LCA & material health results & interpretation EcoPower® Toilet Flush Valve TET1UA
Scope and summary
- Cradle to gate
- Cradle to gate with options
- Cradle to grave
Functional unit
One flush valve for toilets in an average U.S. commercial environment for 10 years. The period of 10 years is modeled as the period of application based on the average technical lifespan for commercial applications. The economical lifespan of commercial applications can be longer or shorter due to aesthetic replacements or more intense use. The implication is that the LCA model assumes that the application ends at year 10 and that the materials will be treated in an end-of-life scenario.
Reference service life: 10 years
Data reporting period: 2016
Default use phase scenario
10 years of service in an average U.S. commercial environment in combination with a toilet with 1.0 gallon/use, 51 uses/day, and 260 days/year resulting in 132,600 gallons of water.
What’s causing the greatest impacts
All life cycle stages
The use and production stages are both important and dominate the results for all impact categories. The impact of the use stage is mostly due to the embedded energy arising from acquisition, treatment and distribution of the water used during the use of the toilet for which the valves are installed. The production stage itself has a significant contribution to eutrophication (mostly from emissions from copper mining), non-carcinogens (emissions from the production of coal, copper and zinc) and ecotoxicity (mostly from the disposal of steel slags and bottom ashes, as well as from barium emissions to water due to the extraction processes of natural gas).
The recovery stage includes recycling processes and benefits by preventing the need to produce primary materials. Recycling is a relevant factor for some of the impact categories, offsetting a portion of the impacts caused by production. Additionally, the delivery of the product to the construction/installation site, the construction/installation processes, the processes for dismantling the product and final waste treatment during the end of life stage do not have a significant impact.
Production stage
Bronze and stainless steel parts, together with the printed wiring board, have significant contributions to the impact categories. The stainless steel material is relevant to the carcinogenics category. The electroplating process is a major contributor to the ozone depletion category while the die casting process is relevant to the ecotoxicity and non-carcinogenics categories. Additionally, polishing and potting have a somewhat significant processing contribution to the results. Transport via oceanic freighter appears as a relevant contributor to the fossil fuel depletion and smog categories. The remaining parts and processes contribute between 3% and 15% to the overall impacts in the rest of the categories.
Sensitivity analysis
There are no sensitivity results that lead to variations greater than 10% in the LCA results.
TOTO PeoplePlanetWater™ programs improving environmental performance
- TOTO’s EcoPower® products are powered by the force of running water.
- The electronic and mechanical components are programmed and designed to allow water flow and accurate flush volume only when needed.
- Water consumption is reduced in the use phase due to superior flushing performance.
LCA results
Life cycle stage | Production | Construction | Use | End of Life | Recovery |
Information modules: Included | Excluded Reuse and energy recovery are not modeled for sanitary fittings. |
A1 Raw Materials | A4 Transportation/ Delivery | B1 Use | C1 Deconstruction/ Demolition | D Reuse, recovery and/or recycling |
A2 Transportation | A5 Construction/ Installation | B2 Maintenance | C2 Transportation | ||
A3 Manufacturing | B3 Repair | C3 Waste processing | |||
B4 Replacement | C4 Disposal | ||||
B5 Refurbishment | |||||
B6 Operational energy use | |||||
B7 Operational water use | |||||
SM Single Score
Learn about SM Single Score resultsImpacts per 10 years of service | 31.81 mPts | 0.14 mPts | 32.38 mPts | 0.02 mPts | -1.50 mPts |
Materials or processes contributing >20% to total impacts in each life cycle stage | Bronze and zinc parts together with the printed wiring board in addition to manufacturing processes such as die casting and electroplating. | Transportation of the product to installation site or consumer and disposal of packaging. | Volume of water use during the operation of the product and the embedded energy use (such as electricity) in the water used. | Transport to waste processing, waste processing and disposal of material flows transported to a landfill. | Plastic and metal components' recycling processes. |
TRACI v2.1 results per one flush valve
Life cycle stage | Production | Construction | Use | End of Life | Recovery |
Ecological damage
Human health damage
Resources depletion
Impact category | Unit | |||||
Fossil fuel depletion | MJ surplus Mega Joule surplus Fossil fuel depletion is the surplus energy to extract minerals and fossil fuels. |
4.67E+01 | 2.33E+00 | 2.07E+02 | 4.52E-01 | -4.57E+00 |
References
LCA Background Report
TOTO Sanitary Fittings Products LCA Background Report (public version), September 2017
SM Transparency Report Framework
Part A: LCA Calculation Rules and Background Report Requirements v2017 (compliant with ISO14040-44 and ISO14025)
Part B: Product Group Definition – Commercial Flushometer Valves
Transparency Reports™ / environmental product declarations enable purchasers and users to compare the potential environmental performance of products on a life cycle basis. They are designed to present information transparently to make the limitations of comparability more understandable. 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.