Overall Rating | Gold |
---|---|
Overall Score | 82.88 |
Liaison | Patrick McKee |
Submission Date | Nov. 16, 2023 |
University of Connecticut
OP-1: Emissions Inventory and Disclosure
Status | Score | Responsible Party |
---|---|---|
2.90 / 3.00 |
Patrick
McKee Senior Sustainability Program Manager Office of Sustainability |
"---"
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:
The 2022 GHG Inventory was conducted with the UNH SIMAP online calculator. UConn originally used the traditional spreadsheet-style Campus Carbon Calculator (CCC) by UNH, but replaced the CCC with SIMAP in 2017.
For Scope 3 emissions, Commuting reflects only the emissions associated with students and faculty/staff driving to campus in automobiles (SIMAP lists Faculty and Staff separately, but our university tracks them as one group of permits, so we only listed them under "Faculty"). Parking permit numbers are used to estimate the number of miles driven annually. For Purchased goods and services, only paper is reflected here. This data is retrieved from UConn’s purchasing office. For solid waste, data is obtained from UConn’s waste contractor, Willimantic Waste, and wastewater data is retrieved from the Facilities department, who runs our on-site wastewater treatment plant.
For Scope 3 emissions, Commuting reflects only the emissions associated with students and faculty/staff driving to campus in automobiles (SIMAP lists Faculty and Staff separately, but our university tracks them as one group of permits, so we only listed them under "Faculty"). Parking permit numbers are used to estimate the number of miles driven annually. For Purchased goods and services, only paper is reflected here. This data is retrieved from UConn’s purchasing office. For solid waste, data is obtained from UConn’s waste contractor, Willimantic Waste, and wastewater data is retrieved from the Facilities department, who runs our on-site wastewater treatment plant.
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?:
Yes
A brief description of the GHG inventory verification process:
Once completed, the inventory is reviewed and verified by the Sustainability Program Manager and the Energy & Compliance Manager who is responsible for the Energy Management unit within Facilities Operations & Building Services, which operates and maintains the stationary sources that account for the vast majority of our GHG emissions, and which manages UConn's purchased power activities. The inventory is also presented annually at the spring meeting of UConn's Environmental Policy Advisory Council, which is responsible for overseeing implementation of UConn's Climate Action Plan and carbon-neutrality commitment pursuant to the Second Nature's Carbon/Climate Commitment.
UConn’s Storrs Campus is subject to the EPA’s GHG reporting requirements, which are codified in 40 CFR 98, because the facility has stationary fuel combustion sources with an aggregate maximum rated heat input capacity equal to or greater than 30 million Btu per hour and the facility’s total CO2e emissions are equal to or greater than 25,000 metric tons. UConn prepares a GHG emissions report to EPA by March 31st of each year covering emissions during the previous calendar year and submits the report electronically through EPA’s online e-GGRT system. EPA reviews and verifies the accuracy of our annual GHG emissions report/inventory as a regulatory compliance matter.
UConn’s Storrs Campus is subject to the EPA’s GHG reporting requirements, which are codified in 40 CFR 98, because the facility has stationary fuel combustion sources with an aggregate maximum rated heat input capacity equal to or greater than 30 million Btu per hour and the facility’s total CO2e emissions are equal to or greater than 25,000 metric tons. UConn prepares a GHG emissions report to EPA by March 31st of each year covering emissions during the previous calendar year and submits the report electronically through EPA’s online e-GGRT system. EPA reviews and verifies the accuracy of our annual GHG emissions report/inventory as a regulatory compliance matter.
Documentation to support the GHG inventory verification process:
Scope 1 GHG emissions
Weight in MTCO2e | |
Stationary combustion | 100,947.90 Metric tons of CO2 equivalent |
Other sources (mobile combustion, process emissions, fugitive emissions) | 2,891.50 Metric tons of CO2 equivalent |
Total gross Scope 1 GHG emissions, performance year:
103,839.40
Metric tons of CO2 equivalent
Scope 2 GHG emissions
Weight in MTCO2e | |
Imported electricity | 4,372.02 Metric tons of CO2 equivalent |
Imported thermal energy | 0 Metric tons of CO2 equivalent |
Total gross Scope 2 GHG emissions, performance year:
4,372.02
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 | 1,626.54 Metric tons of CO2 equivalent |
Commuting | Yes | 11,936.21 Metric tons of CO2 equivalent |
Purchased goods and services | Yes | 157.40 Metric tons of CO2 equivalent |
Capital goods | No | --- |
Fuel- and energy-related activities not included in Scope 1 or Scope 2 | Yes | 37,666.22 Metric tons of CO2 equivalent |
Waste generated in operations | Yes | 875.89 Metric tons of CO2 equivalent |
Other sources | No | --- |
Total Scope 3 GHG emissions, performance year:
52,262.26
Metric tons of CO2 equivalent
A brief description of how the institution accounted for its Scope 3 emissions:
UConn internally tracks all Scope 3 emissions data, including but not limited to Faculty commuting, student commuting, waste water, paper purchasing, and more. All data is tracked within fiscal and calendar years and is submitted annually to the Office of Sustainability.
Part 2. Air pollutant emissions inventory
Yes
Annual weight of emissions for::
Weight of Emissions | |
Nitrogen oxides (NOx) | 28.28 Tons |
Sulfur oxides (SOx) | 2.34 Tons |
Carbon monoxide (CO) | 28.81 Tons |
Particulate matter (PM) | 56.20 Tons |
Ozone (O3) | 0 Tons |
Lead (Pb) | 0 Tons |
Hazardous air pollutants (HAPs) | 0 Tons |
Ozone-depleting compounds (ODCs) | 0 Tons |
Other standard categories of air emissions identified in permits and/or regulations | 0 Tons |
Do the air pollutant emissions figures provided include the following sources?:
Yes or No | |
Major stationary sources | Yes |
Area sources | No |
Mobile sources | Yes |
Commuting | No |
Off-site electricity production | Yes |
None
A brief description of the methodology(ies) the institution used to complete its air emissions inventory:
The University uses a combination of methodologies to track emissions from our fuel burning sources of emissions. For most sources, UConn tracks fuel use and/or hours of operation and applies a standard emissions factor (EPA AP-42, manufacturer’s guarantee, or from stack test results) with worst case assumptions. For one particular boiler, the University uses actual continuous emission monitoring data for NOx. Every month a new 12-month rolling total is calculated for the emissions categories to demonstrate permit compliance.
UConn Design Guidelines and Performance Standards (pp 19, 3.10 Air Emissions):
http://paes.uconn.edu/wp-content/uploads/sites/1525/2016/04/Design-Guidelines-and-Performance-Standards-March-2016.pdf
UConn Environmental Health & Safety
https://ehs.uconn.edu/
NOx and VOCs (Volatile Organic Compounds) are precursors to ozone formation and are dependent upon atmospheric conditions. Therefore, ozone and ODCs are difficult to measure and not tracked.
UConn Design Guidelines and Performance Standards (pp 19, 3.10 Air Emissions):
http://paes.uconn.edu/wp-content/uploads/sites/1525/2016/04/Design-Guidelines-and-Performance-Standards-March-2016.pdf
UConn Environmental Health & Safety
https://ehs.uconn.edu/
NOx and VOCs (Volatile Organic Compounds) are precursors to ozone formation and are dependent upon atmospheric conditions. Therefore, ozone and ODCs are difficult to measure and not tracked.
Optional Fields
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Gross Scope 2 GHG emissions from imported thermal energy (location-based) :
---
Website URL where information about the institution’s emissions inventories is available:
Additional documentation to support the submission:
---
Data source(s) and notes about the submission:
Ozone and ODCs are not tracked (difficult to measure). We do however track HCFCs used to replace refrigerants in chillers and other cooling equipment. This is tracked as part of our GHG inventory as a way to measure emissions of ODCs that are also GHG emissions sources.
On our attached Greenhouse Gas Report, 'Direct Transportation' encompasses business travel.
On our attached Greenhouse Gas Report, 'Direct Transportation' encompasses business travel.
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.