Overall Rating | Silver - expired |
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Overall Score | 61.34 |
Liaison | Jennifer Kleindienst |
Submission Date | Dec. 20, 2019 |
Wesleyan University
OP-1: Emissions Inventory and Disclosure
Status | Score | Responsible Party |
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2.21 / 3.00 |
William
Nelligan Director of Environmental Health, Safety, and Sustainability Physical Plant - Facilities |
"---"
indicates that no data was submitted for this field
Part 1. Greenhouse gas emissions inventory
Yes
A copy of the most recent GHG emissions inventory:
A brief description of the methodology and/or tool used to complete the GHG emissions inventory:
Wesleyan uses SIMAP to calculate its greenhouse gas emissions inventory; the inventory is calculated internally by Wesleyan's Facilities Business Manager.
Has the GHG emissions inventory been validated internally by personnel who are independent of the GHG accounting and reporting process and/or verified by an independent, external third party?:
No
A brief description of the GHG inventory verification process:
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Documentation to support the GHG inventory verification process:
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Scope 1 GHG emissions
Weight in MTCO2e | |
Stationary combustion | 19,651 Metric tons of CO2 equivalent |
Other sources (mobile combustion, process emissions, fugitive emissions) | 326 Metric tons of CO2 equivalent |
Total gross Scope 1 GHG emissions, performance year:
19,977
Metric tons of CO2 equivalent
Scope 2 GHG emissions
Weight in MTCO2e | |
Imported electricity | 1,187 Metric tons of CO2 equivalent |
Imported thermal energy | 0 Metric tons of CO2 equivalent |
Total gross Scope 2 GHG emissions, performance year:
1,187
Metric tons of CO2 equivalent
GHG emissions from biomass combustion
0
Metric tons of CO2 equivalent
Scope 3 GHG emissions
Yes or No | Weight in MTCO2e | |
Business travel | Yes | 3,681 Metric tons of CO2 equivalent |
Commuting | Yes | 1,540 Metric tons of CO2 equivalent |
Purchased goods and services | Yes | 112 Metric tons of CO2 equivalent |
Capital goods | No | --- |
Fuel- and energy-related activities not included in Scope 1 or Scope 2 | Yes | 60 Metric tons of CO2 equivalent |
Waste generated in operations | Yes | 0 Metric tons of CO2 equivalent |
Other sources | Yes | 1,319 Metric tons of CO2 equivalent |
Total Scope 3 GHG emissions, performance year:
6,712
Metric tons of CO2 equivalent
A brief description of how the institution accounted for its Scope 3 emissions:
Scope 3 emissions (other) include study abroad (1329 MTCO2e), solid waste (-25 MTCO2e), and wastewater (15 MTCO2e).
Commuting data is based on zip codes.
Employee business travel is extrapolated from spend on air and ground travel.
Study abroad air travel is extrapolated based on country visited (calculate RT emissions to largest city in that country).
Solid waste, wastewater, paper purchasing, and T&D loss emissions are all direct calculations.
Commuting data is based on zip codes.
Employee business travel is extrapolated from spend on air and ground travel.
Study abroad air travel is extrapolated based on country visited (calculate RT emissions to largest city in that country).
Solid waste, wastewater, paper purchasing, and T&D loss emissions are all direct calculations.
Part 2. Air pollutant emissions inventory
Yes
Annual weight of emissions for::
Weight of Emissions | |
Nitrogen oxides (NOx) | 18.70 Tons |
Sulfur oxides (SOx) | 0.85 Tons |
Carbon monoxide (CO) | 11.37 Tons |
Particulate matter (PM) | 4.16 Tons |
Ozone (O3) | 0 Tons |
Lead (Pb) | 0.00 Tons |
Hazardous air pollutants (HAPs) | 0.22 Tons |
Ozone-depleting compounds (ODCs) | 0.00 Tons |
Other standard categories of air emissions identified in permits and/or regulations | 2.64 Tons |
Do the air pollutant emissions figures provided include the following sources?:
Yes or No | |
Major stationary sources | Yes |
Area sources | Yes |
Mobile sources | No |
Commuting | No |
Off-site electricity production | No |
None
A brief description of the methodology(ies) the institution used to complete its air emissions inventory:
Wesleyan has inventoried every piece of fossil fuel burning equipment on campus. Equipment is grouped based on its capacity and type of fuel and emissions calculations, following EPA prescribed processes. These processes are performed for each group of equipment. Emissions calculations are maintained on a rolling 12 month period. The data above is from the most recent year collected, ending in September 2017.
For stationary air emissions, we do not record ozone as a pollutant. PM includes PM 2.5 and PM 10. HAPs include benzene, dichlorobenzene, formaldehyde, hexane, naphthalene, toluene, ethyl benzene, xylene, acrolein, methanol, and styrene. The only ODC Wesleyan includes in its air inventory is carbon tetrachloride. Our "other" category is VOCs (0.82 tons). The data represented for stationary sources is for calendar year 2015.
For stationary air emissions, we do not record ozone as a pollutant. PM includes PM 2.5 and PM 10. HAPs include benzene, dichlorobenzene, formaldehyde, hexane, naphthalene, toluene, ethyl benzene, xylene, acrolein, methanol, and styrene. The only ODC Wesleyan includes in its air inventory is carbon tetrachloride. Our "other" category is VOCs (0.82 tons). The data represented for stationary sources is for calendar year 2015.
Optional Fields
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Gross Scope 2 GHG emissions from imported thermal energy (location-based) :
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Website URL where information about the institution’s emissions inventories is available:
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Additional documentation to support the submission:
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Data source(s) and notes about the submission:
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The information presented here is self-reported. While AASHE staff review portions of all STARS reports and institutions are welcome to seek additional forms of review, the data in STARS reports are not verified by AASHE. If you believe any of this information is erroneous or inconsistent with credit criteria, please review the process for inquiring about the information reported by an institution or simply email your inquiry to stars@aashe.org.