspaces is an increasing concern (Comber, Brunsdon, & Green, 2008). Addressing such disparities is crucial for achieving equitable urban development.
Park Area Filter
International literature (Comber, Brunsdon, & Green, 2008) identifies a 2-hectare minimum for urban park areas. Sadeghian and Vardanyan (2015) categorize urban parks into three types, setting specific area and distance standards for each, notably city parks and community parks with a 2-hectare minimum and a 2.4 km maximum from residential areas. Romanian law classifies parks as "public green spaces with unlimited access" and requires a minimum of 1 hectare, incorporating both natural and built environments to facilitate cultural, educational, and recreational activities. In this project, hexagon grids measuring 900 by 900 square feet are utilized to conduct hotspot analysis. Given that one hectare would encompass nearly 2.5 hexagon grids, this area may be excessively large for detailed analysis. Therefore, one acre, which is approximately 0.4 hectares, has been selected as a more suitable scale. This choice ensures a more manageable and precise spatial resolution for our analytical purposes.
Distance
Both the distance and the available area within that distance were emphasized as two elements of accessibility in the previous research. The analysis of accessibility examines the daily mobility patterns of travelers, focusing on their journeys and preferred methods of transportation, especially walking. The statistical analysis of trip lengths is used to establish an adaptive threshold, which in turn aids in calculating a cumulative potential measure for assessing accessibility. (Rojas, Páez, Barbosa, & Carrasco, 2016). The distance is typically measured either as the Euclidean distance, which is a straight line between two points, or as the network distance, which represents the shortest route along an actual path from origin to destination. The network distance generally provides a more accurate reflection of actual travel conditions compared to the Euclidean distance (Reyes, Páez, & Morency, 2014).
Synthesizing previous studies, it is observed that the standard walking distance for accessing urban green spaces is commonly set within a 5-10 minute threshold. Conversely, the cycling distance to access these areas varies more widely, ranging from approximately 1300 meters up to 5 kilometers (Richardson, Pearce, Mitchell, Day, & Kingham, 2010).
NYC Open Data (2023) depicts that "Walking distance" refers to a maximum of a 1/4-mile for smaller sites like playgrounds and sitting areas, while for larger parks that cater to a broader area, such as those over 8 acres or near water, the distance extends to up to a 1/2-mile.
Based on the walking distance and time threshold for park accessibility, the project references the article by Curran (2024) and sets a 4 km (about 2.48 miles) threshold for cycling distance.
City Choice
The selection of New York City, Boston, and Washington DC for this study on urban park accessibility is informed by their park access metrics, which are exemplary in the U.S. Washington DC, with 99% of its residents living near a park and the highest park-related public spending, sets the benchmark for accessibility. New York City and Boston, both boasting high accessibility with 99% and 100% of residents respectively living within a 10-minute walk of a park, offer robust comparative cases (Trust for Public Land, n.d.). These cities provide diverse yet successful models of urban park accessibility, making them ideal for examining how public green spaces can enhance urban living.
GIS: A Vital Tool
The Geographic Information System (GIS) is a software designed to collect, store, and display diverse types of data, including physical, biological, environmental, ecological, and geological aspects. This integration facilitates comprehensive spatial and analytical evaluations (Gharehbaghi & Scott-Young, 2018).
GIS is essential for addressing urban park accessibility by integrating complex spatial and non-spatial data for comprehensive analysis and decision-making. It manages diverse variables like park area, distances, and demographic profiles, enhancing the understanding of green space accessibility across populations. Capabilities of GIS in modeling network distances and conducting hotspot analyses are crucial. Moreover, the use of Model Builder in GIS allows for the automation of these processes, enabling consistent application of analysis criteria across different urban areas. This systematic approach helps urban planners in strategic planning and connectivity optimization between neighborhoods and parks, thus improving the quality of life through better access to green spaces.
Hypothesis
- Densely populated blocks are predominantly located near parks.
- The majority of residents live within walking and cycling distance to parks.
The project will employ the GIS tools described previously to evaluate park accessibility in New York City, Boston, and Washington DC. Building on the hypothesis that densely populated blocks tend to cluster near parks, the analysis will define service areas for each city. This approach will facilitate a detailed comparison of the effectiveness with which these urban environments provide their residents access to green spaces. This comparative study aims to highlight variations in park accessibility and its correlation with population density, thereby providing insights into urban planning and the distribution of recreational areas.
Methodology
This section will outline the methodologies utilized within ArcGIS Pro.
Flow Chart
This flowchart delineates the methodology for assessing the accessibility of urban parks using GIS. It integrates various datasets, including road, parks and population, to build network datasets that consider two travel modes—walking and cycling. The process involves categorizing and filtering parks based on size and type, then analyzing the service areas to determine the population served. The inclusion of population data, linked via geographical identifiers, enhances the precision of the accessibility analysis, further refined by spatial analysis techniques like hotspot analysis to interpret the distribution and accessibility impacts comprehensively.
Filtered Parks
New York City
The initial filtering criterion is based on the classification of NYC parks, visualized through a bar chart that includes various categories such as Community Park, Nature Area, Waterfront Facility, Flagship Park, Neighborhood Park, Managed Sites, and Cemetery. Moreover, the project employs an additional filtering criterion based on park size, specifically selecting parks that cover a minimum area of 1 acre. This dual filtering approach ensures a focused analysis of significant urban green spaces in New York City.
Visualized Statistics: Counts by Type of Parks in NYC
Boston
In Boston, the analysis applies solely an area-based filter to the selection of urban green spaces.
Visualized Statistics: Counts by Type of Parks in Boston
Washington DC
In Washington DC, the selection criteria for urban green spaces involve categories such as Park, Small Park, Large Park, Aquatic Center, and Median. Additionally, the areas of these facilities are also filtered.
Visualized Statistics: Counts by Type of Parks in DC
Hotspot Analysis
Hotspot analysis is a tool based on Gi* Statistics raised by Getis and Ord in 1992, and developed on ArcGIS platform by ESRI in 2015 (Rossi & Becker, 2019). Hotspot analysis could identify features clustering or groupings within an area, by either presenting high or low value of a given variable (Sánchez-Martín, Rengifo-Gallego & Blas-Morato, 2019; Rossi & Becker, 2019). Based on this feature, an analysis of grouping parks into different clusters could be performed.
Given the advantage of using hexagons as grids in spatial analysis, for example, reducing sampling bias and not affected by geodesic, this part created hexagon grids for each city. Although there is no official documents provided, according to Wikipedia, the standard block in Manhattan is about 264 by 900 feet. As a result, the hexagon size is defined as 900 * 900 square feet.
Since cleaned park shapefiles and hexagon grids are ready to use, the next step is to calculate areas of parks within each hexagon. There are two probable ways to calculate the areas of parks within hexagons, one is raster based method, the other is vector based.
Raster Based Method
Rasters consist of a matrix of cells or pixels, organized around unique attribute. Owing to its ability to present continuous data accurately and extension computational ability, this method is widely used in spatial analysis (Rozhkov, 2024).
The key idea of using raster based method is to convert shapefiles into raster, and by calculating the whole number of rasters within each hexagon, the covered areas could be achieved. This method could be fulfilled by Zonal Statistics Tool.
However, there are some limitations of this method. The most important one is the inaccuracy for spatial presentation due to the raster size. In order to keep the computationality easily accessible, the raster size could not be defined too small. However, this could lead to the loss of precision of spatial relationship. As a result, under an available computational occupant raster size, the precision loss is tested to achieve 10% under this project. This limitation leads to the abandon of using raster based method.
Vector Based Method
Vector based methods use shapefiles and related tools to calculate areas. There are several tools seperating shapefiles, whereas Split outputs several new shapefiles, Clip do not give a proper feedback in this case. As a result, a new tool called Identity is introduced.
Computes a geometric intersection of the input features and identity features. The input features or portions thereof that overlap identity features will get the attributes of those identity features.
Illustration of Identity Tool for ArcGIS Pro 3.3 by ESRI
By Identity tool, parks could be divided according to hexagons.
Since the identitied parks retrived, calculate geometry could be possible. Spatial join the identitied parks with calculated areas to hexagon grids, the hexagon grids would be weighted with park areas.
A question might be raised that whether null values should be replaced by 0 value. A arcpy script was created for this purpose. After testing, the answer to the question is no replacement should be required. This is due to by entering 0 values instead of null values, the hotspot result would be all hexagons with park covered. The result could be meaningless. This could make sense since Hotspot Analysis is used to detect anomaly values. Since null values are replaced with 0, and 0 values takes the majority proportion of each city, those hexagons with area values should be anomaly data. In this case, all park areas could be treated as hotspot, which lead the result meaningless.
By performing Hot Spot Analysis (Getis-Ord Gi*) Tool based on Zoom of Indifference and Euclidean Distance, hotspot map could be achieved.
The hotspot maps could be found at the right-hand side. The left map with greens are where selected parks locate, whereas the right map with red and blue colors are the results of hotspots.
Hotspots here in the red color stands for the clusters where big parks or flagship parks locates. Coldspots here in the blue color stands for the clusters where small parks or community parks locates. White colors, however, geostatistically not significant to be anomaly, stands for those parks not clustered with big-flagship parks or small-community parks.
By building a model builder, combine all the steps into the model.
Whole Model Builder for Hotspot Analysis within NYC, DC and BOS
This is the swipe map of New York City (NYC).
This is the swipe-map of Washington, DC.
This is the swipe-map of Boston.
Selected Roads
New York City
For the selection of roads, the criteria are based on the MAF/TIGER Feature Class Code (MTFCC).
The specific codes selected for bike lanes are S1400, S1730, and S1820, which correspond to Local Neighborhood Road, Rural Road, City Street; Alley, and Bike Path or Trail, respectively.
The specific codes selected for sidewalks are S1400, S1500, S1630, S1710, S1720, S1730, S1820, and S1830, which correspond to Local Neighborhood Road, Rural Road, City Street; Vehicular Trail; Ramps; Walkway/Pedestrian Trail; Stairway; Alley; Bike Path or Trail; Bridle Path respectively.
Model Builder for Road Selection in NYC
This road selection model builder begins by taking the comprehensive road dataset and projecting it into NAD 1983 UTM Zone 18N. Following this, the model applies the SBA tool to isolate roads according to MTFCC. The selected roads are then transferred to new layers inside the feature dataset for later analysis.
Boston
For the selection of roads, the criteria are based on the MAF/TIGER Feature Class Code (MTFCC).
The selection criterion for Boston is the same as NYC.
The model builder begins by taking the comprehensive road dataset and projecting it into NAD 1983 UTM Zone 18N. Following this, the model applies the SBA tool to isolate roads according to MTFCC. The selected roads are then transferred to new layers inside the feature dataset for later analysis.
Washington DC
For the selection of roads, the criteria are based on the MAF/TIGER Feature Class Code (MTFCC).
The selection criterion for Washington DC is the same as NYC.
The model builder begins by taking the comprehensive road dataset and projecting it into NAD 1983 UTM Zone 18N. Following this, the model applies the SBA tool to isolate roads according to MTFCC. The selected roads are then transferred to new layers inside the feature dataset for later analysis.
Building Network Dataset and Service Area
For all three cities, the process begins by selecting roads and calculating the geometry of each road's length to ensure measurements are in US Survey Miles. Following this, a Network Dataset is built separately for each city using the selected roads. Adjustments are then made to the properties of the Network Dataset before running.
For the Service Area analysis, the directionality is set towards facilities. The cutoff distances for walking are established at 0.25 and 0.5 miles; the cutoff distances for cycling are established at 1 and 2.48 miles. Additionally, the polygons generated for these service areas are set to Dissolve, streamlining the visualization and analysis of the network coverage.
Import Facilities - Road Junctions
NYC
Making the centroid of each polygon as the facility method is not considered because the service polygons resulting from that will be somewhat inaccurate, especially for larger parks. Thus we employ the method suggested in the Esri community, using junctions within some very small distance of the park boundaries as input facilities for service area analysis(Service Area Analysis - Facilities Are Polygons, 2015).
For this "very small distance", we test with many small parks as samples to ensure that they have at least junctions equal to their vertices, which proves that 30m is an optimal choice.
Model Builder for Road Junction NYC
The model builder described involves a sequence of steps focused on spatially analyzing junctions near parks. Initially, it constructs a network dataset and uses the resulting junctions to create a 30m pairwise buffer. Subsequently, the model selects junctions within this buffer that intersect with park areas. A further step includes erasing junctions that are located inside the parks to refine the dataset. This process aids in determining the most relevant junctions for accessibility or infrastructure planning related to urban park areas.
In the project, the assumption is that cyclists are likely to ride to large parks identified as significant in the hotspot analysis. The process includes an additional step where the previously selected junctions are clipped to the hotspots of parks, specifically targeting areas with a GI_Bin score greater than zero. This step helps to focus on the most relevant areas for cycling accessibility related to major park attractions.
Boston
Method is same as NYC.
Washington DC
Method is same as NYC.
Service Area
NYC
Pedestrian-accessible areas primarily cover dense residential neighborhoods in boroughs such as Manhattan, Brooklyn, and parts of Queens, reflecting pedestrian-friendly infrastructure and easy access to parks. These areas are also high population density areas, meaning that most residents can easily walk to the parks.
Several distinct areas across the city that are not well-covered by the cycling accessibility areas extending from large parks. These areas are:
- Northern Manhattan and Western Bronx: This area includes neighborhoods like Washington Heights and Inwood in Manhattan, as well as parts of the Bronx near the Harlem River. Historically, parts of Northern Manhattan (like Washington Heights and Inwood) and the Western Bronx have been immigrant gates, with diverse but economically lower-income populations. These areas have often been ignored in city planning initiatives, which favored more wealthier, centrally-located neighborhoods. The focus for investment there in green infrastructure means that while there are some large parks like Van Cortlandt Park and Inwood Hill Park, the connectivity to these parks by cycling paths is not as developed as in other wealthier parts of the city.
- Central Brooklyn: Including areas such as Bedford-Stuyvesant and Crown Heights. Central Brooklyn neighborhoods such as Bedford-Stuyvesant and Crown Heights have faced severe socio-economic challenges, including high rates of poverty and crime, which historically blocked investment in public amenities.
- Eastern Queens: This includes neighborhoods like Jamaica and Valley Stream. Eastern Queens developed as a series of suburban neighborhoods, which traditionally custom to residential and commercial development over the construction of large public parks. The area's layout with larger private properties and preference for car travel may means fewer public spaces were assigned.
Service Area
Boston
Walking accessibility areas primarily cover dense urban areas such as downtown Boston, Cambridge, and surrounding neighborhoods. The pedestrian accessibility to parks in these areas is substantial, revealing Boston's commitment to ensuring that green spaces are within easy walking distance for many residents.
As seen in the cycling network, there seems to be a lack of large parks north of Boston that are accessible by cycling. Northern parts of Boston, near areas like Somerville and Cambridge, are highly urbanized with dense road networks and built environments. These dense areas often have narrower streets and more congested traffic and are unable to host large parklands.
Service Area
Washington DC
Bicycling accessibility and walking accessibility are relatively close to each other, suggesting that D.C.'s large parks are relatively evenly distributed and that the large parks that follow the river and the smaller parks in urban areas complement each other, contributing to a broad range of services.
It is also evident that there are parts of the National Wetland Park along the river to the west that are away from the reach of cycling or walking.
Results
Population Density Distribution Comparison with Park Hospot in NYC
Population Density Distribution Comparison with Park Hospot in DC
Population Density Distribution Comparison with Park Hospot in Boston
From three swipe maps above, it could be concluded that population distribution has no strong relationship with where parks locates. Except for DC, NYC and Boston has a high population density in central areas, whereas parks, especially big-flagship parks are not necessarily sorrounded with high density populations. DC, however, although sorrounded by high density populations, not only in big-flagship parks, but also small-community parks, due to the small area size of DC's region, this result has no enough extenaility. As a result, no conclusion could be achieved of people choosing residential areas according to park cluster areas from this analysis.
walking | biking | Large Park area per 1,000 residents(acre) | All Park area per 1,000 residents(acre) | |||
---|---|---|---|---|---|---|
NYC | 6,937,066 | 78.79% | 6842436 | 77.72% | 2.85 | 7.17 (depts.washington.edu, n.d.) |
Boston | 645,173 | 95.49% | 440845 | 65.25% | 8.47 | 10.36 (www.boston.gov, 2016) |
Washington DC | 649,945 | 94.26% | 632,700 | 91.76% | 11.67 | 12.90 (NCPC Home Page, n.d.) |
Served Population and Average Park Area in 3 Cities
D.C. and Boston satisfy the criteria of 10.8 acres of all parkland per 1,000 residents by NRPA. D.C. even has over 10.8 acres of large parkland per 1,000 residents.
NYC's park strategy seems focused on accessibility and high population coverage with smaller parks spread throughout the city, which is typical for its dense urban environment. In contrast, Washington D.C. emphasizes larger parks, possibly benefiting from more available space and a city layout that can supports expansive green areas. Boston appears to balance both approaches, with a decent proportion of large parks and good overall accessibility.
From the chart, NYC has similar walk-accessible and bike-accessible populations. It also offers the most extreme difference in park acreage per 1,000 residents. Boston provides a moderate level of metrics, only percentage of population within cycling accessibility is small. D.C. shows the most generous park allocation.
Discussion
Underlying reason for uncorrelation of population and park density
In the project, numerous parks are filtered out based on their categories and area. This selection criterion could potentially lead to discrepancies in the correlation between population and park density. It is important to consider that people may frequently visit smaller parks as well, despite their exclusion from the analysis due to size constraints. Ignoring these smaller parks might distort the actual accessibility and usage patterns within the urban landscape, which could, in turn, affect the reliability of the study's findings regarding the distribution and utilization of green spaces by the local population.
Moreover, when residents consider where to live, many factors come into play beyond just access to green spaces. Housing prices are a significant consideration, as affordability often dictates the neighborhoods people can choose. Commute times are another critical factor, as longer commutes can negatively impact work-life balance and overall quality of life. Proximity to schools, healthcare facilities, and shopping centers also play crucial roles in these decisions. Safety, community amenities, and the overall reputation of a neighborhood are additional factors that influence residential choices. All these elements combined shape the preferences and decisions of residents when selecting their living environments.
Morran's I and Getis-Ord G*
Morran's Index offen comes with Hot Spot Analysis (Getis-Ord G*) when doing spatial analysis and statistics. Morran's Index is a tool analyze the global spatial pattern, whereas Hot Spot Analysis focus on local spatial clusters. In this report, an analysis on how parks distribute and cluster within different cities is more likely to be a local spatial pattern, considering of the purpose of picking out big-flagship parks' cluster for further analysis. In this case, Morran'I could be one reference, but not a necessarity.
Service Area Distribution among 2 Travel Mode
Differences in walking and biking accessibility are largely dictated by urban area restrictions on the construction of large parks. Walking accessibility in this study is based on parks larger than 1 acre in the green space category (excluding purely hard surfaces), while biking accessibility is based on large parks that can be linked together to form hotspot clusters in the above parks. Large, contiguous parks require sufficient space, and thus the dense residential neighborhoods or narrow landmasses in the three cities rarely have such conditions, leaving several hard-to-reach areas within cycling accessibility. The distribution of walking accessibility is relatively even in all three cities, demonstrating excellent community-level urban park planning.
Limitation
Facilities Selection
Ideally, the selection of facilities should be based on the generation of real entrances and exits of the park; but in this project, due to the lack of entrance and exit points or park route feature class, only all junctions within 30m from the park polygons can be selected as facility points. Such a method may cause errors for large parks in dense road areas, resulting in more “entrances and exits” than in reality. For example, in New York's Central Park, the selected junctions are more than the actual number of entrances and exits due to Manhattan's dense road network around the park.
Block-level Population Selection
This study assumes an even distribution of population within each block and selects only blocks that are entirely within the accessible area for analysis. There are several limitations to this approach. First, assuming an even distribution of population within each block may not accurately reflect true population and residential patterns, which can vary widely, especially in urban areas with mixed land uses. In addition, excluding blocks that are only partially within accessible areas may result in an underestimation of the population that may benefit from proximity to parks and amenities. This approach ignores the portion of the population that lives near the defined boundary but not entirely within the accessibility definition. As a result, the study may not fully reflect the actual extent of the population that is accessible to park facilities, thus affecting the accuracy of the accessibility impact assessment.
Assumptions and Data Gaps for Cycling Accessibility
The analysis assumes that individuals predominantly cycle to parks with significant GI Bin Scores identified through hotspot analysis. This assumption restricts the estimated cycling service areas, resulting in noticeably lower coverage compared to walking service areas. However, this may not accurately reflect real-world behaviors, as individuals might cycle to a broader range of parks, not solely those rated highly in the GI Bin Scores. Furthermore, the study lacks empirical data on cycling patterns to parks, which constrains the ability to validate and refine the assumptions made about cycling accessibility. This limitation highlights the necessity for comprehensive data collection on urban cycling behavior to enhance the accuracy of service area modeling and ensure that urban planning decisions are informed by representative activity patterns.
Policy Recommendation
Urban planners and policymakers should prioritize the development of new green spaces in densely populated urban areas where such amenities are currently insufficient. Simultaneously, incentives or zoning adjustments could be implemented to guide residential developments closer to existing large park clusters. This dual strategy will enhance the overall accessibility to green spaces, fostering healthier urban environments and improving quality of life for city residents. Furthermore, regular assessments should be conducted to ensure that the distribution of green spaces continues to meet the evolving needs of the urban population.
Conclusion
This study highlights the critical role of parks in enhancing the quality of urban life, corroborating the findings of previous research. The position is that densely populated blocks tend to be situated near parks, with most residents residing within walking and cycling distances of these green spaces. To investigate this hypothesis, GIS tools were employed to construct heatmaps, perform hotspot and network analyse to assess park accessibility in New York City, Boston, and Washington D.C.
Results demonstrate that Washington D.C. and Boston adhere to, and sometimes surpass, the National Recreation and Park Association's (NRPA) recommended standard of 10.8 acres of parkland per 1,000 residents. New York City, with its dense urban structure, showcases significant variance in park acreage per capita, indicative of a strategic focus on maximizing accessibility through numerous smaller parks. Conversely, Washington D.C.'s generous parkland allocation likely reflects urban planning strategies that leverage available space for larger parks. Boston balances accessibility and size, with a considerable proportion of large parks and favorable accessibility statistics.
Nevertheless, the study encounters limitations concerning the Facilities Selection and Block-level Population Selection, which may skew the correlation between population density and park accessibility. Despite these constraints, the research contributes valuable insights into the spatial distribution and accessibility of urban parks, highlighting crucial areas for policy enhancement.
Appendix
Contribution of Each Member
Feiyang Ren: Network analysis of biking mode and related part in story map.
Ruixin Gan:Network analysis of walking mode and related part in storymap.
Xueliang Yang: Hotspot analysis for park areas; heatmap for population density distribution.
References
City of Boston. (2016). Parks and recreation. https://www.cityofboston.gov/parks
Comber, A., Brunsdon, C., & Green, E. (2008). Using a GIS-based network analysis to determine urban greenspace accessibility for different ethnic and religious groups. Landscape and Urban Planning, 86(1), 103-114. https://doi.org/10.1016/j.landurbplan.2008.01.002
Cracu, G.-M., Schvab, A., Prefac, Z., Popescu, M., & Sîrodoev, I. (2024). A GIS-based assessment of pedestrian accessibility to urban parks in the city of Constanța, Romania. Applied Geography, 103(229). https://doi.org/10.1016/j.apgeog.2024.103229
Curran, D. (n.d.). How long to cycle 4 km (By age gender & speed). Condition and Nutrition. https://conditionandnutrition.com/how-long-to-cycle-4-km-by-age-gender-speed/
El Murr, K., Boisjoly, G., & Waygood, E. O. D. (2023). Measuring accessibility to parks: Analyzing the relationship between self-reported and calculated measures. Journal of Transport Geography, 103(550). https://doi.org/10.1016/j.jtrangeo.2023.103550
Gharehbaghi, K., & Scott-Young, C. (2018). GIS as a vital tool for Environmental Impact Assessment and Mitigation. IOP Conference Series: Earth and Environmental Science, 127(1), 012009. https://doi.org/10.1088/1755-1315/127/1/012009
Haase, D., et al. (2014). A quantitative review of urban ecosystem service assessments: Concepts, models, and implementation. AMBIO, 43(4), 413-433. https://doi.org/10.1007/s13280-014-0509-5
Hoshino, T., & Kuriyama, K. (2010). Measuring the benefits of neighbourhood park amenities: Application and comparison of spatial hedonic approaches. Environmental and Resource Economics, 45(3), 429-444. https://doi.org/10.1007/s10640-009-9321-5
NCPC Home Page. (n.d.). https://www.ncpc.gov
NYC OpenData. (2023). Walk to a Park Service area. https://data.cityofnewyork.us/Recreation/Walk-to-a-Park-Service-area/5vb5-y6cv
Peters, K., Elands, B., & Buijs, A. (2010). Social interactions in urban parks: Stimulating social cohesion? Urban Forestry & Urban Greening, 9(1), 93-100. https://doi.org/10.1016/j.ufug.2009.11.003
Reyes, M., Páez, A., & Morency, C. (2014). Walking accessibility to urban parks by children: A case study of Montreal. Landscape and Urban Planning, 125, 38-47. https://doi.org/10.1016/j.landurbplan.2014.02.002
Richardson, E., Pearce, J., Mitchell, R., Day, P., & Kingham, S. (2010). The association between green space and cause-specific mortality in urban New Zealand: An ecological analysis of green space utility. BMC Public Health, 10, Article 240. https://doi.org/10.1186/1471-2458-10-240
Rojas, C., Páez, A., Barbosa, O., & Carrasco, J. (2016). Accessibility to urban green spaces in Chilean cities using adaptive thresholds. Journal of Transport Geography, 58, 12-22. https://doi.org/10.1016/j.jtrangeo.2016.10.012
Rossi, F., & Becker, G. (2019). Creating forest management units with Hot Spot Analysis (Getis-Ord Gi*) over a forest affected by mixed-severity fires. Australian Forestry, 82(4), 166–175. https://doi.org/10.1080/00049158.2019.1678714
Rozhkov, Anton (2024). Apatial Analyst 1[Lecture PowerPoint Slide]. Available: https://brightspace.nyu.edu/d2l/le/lessons/341690/topics/9961922