EPD additional content Cascadia Clip®
Data
Background
This product-specific plant-specific declaration was created by collecting production data from the British Columbia, Canada location. Secondary data sources include those available in ecoinvent v3, Industry data 2.0, and US-EI 2.2 databases.
Allocation
The PCR prescribes where and how allocation occurs. Since only facility-level data were available, allocation among the facility's other products was necessary to determine the input and output flows associated with the product. The allocation of electricity, water, and fuel consumption was based on the percentage of production by mass for the fabricated clip systems. The mass allocation considered the ratio between each clip production and the total annual site production output. Additionally, no co‐products were produced during the fabrication processes.
Cut-off criteria
Cut-off criteria for the inclusion of mass and energy flows are 1% of renewable primary resource (energy) usage, 1% nonrenewable primary resource (energy) usage, 1% of the total mass input of that unit process, and 1% of environmental impacts. The total of neglected input flows per module does not exceed 5% of energy usage, mass, and environmental impacts. The only exceptions to these criteria are substances with hazardous and toxic properties, which must be listed even when the given process unit is under the cut-off criterion of 1% of the total mass. No known flows are deliberately excluded from this declaration; therefore, these criteria have been met. Biogenic carbon is included in reported results.
Quality
Inventory data quality is judged by its precision (measured, calculated, or estimated), completeness (e.g., unreported emissions), consistency (degree of uniformity of the methodology applied on a study serving as a data source), and representativeness (geographical, temporal, and technological).
To cover these requirements and to ensure reliable results, first-hand industry data in combination with consistent background LCA information from SimaPro Analyst 9.5, and the ecoinvent v3.9, Industry data 2.0, and US-EI 2.2 databases were used.
Sustainable Minds worked with Cascadia to obtain a comprehensive set of primary data associated with the manufacturing processes. The product system was checked for mass balance and completeness of the inventory. The data set was considered complete based on our understanding of the manufacturing site and a review with key stakeholders on the Cascadia team, and cut-off criteria were observed consistent with those prescribed in the PCR. Capital equipment was excluded as required by the PCR. Otherwise, no data was knowingly omitted. Where country-specific data were unavailable, global or rest-of-world averages were used as proxies to represent transportation in those locations. Additionally, no proxy data were used to represent materials and therefore did not have a significant impact of the results.
Primary data were collected with a similar level of detail, while background data were sourced primarily from the ecoinvent database, and other databases were used if data were not available in ecoinvent or the data set was judged to be more representative. Other methodological choices were made consistently throughout the model.
Technical information
Major assumptions and limitations:
- Primary data were modeled based on the information provided by Cascadia and supplemented by data contained in the technical and safety data sheets provided.
- Since energy inputs were not available on a per-product basis, electricity and natural gas consumption were allocated proportionately based on the percentage of production for individual clip products versus total site annual outputs.
- Generic data sets used for material inputs, transport, and waste processing are considered good quality, but actual impacts from material suppliers, transport carriers, and local waste processing may vary.
- The impact assessment methodology categories do not represent all possible environmental impact categories.
- Characterization factors used within the impact assessment methodology may contain varying levels of uncertainty.
- LCA results are relative expressions and do not predict impacts on category endpoints, the exceeding of thresholds, safety margins, or risks.
Major system boundary exclusions:
- Construction of major capital equipment
- Maintenance and operation of support equipment
- Human labor and employee transport
- Manufacture and transport of packaging materials not associated with the final product
- Disposal of packaging materials not associated with the final product
- Building operational energy and water use
Flow diagram
Cascadia Clip® fiberglass thermal spacer: LCIA results, resource use, output and waste flows, and carbon emissions & removals per declared unit
Parameter | Unit | A1 Raw materials |
A2 Transport |
A3 Manufacturing |
Total |
LCIA results | |||||
Ozone depletion |
kg CFC-11 eq |
5.09E-08 |
3.40E-09 |
1.07E-09 |
5.54E-08 |
Global warming |
kg CO2 eq |
3.61E+00 |
2.15E-01 |
1.14E-01 |
3.94E+00 |
Smog |
kg O3 eq |
1.57E-01 |
4.84E-02 |
1.69E-03 |
2.08E-01 |
Acidification |
kg SO2 eq |
1.09E-02 |
2.62E-03 |
6.18E-05 |
1.36E-02 |
Eutrophication |
kg N eq |
2.38E-03 |
1.13E-04 |
1.94E-05 |
2.52E-03 |
Carcinogenics |
CTUh |
2.95E-08 |
1.67E-10 |
1.91E-11 |
2.97E-08 |
Non-carcinogenics |
CTUh |
1.57E-07 |
1.86E-08 |
8.71E-10 |
1.77E-07 |
Respiratory effects |
kg PM2.5 eq |
1.35E-03 |
1.79E-04 |
4.79E-06 |
1.54E-03 |
Additional environmental information |
|||||
Ecotoxicity |
CTUe |
2.54E+00 |
3.53E-01 |
1.50E-03 |
2.89E+00 |
Fossil fuel depletion |
MJ surplus |
4.65E+01 |
2.80E+00 |
1.52E+00 |
5.08E+01 |
Resource use indicators |
|||||
Renewable primary energy used as energy carrier (fuel) |
MJ, NCV |
1.49E+01 |
1.47E+01 |
4.36E-03 |
2.97E+01 |
Renewable primary resources with energy content used as material |
MJ, NCV |
1.58E-01 |
0 |
0 |
1.58E-01 |
Total use of renewable primary resources with energy content |
MJ, NCV |
1.51E+01 |
1.47E+01 |
4.36E-03 |
2.98E+01 |
Non-renewable primary resources used as an energy carrier (fuel) |
MJ, NCV |
5.81E+01 |
5.34E+01 |
2.99E+00 |
1.14E+02 |
Non-renewable primary resources with energy content used as material |
MJ, NCV |
4.33E-02 |
0 |
0 |
4.33E-02 |
Total use of non-renewable primary resources with energy content |
MJ, NCV |
5.81E+01 |
5.34E+01 |
2.99E+00 |
1.14E+02 |
Secondary materials |
kg |
0 |
0 |
0 |
0 |
Renewable secondary fuels |
MJ, NCV |
0 |
0 |
0 |
0 |
Non-renewable secondary fuels |
MJ, NCV |
0 |
0 |
0 |
0 |
Recovered energy |
MJ, NCV |
0 |
0 |
0 |
0 |
Use of net fresh water resources |
m3 |
3.27E+00 |
2.00E-02 |
2.98E-02 |
3.32E+00 |
Output flows and waste category indicators |
|||||
Hazardous waste disposed |
kg |
0 |
0 |
0 |
0 |
Non-hazardous waste disposed |
kg |
0 |
0 |
1.92E-02 |
1.92E-02 |
High-level radioactive waste, conditioned, to final repository |
kg |
3.66E+02 |
2.90E+00 |
8.23E+00 |
3.77E+02 |
Intermediate- and low-level radioactive waste, conditioned, to final repository |
kg |
2.63E-01 |
1.51E-03 |
9.24E-04 |
2.66E-01 |
Components for re-use |
kg |
0 |
0 |
2.00E-02 |
2.00E-02 |
Materials for recycling |
kg |
0 |
0 |
9.95E-05 |
9.95E-05 |
Materials for energy recovery |
kg |
0 |
0 |
0 |
0 |
Exported energy |
MJ |
0 |
0 |
0 |
0 |
Carbon emissions and removals |
|||||
Biogenic carbon removal from product | kg CO2 |
0 |
0 |
0 |
0 |
Biogenic carbon emission from product | kg CO2 |
0 |
0 |
0 |
0 |
Biogenic carbon removal from packaging | kg CO2 | 1.99E-02 |
0 |
1.12E-02 |
3.11E-02 |
Biogenic carbon emission from packaging | kg CO2 | 0 |
0 |
0 |
0 |
Biogenic carbon emission from combustion of waste from renewable sources used in production processes | kg CO2 | 0 |
0 |
0 |
0 |
Calcination carbon emissions | kg CO2 | 0 |
0 |
0 |
0 |
Carbonation carbon removals | kg CO2 | 0 |
0 |
0 |
0 |
Carbon emissions from combustion of waste from renewable and non- renewable sources used in production processes | kg CO2 | 0 |
0 |
0 |
0 |
LCIA results for a single clip component
Impact category |
Unit |
A1 Raw materials |
A2 Transport |
A3 Manufacturing |
Total |
Ozone depletion |
kg CFC-11 eq |
4.82E-08 |
1.81E-09 |
1.06E-09 |
5.11E-08 |
Global warming |
kg CO2 eq |
1.97E+00 |
1.16E-01 |
1.14E-01 |
2.20E+00 |
Smog |
kg O3 eq |
9.41E-02 |
2.48E-03 |
1.69E-03 |
9.82E-02 |
Acidification |
kg SO2 eq |
6.95E-03 |
1.57E-04 |
6.18E-05 |
7.17E-03 |
Eutrophication |
kg N eq |
2.14E-03 |
1.91E-05 |
1.94E-05 |
2.18E-03 |
Carcinogenics |
CTUh |
1.73E-08 |
1.02E-10 |
1.91E-11 |
1.74E-08 |
Non-carcinogenics |
CTUh |
5.54E-08 |
1.54E-08 |
8.70E-10 |
7.17E-08 |
Respiratory effects |
kg PM2.5 eq |
9.21E-04 |
3.63E-05 |
4.78E-06 |
9.62E-04 |
Additional environmental information |
|||||
Ecotoxicity |
CTUe |
2.07E+00 |
3.12E-01 |
1.48E-03 |
2.39E+00 |
Fossil fuel depletion |
MJ surplus |
2.84E+01 |
1.56E+00 |
1.54E+00 |
3.14E+01 |
LCIA results for 12 inches of metal rail
Impact category |
Unit |
A1 Raw materials |
A2 Transport |
A3 Manufacturing |
Total |
Ozone depletion |
kg CFC-11 eq |
1.35E-09 |
7.96E-10 |
1.71E-12 |
2.15E-09 |
Global warming |
kg CO2 eq |
8.17E-01 |
4.99E-02 |
6.74E-05 |
8.67E-01 |
Smog |
kg O3 eq |
3.17E-02 |
2.30E-02 |
1.89E-06 |
5.47E-02 |
Acidification |
kg SO2 eq |
1.96E-03 |
1.23E-03 |
4.04E-08 |
3.19E-03 |
Eutrophication |
kg N eq |
1.20E-04 |
4.69E-05 |
5.76E-09 |
1.67E-04 |
Carcinogenics |
CTUh |
6.09E-09 |
3.24E-11 |
1.81E-14 |
6.12E-09 |
Non-carcinogenics |
CTUh |
5.10E-08 |
1.58E-09 |
1.89E-13 |
5.26E-08 |
Respiratory effects |
kg PM2.5 eq |
2.16E-04 |
7.15E-05 |
5.00E-09 |
2.88E-04 |
Additional environmental information |
|||||
Ecotoxicity |
CTUe |
2.32E-01 |
2.08E-02 |
6.15E-06 |
2.52E-01 |
Fossil fuel depletion |
MJ surplus |
9.08E+00 |
6.23E-01 |
5.18E-05 |
9.71E+00 |