Environmental Product Declaration

Zero Thresholds

Brand: Allegion

Environmental Product Declaration: Zero Thresholds

About Allegion

Allegion is a global pioneer in safety and security, with leading brands like LCN®, Schlage®, Steelcraft® and Von Duprin®. Focusing on security around the door and adjacent areas, Allegion produces a range of solutions for homes, businesses, schools and other institutions. Allegion is a $2 billion company, with products sold in almost 130 countries. As a subsidiary of Allegion plc, Zero International brand is recognized as the standard for quality in door sealing hardware. Their perimeter seals and thresholds are engineered for durability and reliable performance even under the most challenging installation and operating conditions. They also support green building applications by promoting heating and cooling efficiency.

Allegion is pioneering safety by protecting people where they live and work – and protecting our environment at the same time. We promote the health and safety of our employees, customers and local community members worldwide through our commitment to conducting business in a safe and environmentally responsible manner. Additionally, Allegion recognizes the value of the Leadership in Energy and Environmental Design (LEED) rating system to building environmentally safe and sustainable structures. By using Life Cycle Assessment and Environmental Product Declarations, we aim to provide our customers with the information they need to make decisions regarding their own sustainable building concepts and green solutions. At Allegion, we value the importance of a cleaner world and are committed to being a responsible member of our global communities.

Product Identification

Zero thresholds are designed primarily to close the gap between the floor and the bottom of a door. This helps keep external elements like air, water, snow, and pests from entering the indoors. The threshold works in conjunction with other products such as weatherstripping and door bottoms to help protect the indoors. Zero thresholds feature top-quality materials and construction, designed to stand up to the demands of heavy traffic applications as well as those with extreme temperature differentials.

Table 1: Product Specification

Threshold ModelLength (mm)Height (mm)
65A Rabbeted thresholds-standard127.012.7
545A Saddle thresholds127.06.4
656A Saddle thresholds152.412.7
625A Thermal break thresholds127.012.7

For a complete list of products, see Zero's Door Sealing Systems product catalog.

Application and Standards

Application

Zero thresholds are designed to be used in commercial applications such as health care, education, hospitality, and retail. The product can also be used residentially if desired.

Table 2: BHMA Standards

Threshold ModelANSI/BHMA
65A Rabbeted thresholds-standardJ36100, J36130
545A Saddle thresholdsJ32100, J32130
656A Saddle thresholdsJ32100, J32130
625A Thermal break thresholds-

* All Zero thresholds are designed for heavy-duty applications and far exceed BHMA A156.22 cycle test and force test requirements for Grade 1.

Declaration of Methodological Framework

This particular LCA is a cradle-to-gate with options LCA. A summary of the life cycle stages can be found in Table 11. The cut-off criteria are described in Section 0 and allocation procedures are described in Section 2.8. No known flows are deliberately excluded from this EPD.

Technical Data

ParameterStandardValue/Testing Result
FIRE RATED-UL10CANSI/UL 10CPass
ADA ACCESSIBLEICC/ANSI A117.1Pass

This chart illustrates the most common types of threshold classifications.

Properties of Declared Product as Delivered

For shipping, all thresholds are packaged individually in cardboard boxes. Along with the threshold, an instruction manual, labels and screw bag are also included.

Material Composition and Manufacturing

Material Composition

Table 4: Material Composition

ComponentMaterialMass %
ProductNeoprene88.8–98.8%
Silicone0.0–3.8%
PVC0.0–8.3%
FastenersSteel1.2–2.9%

Manufacturing

Zero threshold products are manufactured at Allegion's Indianapolis plant, located at 2720 Tobey Dr, Indianapolis, IN 46219. Allegion receives metal sub-components from their suppliers in the US and China. These components are then assembled, finished and packaged in the facility in Indianapolis. Along with the threshold, an instruction manual, labels and a screw bag are also included in cardboard boxes. Product is shipped to customers via UPS or LTL carriers. Natural resources used in the manufacturing process include electricity, natural gas and water. Steel waste is also generated as parts of the product are formed, sheared and assembled. All steel waste is collected and recycled offsite.

Packaging and Transportation

Packaging

Table 5: Packaging

Packaging TypeMaterialAmount (kg)Disposal Pathway
Screw pack bagPolypropylene0.001Landfilled (68%), Incinerated (17%), Recycled (15%)
Plastic sleevePolypropylene0.010Landfilled (68%), Incinerated (17%), Recycled (15%)
Instruction sheetPaper0.040Landfilled (20%), Incinerated (5%), Recycled (75%)

Transportation

It is assumed that all raw materials are distributed by truck, based on global region. An average distance using this information was calculated and used in the model. An average shipping distance from the manufacturing location to the customer was utilized and was calculated from sales records. The transportation distance for all waste flows is assumed to be 161 km based on best available data.

Installation, Reuse, Recycling, and Disposal

Product Installation

Detailed installation instructions can be found online. While installation equipment is required to install the product, it is not included in the study as these are multi-use tools and the impacts per declared unit is considered negligible. All waste generated during installation, including packaging waste, is disposed of according to the tables found in Section 2.8.5 of Part A: Life Cycle Assessment Calculation Rules and Report Requirements from UL Environment.

Reuse, Recycling, and Energy Recovery

Zero threshold products may be recycled or reused at the end of life. The LCA that this EPD is created from takes the conservative approach by assuming that all products are disposed of within the system boundary.

Disposal

Disposal pathways in the EPD are modeled in accordance with disposal routes and waste classification referenced in Sections 2.8.5 and 2.8.6 of Part A: Life Cycle Assessment Calculation Rules and Report Requirements from UL Environment. This indicates an end-of-life split amongst landfill, recycling, and incineration pathways.

Life Cycle Assessment Background Information

Declared Unit

The declared unit is one threshold per standard doorleaf, as indicated in Table 6.

NameValueUnit
Declared Unit1 threshold per standard door leaf
Mass per Declared Unit, excluding fasteners1.170kg
Fasteners0.010kg

System Boundary

The type of EPD is cradle-to-gate with options. All LCA modules are included and are summarized in Table 7.

Module NameDescriptionAnalysis PeriodSummary of Included Elements
A1Product Stage: Raw Material Supply2018Raw Material sourcing and processing as defined by secondary data.
A2Product Stage: Transport2018Shipping from supplier to manufacturing site. Fuel use requirements estimated based on product weights and estimated distance.
A3Product Stage: Manufacturing2018Energy, water and material inputs required for manufacturing products from raw materials. Packaging materials and manufacturing waste are included as well.
A4Construction Process Stage: Transport2018Shipping from manufacturing site to project site. Fuel use requirements estimated based on product weights and mapped distance.
A5Construction Process Stage: Installation2018Installation materials, installation waste and packaging material waste.
B1Use Stage: UseMNDModule not declared
B2Use Stage: MaintenanceMNDModule not declared
B3Use Stage: RepairMNDModule not declared
B4Use Stage: ReplacementMNDModule not declared
B5Use Stage: RefurbishmentMNDModule not declared
B6Operational Energy UseMNDModule not declared
B7Operational Water UseMNDModule not declared
C1EOL: Deconstruction2018No inputs required for deconstruction.
C2EOL: Transport2018Shipping from project site to landfill. Distance assumed to be 100 miles from installation site to landfill.
C3EOL: Waste Processing2018Waste processing not required. All waste can be processed as is.
C4EOL: Disposal2018Assumes all products are sent to landfill. Landfill impacts modeled based on secondary data.
DBenefits beyond systemMNDModule not declared

Estimates and Assumptions

All estimates and assumptions are within the requirements of ISO 14040/44. The majority of the estimations are within the primary data. The primary data was collected as annual totals including all utility usage and production information. For the LCA, the usage information was divided by the production to create an energy and water use per declared unit, i.e., one threshold. Another assumption is that the installation tools are used enough times that the per threshold impacts are negligible.

Cut-off Criteria

All inputs in which data was available were included. Material inputs greater than 1% (based on total mass of the final product) were included within the scope of analysis. Material inputs less than 1% were included if sufficient data was available to warrant inclusion and/or the material input was thought to have significant environmental impact. Cumulative excluded material inputs and environmental impacts are less than 5% based on total weight of the functional unit.

Data Sources, Quality, and Allocation

Data Sources

Primary data were collected by facility personnel and from utility bills and was used for all manufacturing processes. Whenever available, supplier data was used for raw materials used in the production process. When primary data did not exist, secondary data for raw material production was utilized from GaBi Database Version 9.2.0.58, Service pack 39.

Data Quality

Geographical Coverage

The geographical scope of the manufacturing portion of the life cycle is Indianapolis, Indiana. This LCA uses country specific energy datasets that take into account US eGrid specific energy and transportation mixes. Overall, the geographic coverage of primary data is considered good.

Time Coverage

Primary data were provided by Allegion associates and represent calendar year 2018. Using 2018 data meets the PCR requirement that manufacturer specific data be within the last 5 years. Time coverage of this data is considered good. Data necessary to model cradle-to-gate unit processes was sourced from thinkstep LCI datasets. Time coverage of the GaBi datasets varies from approximately 2010 to present. All datasets rely on at least one 1-year average data. Overall time coverage of the datasets is considered good and meets the requirement of the PCR that all data be updated within a 10-year period. The specific time coverage of secondary datasets can be referenced in the dataset references table in each supplemental LCA report.

Technological Coverage

Primary data provided by Allegion are specific to the technology that the company uses in manufacturing their product. It is site specific and considered of good quality. It is worth noting that the energy and water used in manufacturing the product includes overhead energy such as lighting, heating and sanitary use of water. Sub-metering was not available to extract process only energy and water use from the total energy use. Sub-metering would improve the technological coverage of data quality. Data necessary to model cradle-to-gate unit processes was sourced from thinkstep LCI datasets. Technological coverage of the datasets is considered good relative to the actual supply chain of Allegion. While improved life cycle data from suppliers would improve technological coverage, the use of lower quality generic datasets does meet the goal of this EPD.

Period under Review

The period under review is calendar year 2018.

Allocation

General principles of allocation were based on ISO 14040/44. Where possible, allocation was avoided. When allocation was necessary it was done on a physical mass basis. Allocation was most prevalent in the secondary GaBi datasets used to represent upstream processes. As a default, GaBi datasets use a physical mass basis for allocation.

Life Cycle Assessment Scenarios

Table 8: Transport to the Building Site (A4)

NameValueUnit
Fuel typeDiesel
Liters of fuel39.0625l/100km
Vehicle typeTruck
Transport distance621.30km
Capacity utilization0.65%
Gross density of products transported221.71kg/m³
Capacity utilization volume factor1-

Table 9: Installation into the Building (A5)

NameValueUnit
Fasteners0.01kg
Product loss per functional unit0kg
Waste materials at the construction site before waste processing, generated by product installation0kg
Direct emissions to ambient air, soil and water0kg
VOC emissionsN/Aµg/m³

Table 10: End of Life (C1-C4)

NameValueUnit
Collection processCollected separately0kg
Collected with mixed construction waste1.191kg
RecoveryReuse0kg
Recycling1.012kg
Landfill0.178kg
Incineration0kg
DisposalProduct or material for final deposition0.178kg

Life Cycle Assessment Results

Table 11: Description of the System Boundary Modules

PRODUCT STAGECONSTRUCTION PROCESS STAGEUSE STAGEEND OF LIFE STAGEBENEFITS AND LOADS BEYOND THE SYSTEM BOUNDARY
A1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4D
Raw material supplyTransportManufacturingTransport from gate to siteAssembly/InstallUseMaintenanceRepairReplacementRefurbishmentBuilding Operational Energy UseBuilding Operational Water UseDeconstructionTransportWaste processingDisposalReuse, Recovery, Recycling
Cradle to Gate with OptionsXXXXXMNDMNDMNDMNDMNDMNDMNDXXXXMND

Life Cycle Impact Assessment Results

Table 12: CML Results

CML v4.2A1-A3A4A5B1B2B3B4B5B6B7C1C2C3C4D
ADP-elements [kg Sb eq]-8.50E-061.81E-08-3.00E-10MNDMNDMNDMNDMNDMNDMND0.00E+002.77E-090.00E+003.09E-090.00E+00
ADP-fossil fuel [MJ]1.95E+021.34E+00-1.58E-02MNDMNDMNDMNDMNDMNDMND0.00E+002.05E-010.00E+001.16E-010.00E+00
AP [kg SO2 eq]5.11E-023.22E-041.51E-05MNDMNDMNDMNDMNDMNDMND0.00E+002.98E-050.00E+003.17E-050.00E+00
EP [kg Phosphate eq]3.74E-039.07E-058.95E-06MNDMNDMNDMNDMNDMNDMND0.00E+008.59E-060.00E+007.24E-060.00E+00
GWP [kg CO2 eq]1.56E+019.65E-021.41E-02MNDMNDMNDMNDMNDMNDMND0.00E+001.46E-020.00E+007.50E-030.00E+00
ODP [kg CFC 11 eq]2.27E-089.00E-18-5.63E-18MNDMNDMNDMNDMNDMNDMND0.00E+001.38E-180.00E+002.72E-170.00E+00
POCP [kg Ethene eq]3.00E-03-4.59E-055.37E-06MNDMNDMNDMNDMNDMNDMND0.00E+00-4.47E-060.00E+002.81E-060.00E+00

Table 13: TRACI Results

TRACI v2.1A1-A3A4A5B1B2B3B4B5B6B7C1C2C3C4D
AP [kg SO2 eq]4.96E-024.37E-042.65E-05MNDMNDMNDMNDMNDMNDMND0.00E+003.94E-050.00E+004.16E-050.00E+00
EP [kg N eq]2.46E-033.65E-057.16E-06MNDMNDMNDMNDMNDMNDMND0.00E+003.83E-060.00E+004.67E-060.00E+00
GWP [kg CO2 eq]1.55E+019.65E-021.35E-02MNDMNDMNDMNDMNDMNDMND0.00E+001.46E-020.00E+007.46E-030.00E+00
ODP [kg CFC 11 eq]2.47E-08-5.11E-161.51E-16MNDMNDMNDMNDMNDMNDMND0.00E+00-7.82E-170.00E+00-3.92E-160.00E+00
Resources [MJ]2.02E+011.79E-01-4.82E-04MNDMNDMNDMNDMNDMNDMND0.00E+002.74E-020.00E+001.49E-020.00E+00
SFP [kg O3 eq]5.41E-011.02E-021.54E-04MNDMNDMNDMNDMNDMNDMND0.00E+008.84E-040.00E+006.87E-040.00E+00

Table 14: Resource Use

IMPACT CATEGORYA1-A3A4A5B1B2B3B4B5B6B7C1C2C3C4D
PERE [MJ]4.39E+014.17E-02-4.53E-03MNDMNDMNDMNDMNDMNDMND0.00E+006.39E-030.00E+009.09E-03MND
PERM [MJ]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
PENRE [MJ]2.19E+021.35E+00-2.48E-02MNDMNDMNDMNDMNDMNDMND0.00E+002.06E-010.00E+001.19E-01MND
PENRM [MJ]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
SM [kg]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
RSF [MJ]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
NRSF [MJ]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
RE [MJ]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
FW [m³]1.89E-011.62E-044.49E-06MNDMNDMNDMNDMNDMNDMND0.00E+002.48E-050.00E+001.42E-05MND

Table 15: Output Flows and Waste Categories

IMPACT CATEGORYA1-A3A4A5B1B2B3B4B5B6B7C1C2C3C4D
HWD [kg]1.30E-021.09E-081.10E-10MNDMNDMNDMNDMNDMNDMND0.00E+001.67E-090.00E+004.18E-10MND
NHWD [kg]2.22E+005.08E-051.63E-02MNDMNDMNDMNDMNDMNDMND0.00E+007.77E-060.00E+001.70E-01MND
HLRW [kg]1.13E-053.60E-09-4.21E-09MNDMNDMNDMNDMNDMNDMND0.00E+005.52E-100.00E+001.45E-09MND
ILLRW [kg]9.23E-032.98E-06-3.52E-06MNDMNDMNDMNDMNDMNDMND0.00E+004.56E-070.00E+001.15E-06MND
CRU [kg]0.00E+000.00E+000.00E+00MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
R [kg]0.00E+000.00E+003.59E-02MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+009.64E-010.00E+00MND
MER [kg]0.00E+000.00E+004.43E-03MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND
EE [MJ]0.00E+000.00E+001.08E-02MNDMNDMNDMNDMNDMNDMND0.00E+000.00E+000.00E+000.00E+00MND

LCA Interpretation

LCA Interpretation

The dominance analysis shows that the Production Stage (A1-A3) of the life cycle is responsible for the vast majority of impacts across all impact categories. Specifically, phases A1-A3 contributes the most to ADP-fossil through electricity and thermal energy used during manufacturing. The resources used to extract, and process (electricity and thermal energy) steel and aluminum mainly contribute to the impacts in the A1-A3 module. Transportation to customer (A4) and installation (A5) stages have second and third highest ADP-fossil impacts respectively. This is mainly due to fuels used for transportation to customer and steel fasteners used to install the product.

Additional Environmental Information

Environment and Health During Manufacturing

Allegion meets all federal and state standards related to the Environment and Health during manufacturing. Additionally, Allegion employs a strict waste minimization and recycling program that reduces and recycles waste produced in the manufacturing process. Beyond what is regulated, there are no additional environment and health considerations during the production of goods.

Environment and Health During Use

There are no environmental or health considerations during the use of the product.

Supporting Documentation

Table 16: Acronym Key

ACRONYMTEXTLCA IndicatorsACRONYMTEXT
ADP-elementsAbiotic depletion potential for non-fossil resourcesGWPGlobal warming potential
ADP-fossilAbiotic depletion potential for fossil resourcesOPDDepletion of stratospheric ozone layer
APAcidification potential of soil and waterPOCPPhotochemical ozone creation potential
EPEutrophication potentialResourcesDepletion of non-renewable fossil fuels
LCI Indicators
PEREUse of renewable primary energy excluding renewable primary energy resources used as raw materialsPENRTTotal use of non-renewable primary energy resources (primary energy and primary energy resources used as raw materials)
PERMUse of renewable primary energy resources used as raw materialsSMUse of secondary materials
PERTTotal use of renewable primary energy resources (primary energy and primary energy resources used as raw materials)RSFUse of renewable secondary fuels
PENREUse of non-renewable primary energy excluding non-renewable primary energy resources used as raw materialsNRSFUse of non-renewable secondary fuels
PENRMUse of non-renewable primary energy resources used as raw materialsFWNet use of fresh water
HWDDisposed-of-hazardous wasteMFRMaterials for recycling
NHWDDisposed-of non-hazardous wasteMETMaterials for energy recovery
RWDDisposed-of Radioactive wasteEEEExported electrical energy
CRUComponents for reuseEETExported thermal energy

References

  1. Life Cycle Assessment, Allegion, LCA report for Zero Gasketing and Thresholds. WAP Sustainability Consulting. April 2020.
  2. Product Category Rule (PCR) for preparing an Environmental Product Declaration (EPD) for Product Group Builders Hardware (UL 9004). Version: April 3rd, 2014
  3. ISO 14044: 2006 Environmental Management – Life cycle assessment – Requirements and Guidelines.
  4. ISO 14025: 2006 Environmental labels and declarations – Type III environmental declarations – Principles and Procedures.
  5. ISO 21930: 2007 - Sustainability in building construction -- Environmental declaration of building products
  6. EN 15804: 2012-04 - Sustainability of construction works — Environmental Product Declarations for the product category of construction product. Core rules

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