LCA & material health results & interpretation SonaSpray “fc”
Scope and summary
- Cradle to gate
- Cradle to gate with options
- Cradle to grave
Application
SonaSpray “fc” is a spray applied acoustical texture designed for a wide range of project types. SonaSpray “fc” provides an attractive, high performance solution to acoustical and lighting design objectives in both new construction and renovation projects.
Functional unit
Reference service life: 75 years. One square meter of installed insulation material, packaging included, with a thickness that gives an average thermal resistance of RSI=1m2·K/W over a period of 75 years.
Reference flow: 4.252 kg of product
Thickness: 0.0483 m
Manufacturing data
Reporting period: January 2018-December 2018
Location: Houston, TX
Default installation, packaging, and disposal scenarios
At the installation site, insulation products are unpackaged and installed with a blowing machine. The insulation blower is used to spray on the fiber and adhesive. The potential impact of the blower is included in this study. Plastic packaging waste is disposed (100% to landfill), and no maintenance or replacement is required to achieve the product's life span. 207,546 kWh of electricity and 1,377,032 kg of water are used annually for installation. After removal, the insulation is assumed to be landfilled.
What’s causing the greatest impacts
All life cycle stages
The raw material acquisition and manufacturing stages (A1-A3) dominate the results for all impact categories except for ozone depletion, non-carcinogenics, and smog. The transportation stage dominates for the ozone depletion and non-carcinogenics categories while the construction and installation stage dominates the smog category. Following the raw material acquisition and manufacturing stage and the transportation stage, the next highest impacts come from the construction and installation stage (A5), which have a similar contribution.
Data used for this project represents a mix of primary data collected from ICC on the production of the insulation products (gate-to-gate) and background data from SimaPro databases. Overall, the quality of the data used in this study is considered to be high and representative of the described systems. Data on processing materials and manufacturing the insulation products were collected in a consistent manner and level of detail to ensure high quality data. All submitted data were checked for quality multiple times on the plausibility of inputs and outputs. All questions regarding data were resolved with ICC. Data were collected at ICC’s Houston, TX facility.
No substances required to be reported as hazardous are associated with the production of this product. This is a product free of Red List ingredients.
Raw materials acquisition and manufacturing stage
The impact of the raw material acquisition and manufacturing stages are mostly due to the raw material ingredients. Some raw material ingredients such as boric acid and ethylene vinyl acetate copolymer (data set used for PVA) have slightly higher impacts than other ingredients. This is because of the high material weights used in manufacturing.
How we're making it greener
ICC has energy, waste and water management policies in place and subscribes to third-party environmental services, which includes inspections, audits, and environmental monitoring.
Water management: Water is utilized only in the manufacturing of the adhesives- which are produced in concentrated form and diluted at the job site. No wastewater is generated from the manufacturing process.
Waste management: ICC practices onsite recycling and has partnered with local business to reduce and reuse packaging materials.
Energy management: Products are manufactured in an electrically driven mill, using a process that requires low embodied energy. Electricity use is monitored and processes to conserve energy have been instilled. These products and the manufacturing of these products does not use ozone depleting substances such as CFC’s or HCFC’s; ozone depletion may occur in the transportation phase or raw material extraction phase.
LCA results
Life cycle stage | Raw material acquisition and manufacturing | Transportation | Installation and maintenance | Transportation | Disposal/reuse/ recycling |
Information modules: Included | Stages C1, C3, and D are being excluded *In the installation and maintenance phase, packaging waste and electricity or gas used by the insulation blowing machines in module A5 are the only contributors to the potential impacts. |
A1 Raw Materials | A4 Transporation/ Delivery | A5 Construction/ Installation | C2 Transportation | C4 Disposal |
A2 Transportation | B1 Use | ||||
A3 Manufacturing | B2 Maintenance | ||||
B3 Repair | |||||
B4 Replacement | |||||
B5 Refurbishment | |||||
B6 Operational energy use | |||||
B7 Operational water use | |||||
SM Single Score
Learn about SM Single Score resultsImpacts per 75 years of service | 1.96E-04 mPts | 1.13E-04 mPts | 4.94E-05 mPts | 1.10E-07 mPts | 3.21E-06 mPts |
Materials or processes contributing >20% to total impacts in each life cycle stage | boric acid and ethylene vinyl acetate copolymer used in the production of the insulation. | Truck and trailer, 53ft used to transport product to building site. | Transportation to disposal, energy required for installation with a blowing machine, and disposing of packaging materials. | Transportation to landfill. | Landfilling of product. |
TRACI v2.1 results per functional unit
Life cycle stage | Raw material acquisition and manufacturing | Transportation | Installation and maintenance | Transportation | Disposal/reuse/ recycling |
Ecological damage
Human health damage
Additional environmental information
Impact category | Unit | |||||
Fossil fuel depletion | MJ surplus Mega Joule, lower heating value Fossil fuel depletion is the surplus energy to extract minerals and fossil fuels. |
6.87E+00 | 2.42E+00 | 1.15E+00 | 2.37E-03 | 1.15E-01 |
USEtox percent contribution
Life cycle stage | Raw material acquisition and manufacturing | Transportation | Installation and maintenance | Transportation | Disposal/reuse/ recycling |
References
LCA Background Report
ICC Insulation Products LCA Background Report (public version), ICC 2020. SimaPro Analyst 8.5.2.0, Ecoinvent 3.1, 2.2 database.
PCRs
ISO 21930:2017 serves as the core PCR along with EN 15804 and UL Part A.
ULE PCR Part A: Life Cycle Assessment Calculation Rules and Report Requirements v3.1
May 2, 2018. Technical Advisory Panel members reviewed and provided feedback on content written by UL Environment and USGBC. Past and present members of the Technical Advisory Panel are listed in the PCR.
ULE PCR Part B: Building Envelope Thermal Insulation
Version 2.0, April 2018. PCR review conducted by Thomas Gloria, PhD (chair, [email protected]); Andre Desjarlais; and Christoph Koffler, PhD.
ULE General Program Instructions v2.1, April 2017
ISO 14025, “Sustainability in buildings and civil engineering works -- Core rules for environmental product declarations of construction products and services”, ISO21930:2017
Download PDF SM Transparency Report/Material Health Overview, which includes the additional EPD content required by the UL Environment PCR.
SM Transparency Reports (TR) are ISO 14025 Type III environmental declarations (EPD) that enable purchasers and users to compare the potential environmental performance of products on a life cycle basis. Environmental declarations from different programs (ISO 14025) may not be comparable. They are designed to present information transparently to make the limitations of comparability more understandable. Limitations of LCA results for the products represent production volumes for the Houston, TX facility only. TRs/EPDs of products that conform to the same PCR and include the same life cycle stages, but are made by different manufacturers, may not sufficiently align to support direct comparisons. They therefore, cannot be used as comparative assertions unless the conditions defined in ISO 14025 Section 6.7.2. ‘Requirements for Comparability’ are satisfied. Comparison of the environmental performance of building envelope thermal insulation using EPD information shall be based on the product’s use and impacts at the building level, and therefore EPDs may not be used for comparability purposes when not considering the building energy use phase as instructed under the PCR. Environmental declarations from different programs based upon differing PCRs may not be comparable. Full conformance with the PCR for building envelope thermal insulation allows EPD comparability only when all stages of a life cycle have been considered, when they comply with all referenced standards, use the same sub-category PCR, and use equivalent scenarios with respect to construction works. Compliance with model building codes does not always ensure compliance with state or local building codes, which may be amended versions of these model codes. Always check with local building code officials to confirm compliance. However, variations and deviations are possible. Example of variations: Different LCA software and background LCI data sets may lead to different results upstream or downstream of the life cycle stages declared.