inequitable distribution of the urban heat island...

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Inequitable Distribution of the Urban Heat Island Effect in Minneapolis Neighborhoods Manisha Rattu, Stanford University, UCSC Doris Duke Conservation Scholar The Natural Capital Project, Institute on the Environment, University of Minnesota Background Methods This research was supported by the Natural Capital Project and Islands in the Sun. Future Directions Conclusion Results Data Collection All GIS UHI and temperature data was provided by UMN Islands in the Sun Project in the form of raster layers (Dr. Tracy Twine and Phillip Mykleby). All shapefiles (e.g., tree canopy and American Community Survey Census data summarized by neighborhood, or provided by the Minneapolis Park and Recreation Board (MPRB). In the available neighborhood-level Census data, two industrial neighborhoods were not included and thus excluded from this analysis. 1. Conduct neighborhood scale analysis of urban tree canopy (street trees, parks, and private lawns) and relate it to UHI in Minneapolis. Hypothesis: More tree canopy associated negatively with UHI 2. Delve into the relationship between income and UHI. Hypothesis: Higher income associated negatively with UHI 3.Study the racial demographics of neighborhoods most impacted by UHI and absence of urban tree canopy. Hypothesis: Areas with more people of color associated positively with UHI Objectives Urban Heat Island or “UHI” is heat in degrees that is above the baseline average temperature. Expanding urbanization has increased the amount of urban impervious surfaces, which increase the absorption of solar radiation and further UHI effects. 1 UHI hotspots directly and indirectly lead to unsafe living conditions for humans 2 , including heightened temperatures and increased air pollution 3 . These effects are amplified during the summer time when there is more solar radiation 2 and at night, due to the slow release of heat absorbed by impervious surfaces 4 . Urban trees stimulate shading, evapotranspiration, and airflow, which in turn can reduce temperatures and provide cooling benefits 5 . UHI effects tend to disproportionately impact certain communities and populations, leading to equity concerns. For example, a study conducted in Phoenix, AZ revealed that urban poor are more vulnerable to UHI effects, due to their “living in areas with less vegetation, which expose residents to higher outdoor temperatures.” 6 This study does a similar analysis in Minneapolis, Minnesota. ArcGIS After obtaining the necessary data files, all were transformed into the correct projection. The raster layers were resampled before running zonal statistics to summarize UHI by neighborhood. Afterwards, the various data tables were joined to create a central database of Minneapolis neighborhood UHI attributes. Statistical Analysis The linear regression modeling tool in JMP Pro was used to test the variables for significance. 1. UHI is higher in neighborhoods with less canopy cover to provide shading and cooling benefits. 2. Neighborhoods with lower UHI tend to have a greater median income than neighborhoods with limited tree canopy cover. 3. Neighborhoods with a greater percentage of People of Color tend to have higher UHI, and less urban tree canopy accordingly. This study supports all initial hypotheses and suggests the potential for future research. The MPRB is currently working on a 20-Year Neighbor Park Plan and is interested in issues of park access and equity. Further research that builds on this analysis to improve our understanding about how increasing urban tree canopy in parks and public spaces mitigates UHI, especially in vulnerable neighborhoods, would be of interest to the park agency. Use a model to determine the amount of heat mitigation from planting more trees Include the heat wave event data in analysis to observe effects under extreme UHI conditions • Incorporate air conditioning (A/C) information into neighborhood analysis and conduct vulnerability analysis Create a prioritization list of vulnerable neighborhoods based on multiple variables, such as A/C availability, tree cover, and demographic variables • Based on these analyses and in conjunction with MPRB, a policy recommendation would be to increase urban tree canopy by planting more street and park trees References 1. Loughner, C.P., et al. “Roles of Urban Tree Canopy and Buildings in Urban Heat Island Effects: Parameterization and Preliminary Results.” J. of Appl. Meteor. Climatol. 51.10 (2012): 1775–1793. Web. 14 Aug. 2017 2. Kunkel, K.E. et al. “The July 1995 Heat Wave in the Midwest: A Climatic Perspective and Critical Weather Factors.” Bull. Amer. Meteor. Soc. 77.7 (1996): 1507–1518. Web. 15 Aug. 2017. 3. Tai, A.P.K., et al. “Correlations between Fine Particulate Matter (PM2.5) and Meteorological Variables in the United States: Implications for the Sensitivity of PM2.5 to Climate Change.” Atmos. Environ. 44.32 (2010): 3976–3984. Web. 15 Aug. 2017. 4. Harlan, S.L., et al. “Neighborhood Microclimates and Vulnerability to Heat Stress.” Soc. Sci. Med. 63.11 (2006): 2847–2863. Web. 14 Aug. 2017. 5. Mcpherson, E Gregory, et al. “Energy Conservation Potential Of Urban Tree Planting.” Journal of Arboriculture 19.6 (1993): n. pag. Web. 16 Aug. 2017. 6. Jenerette, G.D., et al. “Ecosystem Services and Urban Heat Riskscape Moderation: Water, Green Spaces, and Social Inequality in Phoenix, USA.” Ecol. Appl. 21.7 (2011): 2637–2651. Web. 14 Aug. 2017. Night UHI is significantly and negatively correlated with Urban Tree Canopy (p-value < 0.0001, R2 = 0.34) 20% (78,875) of Minneapolis residents live in areas where the night UHI effect is greater than 2 degrees Celsius. 45% (35,944) of those residents are people of color, 11% (8,676) do not have health insurance, and 30% (23,663) are under the poverty line. In neighborhoods with more than 40% Urban Tree Canopy, 76% of residents are White. Night UHI is significantly and positively correlated with Persons of Color (p-value = 0.0364, R2 = 0.05) Night UHI is significantly and negatively correlated with Median Household Income (p-value < 0.0001, R2 = 0.26) . 0 2 4 6 8 1 Miles . Night UHI Mean (C) Urban Tree Canopy (%) People of Color (%) . . Median Household Income ($) Minneapolis, MN, USA Urban Tree Canopy (%) 4 - 15 15 - 29 29 - 38 38 - 49 People of Color (%) 10 - 20 20 - 33 33 - 61 61 - 91 Median Household Income ($) 17,469 - 37,438 37,438 - 59,414 59,414 - 83,520 83,520 - 118,750 Night UHI Mean (C) 1.4 - 1.6 1.6 - 1.8 1.8 - 2.0 2.0 - 2.2 Urban Tree Canopy Cover VS. Night UHI Median Household Income VS. Night UHI 1.2 1.4 1.6 1.8 2 2.2 2.4 0 10 20 30 40 50 Night UHI Mean (C) Urban Tree Canopy (%) People of Color VS. Night UHI 1.2 1.4 1.6 1.8 2 2.2 2.4 0 20000 40000 60000 80000 100000 120000 Night UHI Mean (C) Median Household Income ($) 1.2 1.4 1.6 1.8 2 2.2 2.4 0 0.2 0.4 0.6 0.8 1 Night UHI Mean (C) People of Color (%)

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Page 1: Inequitable Distribution of the Urban Heat Island …environment.umn.edu/.../2017/09/Manisha_Rattu_UHI_Poster.pdfExpanding urbanization has increased the amount of urban impervious

Inequitable Distribution of the Urban Heat Island Effect in Minneapolis Neighborhoods Manisha Rattu, Stanford University, UCSC Doris Duke Conservation Scholar

The Natural Capital Project, Institute on the Environment, University of Minnesota

Background Methods

This research was supported by the Natural Capital Project and Islands in the Sun.

Future Directions

Conclusion

Results

Data Collection All GIS UHI and temperature data was provided by UMN Islands in the Sun Project in the form of raster layers (Dr. Tracy Twine and Phillip Mykleby). All shapefiles (e.g., tree canopy and American Community Survey Census data summarized by neighborhood, or provided by the Minneapolis Park and Recreation Board (MPRB). In the available neighborhood-level Census data, two industrial neighborhoods were not included and thus excluded from this analysis.

1.  Conduct neighborhood scale analysis of urban tree canopy (street trees, parks, and private lawns) and relate it to UHI in Minneapolis. •  Hypothesis: More tree canopy associated

negatively with UHI 2.  Delve into the relationship between income and

UHI. •  Hypothesis: Higher income associated

negatively with UHI 3.  S t u d y t h e r a c i a l d e m o g r a p h i c s o f

neighborhoods most impacted by UHI and absence of urban tree canopy. •  Hypothesis: Areas with more people of color

associated positively with UHI

Objectives

Urban Heat Island or “UHI” is heat in degrees that is above the baseline average temperature. Expanding urbanization has increased the amount of urban impervious surfaces, which increase the absorption of solar radiation and further UHI effects.1 UHI hotspots directly and indirectly lead to unsafe living conditions for humans2, including heightened temperatures and increased air pollution3. These effects are amplified during the summer time when there is more solar radiation2 and at night, due to the slow release of heat absorbed by impervious surfaces4. Urban trees stimulate shading, evapotranspiration, and airflow, which in turn can reduce temperatures and provide coo l i ng bene f i t s5 . UHI e f fec ts tend to disproportionately impact certain communities and populations, leading to equity concerns. For example, a study conducted in Phoenix, AZ revealed that urban poor are more vulnerable to UHI effects, due to their “living in areas with less vegetation, which expose residents to higher outdoor temperatures.”6 This study does a similar analysis in Minneapolis, Minnesota.

ArcGIS After obtaining the necessary data files, all were transformed into the correct projection. The raster layers were resampled before running zonal s tat is t ics to summar ize UHI by neighborhood. Afterwards, the various data tables were joined to create a central database of Minneapolis neighborhood UHI attributes.

Statistical Analysis The linear regression modeling tool in JMP Pro was used to test the variables for significance.

1.  UHI is higher in neighborhoods with less canopy cover to provide shading and cooling benefits.

2.  Neighborhoods with lower UHI tend to have a greater median income than neighborhoods with limited tree canopy cover.

3.  Neighborhoods with a greater percentage of People of Color tend to have higher UHI, and less urban tree canopy accordingly.

This study supports all initial hypotheses and suggests the potential for future research. The MPRB is currently working on a 20-Year Neighbor Park Plan and is interested in issues of park access and equity. Further research that builds on this analysis to improve our understanding about how increasing urban tree canopy in parks and public spaces mitigates UHI, especially in vulnerable neighborhoods, would be of interest to the park agency.

•  Use a model to determine the amount of heat mitigation from planting more trees

•  Include the heat wave event data in analysis to observe effects under extreme UHI conditions

•  Incorporate air conditioning (A/C) information into neighborhood analysis and conduct vulnerability analysis

•  Create a prioritization list of vulnerable neighborhoods based on multiple variables, such as A/C availability, tree cover, and demographic variables

•  Based on these analyses and in conjunction with MPRB, a policy recommendation would be to increase urban tree canopy by planting more street and park trees

References 1.  Loughner, C.P., et al. “Roles of Urban Tree Canopy and Buildings in Urban Heat

Island Effects: Parameterization and Preliminary Results.” J. of Appl. Meteor. Climatol. 51.10 (2012): 1775–1793. Web. 14 Aug. 2017

2.  Kunkel, K.E. et al. “The July 1995 Heat Wave in the Midwest: A Climatic Perspective and Critical Weather Factors.” Bull. Amer. Meteor. Soc. 77.7 (1996): 1507–1518. Web. 15 Aug. 2017.

3.  Tai, A.P.K., et al. “Correlations between Fine Particulate Matter (PM2.5) and Meteorological Variables in the United States: Implications for the Sensitivity of PM2.5 to Climate Change.” Atmos. Environ. 44.32 (2010): 3976–3984. Web. 15 Aug. 2017.

4.  Harlan, S.L., et al. “Neighborhood Microclimates and Vulnerability to Heat Stress.” Soc. Sci. Med. 63.11 (2006): 2847–2863. Web. 14 Aug. 2017.

5.  Mcpherson, E Gregory, et al. “Energy Conservation Potential Of Urban Tree Planting.” Journal of Arboriculture 19.6 (1993): n. pag. Web. 16 Aug. 2017.

6.  Jenerette, G.D., et al. “Ecosystem Services and Urban Heat Riskscape Moderation: Water, Green Spaces, and Social Inequality in Phoenix, USA.” Ecol. Appl. 21.7 (2011): 2637–2651. Web. 14 Aug. 2017.

Night UHI is significantly and negatively correlated with Urban Tree Canopy

(p-value < 0.0001, R2 = 0.34)

•  20% (78,875) of Minneapolis residents live in areas where the night UHI effect is greater than 2 degrees Celsius.

•  45% (35,944) of those residents are people of color, 11% (8,676) do not have health insurance, and 30% (23,663) are under the poverty line.

•  In neighborhoods with more than 40% Urban Tree Canopy, 76% of residents are White.

Night UHI is significantly and positively correlated with Persons of Color

(p-value = 0.0364, R2 = 0.05)

Night UHI is significantly and negatively correlated with Median Household Income

(p-value < 0.0001, R2 = 0.26)

.0 2 4 6 81

Miles

.

Night UHI Mean (C) Urban Tree Canopy (%) People of Color (%)

. .

Median Household Income ($)

Minneapolis, MN, USA

Urban Tree Canopy (%)4 - 15

15 - 29

29 - 38

38 - 49

People of Color (%)10 - 20

20 - 33

33 - 61

61 - 91

Median Household Income ($)17,469 - 37,438

37,438 - 59,414

59,414 - 83,520

83,520 - 118,750

Night UHI Mean (C)1.4 - 1.6

1.6 - 1.8

1.8 - 2.0

2.0 - 2.2

Urban Tree Canopy Cover VS. Night UHI

Median Household Income VS. Night UHI

1.2

1.4

1.6

1.8

2

2.2

2.4

0 10 20 30 40 50

Nig

ht U

HI M

ean

(C)

Urban Tree Canopy (%)

People of Color VS. Night UHI

1.2

1.4

1.6

1.8

2

2.2

2.4

0 20000 40000 60000 80000 100000 120000

Nig

ht U

HI M

ean

(C)

Median Household Income ($)

1.2

1.4

1.6

1.8

2

2.2

2.4

0 0.2 0.4 0.6 0.8 1

Nig

ht U

HI M

ean

(C)

People of Color (%)