Carbozinc 859 VOC

Environmental Impact

Product Details

Description

Ultra-low VOC organic zinc epoxy steel primer with extremely fast cure-to-topcoat characteristics for in-shop applications and quick turnaround requirements in the field. Carbozinc 859 VOC has less than 100 g/l VOC (thinned) and can be used in virtually all industrial markets.

EPD PDF Document

ENVIRONMENTALPRODUCT DECLARATIONIN ACCORDANCE WITH ISO 14025 AND ISO 21930:2007SmartEPD-2024-037-0178-01Carbo���� �59 VOCDate of Issue:Oct 15, 2024Exp�rat�o�:Oct 15, 2029Last updated:Oct 15, 2024

Carbo���� �59 VOCCarbolineGe�eral I�format�o�4Refere��e Sta�dards4Ver�fi�at�o� I�format�o�5L�m�tat�o�s, L�ab�l�ty, a�d Ow�ersh�p5Orga���at�o� I�format�o�5Produ�t I�format�o�5Pla�ts6Produ�t Spe��fi�at�o�s6Mater�al Compos�t�o�6Software a�d LCI Data Sour�es7EPD Data Spe��fi��ty7Re�ewable Ele�tr���ty8System Bou�dary8Produ�t Flow D�agram9L�fe Cy�le Module Des�r�pt�o�s9LCA D�s�uss�o�9Results11E�v�ro�me�tal Impa�t Assessme�t11Resour�e Use I�d��ators13Waste a�d output Flow I�d��ators14Carbo� Em�ss�o�s a�d Removals15S�e�ar�os16Tra�sport to the bu�ld��g/�o�stru�t�o� s�te (A4)16I�stallat�o� �� to the bu�ld��g/�o�stru�t�o� s�te (A5)16Refere��e Serv��e L�fe (B1)16Repla�eme�t (B4)17Page 2 / 18

Carbo���� �59 VOCCarbolineE�d of L�fe (C1 - C4)17I�terpretat�o�17Add�t�o�al E�v�ro�me�tal I�format�o�18Refere��es18Page 3 / 18

Carbo���� �59 VOCCarbolineGe�eral I�format�o� Carboline 2150 Schuetz Rd, St. Louis, MO 63146 USA1-800-848-4645info@carboline.com�arbol��e.�omProdu�t Name:Carbozinc 859 VOCFu��t�o�al U��t:1 m2 of covered and protected substrate for 60 years per coat, reference flow depends on service lifeDe�larat�o� Number:SmartEPD-2024-037-0178-01Date of Issue:October 15, 2024Exp�rat�o�:October 15, 2029Last updated:October 15, 2024EPD S�ope:Cradle to graveA1 - A3, A4, A5, B1 - B7, C1 - C4 Market(s) of Appl��ab�l�ty:North AmericaRefere��e Sta�dardsSta�dard(s):ISO 14025 and ISO 21930:2007Core PCR:NSF PCR for Architectural Coatings v.1Date of issue: June 18, 2015Valid until: June 30, 2024Sub-�ategory PCR rev�ew pa�el:Contact Smart EPD for more information.Ge�eral Program I�stru�t�o�s:Smart EPD General Program Instructions v.1.0, November 2022Page 4 / 18

Carbo���� �59 VOCCarbolineVer�fi�at�o� I�format�o�LCA Author/Creator:Juan David Villegasjuan@parqhq.comEPD Program Operator:Smart EPDinfo@smartepd.comwww.smartepd.com585 Grove St., Ste. 145 PMB 966, Herndon, VA 20170, USAVer�fi�at�o�: Independent critical review of the LCA and data, according to ISO 14044 and ISO 14071 : External Ranjani TheregowdaSmart EPD LLCranjani.theregowda@smartepd.com Independent external verification of EPD, according to ISO 14025 and reference PCR(s) : External Ranjani TheregowdaSmart EPD LLCranjani.theregowda@smartepd.comL�m�tat�o�s, L�ab�l�ty, a�d Ow�ersh�p Environmental declarations from different programs (ISO 14025) may not be comparable. Comparison of the environmental performance of products 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 whole building life cycle. EPD comparability is only possible when all stages of a life cycle have been considered. However, variations and deviations are possible. Example of variations: Different LCA software and background LCI datasets may lead to differences results for upstream or downstream of the life cycle stages declared. The EPD owner has sole ownership, liability, and responsibility for the EPD. Orga���at�o� I�format�o� For over seven decades, Carboline has been at the forefront of delivering cutting-edge product development alongside a wealth of technical expertise and experience, offering unparalleled protective coating solutions on a global scale. As a notable manufacturer of paint and coating products, Carboline is dedicated to showcasing its sustainability leadership while recognizing the business value in transparently reporting the comprehensive environmental impacts of its products, spanning from cradle to grave. Further ��format�o� �a� be fou�d at:www.�arbol��e.�omProdu�t Des�r�pt�o� Ultra-low VOC organic zinc epoxy steel primer with extremely fast cure-to-topcoat characteristics for in-shop applications and quick turnaround requirements in the field. Carbozinc 859 VOC has less than 100 g/l VOC (thinned) and can be used in virtually all industrial markets. Further ��format�o� �a� be fou�d at:https://www.�arbol��e.�om/produ�ts/produ�t-deta�ls/Carbo����-�59-vo�Produ�t I�format�o�Fu��t�o�al U��t:1 m2 of covered and protected substrate for 60 years per coat, reference flow depends on service lifeMass:0.483 kgRefere��e Serv��e L�fe:60 YearsPage 5 / 18

Carbo���� �59 VOCCarbolineProdu�t Spe��fi��ty:Product AverageProduct SpecificPla�tsCarboline - Lake Charles2425 Fruge Street, Lake Charles, LA, USAProdu�t Spe��fi�at�o�sProdu�t SKU(s):04810300904DProdu�t Class�fi�at�o� Codes:EC3 - Finishes -> PaintingAndCoating -> PaintByAreaAr�h�te�tural Coat��g Sub�ategory:Exterior Architectural CoatingQual�ty Des�g�at�o�:High QualityDes�g� L�fe:20 yearsMarket-Based L�fet�me:10 yearsI�dustry Durab�l�ty Test:ISO 12944-6Amou�t of Colora�t Needed per L�ter of Coat��g:0 mlMater�al Compos�t�o�Material/Component CategoryOrigin% MassZinc dustVarious63 - 83AdditivesUSA< 10PigmentUSA< 10ResinMEX< 10SolventUSA< 10Packaging MaterialOriginkg Masssteel pailUSA0.0511Page 6 / 18

Carbo���� �59 VOCCarbolineHazardous Materials2-PIPERAZIN-1-YLETHYLAMINE (140-31-8)BENZYL ALCOHOL (100-51-6)BISPHENOL A EPOXY RESIN (25068-38-6)EPOXY RESIN (25036-25-3)ISOPROPANOL (67-63-0)METHYLENEOXIDE, POLYMER WITH BENZENAMINE HYDROGENATED (135108-88-2)MODIFIED UREA-FORMALDEHYDE RESIN (PROPRIETARY)N-BUTANOL (71-36-3)PARACHLOROBENZO TRIFLUORIDE (98-56-6)POLYSTYRENE (9003-53-6)TERT-BUTYL ACETATE (540-88-5)TOLUENE (108-88-3)TRIS-2,4,6-(DIMETHYLAMINOMETHYL) PHENOL (90-72-2)ZINC (DUST OR FUME) (7440-66-6)ZINC OXIDE (1314-13-2)EPD Data Spe��fi��tyPr�mary Data Year:2022-2023Ma�ufa�tur��g Spe��fi��ty:Industry AverageManufacturer AverageFacility SpecificAverag��g: Averaging was not conducted for this EPD Software a�d LCI Data Sour�esLCA Software:SimaPro v. 9.5LCI Foregrou�d Database(s):Ecoinvent v. 3.9.1LCI Ba�kgrou�d Database(s):Ecoinvent v. 3.9.1Page 7 / 18

Carbo���� �59 VOCCarbolineRe�ewable Ele�tr���tyRe�ewable ele�tr���ty �s used:NoSystem Bou�daryProductionA1Raw material supplyA2TransportA3ManufacturingConstructionA4Transport to siteA5Assembly / InstallUseB1UseB2MaintenanceB3RepairB4ReplacementB5RefurbishmentB6Operational Energy UseB7Operational Water UseEnd of LifeC1DeconstructionC2TransportC3Waste ProcessingC4DisposalBenefits & Loads Beyond System BoundaryDRecycling, Reuse Recovery PotentialNDPage 8 / 18

Carbo���� �59 VOCCarbolineProdu�t Flow D�agramL�fe Cy�le Module Des�r�pt�o�s  Primary data were collected for the 12 month period starting October 2022 and ending September 2023 to ensure technical, geographical and temporal the representativeness. The products in this study are manufactured at Carboline’s facilities in Green Bay (Wisconsin), Lake Charles (Louisiana), and Dayton (Nevada). The manufacturing process entails the addition of pre-weighted ingredients, followed by mixing in the correct sequence to create the desired products. Subsequently, Carboline packages and distributes the finished products to various distribution centers. The process involves the use of grid electricity, heat from natural gas combustion, an process water. Non hazardous waste consisting mainly of packaging material is sent to disposal or recycling. LCA D�s�uss�o� Allo�at�o� Pro�edure Product packaging was allocated by mass. Allocation of co-products was avoided, to the extent it was possible, based on the guidance given in ISO 14044:2006, 4.3., in ISO 21930 and section 5 of NSF International PCR for Architectural Coatings v.1.  Volumetric allocation was applied to energy and water use at the facility level, as it represents the partition among selling units (in gallons). Carboline Global, Inc. provided total volume produced at each facility. Cut-off Pro�edure No cut-off criteria are defined for this study. The system boundary was defined based on relevance to the goal of the study. For the processes within the system boundary, all available energy and material flow data have been included in the model. In cases where no matching life cycle inventories are available to represent a flow, proxy data have been applied based on conservative assumptions regarding environmental impacts. Data Qual�ty D�s�uss�o� Page 9 / 18

Carbo���� �59 VOCCarboline The quality of inventory data is evaluated based on several criteria, including precision, completeness, consistency, and representativeness. Precision and Completeness • Precision: The inventory data used in this study were either directly measured, calculated, or estimated based on primary data sources, ensuring high precision. Background data from ecoinvent v3.9.1 database also has documented precision to the extent available. • Completeness: The product system's mass balance and inventory completeness were thoroughly checked. Some exclusions were made in line with the PCR requirements, such as personnel impacts, R&D activities, business travel, secondary packaging, point of sale infrastructure, and the coating applicator. However, no data was intentionally omitted.. Consistency and Reproducibility • Consistency: Primary data were collected with a similar level of detail, while background data came from the ecoinvent v3.9.1 database. The modeling approach and other methodological choices were applied consistently throughout the model. Default values from the PCR were considered where there was unavailability of primary data, For example, the default waste transport distance was used for product disposal assessment. • Reproducibility: This study ensures reproducibility by providing comprehensive disclosure of input-output data, dataset choices, and modeling approaches. A knowledgeable third party should be able to approximate the results using the same data and modeling methods. Representativeness • Temporal: Primary data were collected for the one-year period of October 2022 to September 2023 to ensure the representativeness of post-consumer content. Secondary data from the ecoinvent v3.9.1 database is typically representative of recent years. • Geographical: Primary data represent Carboline's production facilities in Green Bay (Wisconsin), Dayton (Nevada) and Lake Charles (Louisiana). Where applicable, differences in electric grid mix were considered using appropriate secondary data. The use of country-specific data ensures high geographical representativeness, and proxy data were only used when country-specific data were unavailable. • Technological: Both primary and secondary data were tailored to the specific technologies studied, ensuring high technological representativeness. Where no direct raw material information was available in the ecoinvent 3.9.1 database, proxies were identified and used. Page 10 / 18

Carbo���� �59 VOCCarbolineResultsE�v�ro�me�tal Impa�t Assessme�t ResultsTRACI 2.1per 1 m2 of covered and protected substrate for 60 years.LCIA results are relative expressions and do not predict impacts on category endpoints, the exceeding of thresholds, safety margins or risks.MarketImpa�t CategoryMethodU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4GWP-totalTRACI 2.1kg CO2e1.71e+03.26e-100001.02e+100001.82e-21.05e+01.72e+0ODPTRACI 2.1kg CFC11 eq1.29e-75.39e-900006.71e-700003.01e-107.18e-91.14e-9APTRACI 2.1kg SO2 eq1.10e-21.75e-300006.38e-200009.75e-56.89e-44.72e-4EPTRACI 2.1kg N eq1.16e-23.32e-400005.97e-200001.85e-54.45e-41.86e-2POCPTRACI 2.1kg O3 eq1.86e-14.89e-200001.17e+000002.73e-39.06e-37.42e-3Abbreviations:GWP = Global Warming Potential, 100 years (may also be denoted as GWP-total, GWP-fossil (fossil fuels), GWP-biogenic (biogenic sources), GWP-luluc (land use and land use change)), ODP = Ozone Depletion Potential, AP = Acidification Potential, EP = Eutrophication Potential, SFP = Smog Formation Potential, POCP = Photochemical oxidant creation potential, ADP-Fossil = Abiotic depletion potential for fossil resources, ADP-Minerals&Metals = Abiotic depletion potential for non-fossil resources, WDP = Water deprivation potential, PM = Particular Matter Emissions, IRP = Ionizing radiation, human health, ETP-fw = Eco-toxicity (freshwater), HTP-c = Human toxicity (cancer), HTP-nc = Human toxicity (non-cancer), SQP = Soil quality index.Page 11 / 18

Carbo���� �59 VOCCarbolineper 1 m2 of covered and protected substrate for 60 years.TechImpa�t CategoryMethodU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4GWP-totalTRACI 2.1kg CO2e1.71e+03.26e-100004.07e+000009.10e-35.26e-18.22e-1ODPTRACI 2.1kg CFC11 eq1.29e-75.39e-900002.68e-700001.50e-103.59e-95.46e-10APTRACI 2.1kg SO2 eq1.10e-21.75e-300002.55e-200004.88e-53.44e-42.25e-4EPTRACI 2.1kg N eq1.16e-23.32e-400002.39e-200009.27e-62.23e-48.88e-3POCPTRACI 2.1kg O3 eq1.86e-14.89e-200004.69e-100001.36e-34.53e-33.54e-3Abbreviations:GWP = Global Warming Potential, 100 years (may also be denoted as GWP-total, GWP-fossil (fossil fuels), GWP-biogenic (biogenic sources), GWP-luluc (land use and land use change)), ODP = Ozone Depletion Potential, AP = Acidification Potential, EP = Eutrophication Potential, SFP = Smog Formation Potential, POCP = Photochemical oxidant creation potential, ADP-Fossil = Abiotic depletion potential for fossil resources, ADP-Minerals&Metals = Abiotic depletion potential for non-fossil resources, WDP = Water deprivation potential, PM = Particular Matter Emissions, IRP = Ionizing radiation, human health, ETP-fw = Eco-toxicity (freshwater), HTP-c = Human toxicity (cancer), HTP-nc = Human toxicity (non-cancer), SQP = Soil quality index.Comparisons cannot be made between product-specific or industry average EPDs at the design stage of a project, before a building has been specified. Comparisons may be made between product-specific or industry average EPDs at the time of product purchase when product performance and specifications have been established and serve as a functional unit for comparison. Environmental impact results shall be converted to a functional unit basis before any comparison is attempted. Any comparison of EPDs shall be subject to the requirements of ISO 21930 or EN 15804. EPDs are not comparative assertions and are either not comparable or have limited comparability when they have different system boundaries. EPDs are not comparative assertions and are either not comparable or have limited comparability when they have different system boundaries, are based on different product category rules or are missing relevant environmental impacts. Such comparison can be inaccurate, and could lead to erroneous selection of materials or products which are higher-impact, at least in some impact categories.Page 12 / 18

Carbo���� �59 VOCCarbolineResour�e Use I�d��atorsper 1 m2 of covered and protected substrate for 60 years.MarketI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4RPREMJ2.17e+04.20e-200001.11e+100002.34e-32.20e-23.68e-2RPRMMJ4.31e-11.64e-200002.24e+000009.14e-45.61e-37.65e-3RPRTMJ2.60e+05.83e-200001.33e+100003.26e-32.77e-24.44e-2NRPREMJ2.64e+14.61e+000001.55e+200002.57e-14.71e+09.42e-1NRPRMMJ2.76e-26.64e-500001.38e-100003.70e-61.83e-57.44e-5NRPRTMJ2.65e+14.61e+000001.55e+200002.57e-14.71e+09.42e-1ADPFMJ2.43e+06.46e-100001.54e+100003.61e-27.01e-11.11e-1FWm33.87e-25.20e-400001.96e-100002.90e-54.65e-48.35e-4Abbreviations:RPRE or PERE = Renewable primary resources used as energy carrier (fuel), RPRM or PERM = Renewable primary resources with energy content used as material, RPRT or PERT = Total use of renewable primary resources with energy content, NRPRE or PENRE = Non-renewable primary resources used as an energy carrier (fuel), NRPRM or PENRM = Non-renewable primary resources with energy content used as material, NRPRT or PENRT = Total non-renewable primary resources with energy content, SM: Secondary materials, RSF = Renewable secondary fuels, NRSF = Non-renewable secondary fuels, RE = Recovered energy, ADPF = Abiotic depletion potential, FW = Use of net freshwater resources, VOCs = Volatile Organic Compounds.per 1 m2 of covered and protected substrate for 60 years.TechI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4RPREMJ2.17e+04.20e-200004.43e+000001.17e-31.10e-21.76e-2RPRMMJ4.31e-11.64e-200008.94e-100004.57e-42.81e-33.65e-3RPRTMJ2.60e+05.83e-200005.32e+000001.63e-31.38e-22.12e-2NRPREMJ2.64e+14.61e+000006.21e+100001.29e-12.35e+04.50e-1NRPRMMJ2.76e-26.64e-500005.54e-200001.85e-69.15e-63.55e-5NRPRTMJ2.65e+14.61e+000006.21e+100001.29e-12.35e+04.50e-1ADPFMJ2.43e+06.46e-100006.15e+000001.80e-23.51e-15.29e-2FWm33.87e-25.20e-400007.85e-200001.45e-52.33e-43.99e-4Abbreviations:RPRE or PERE = Renewable primary resources used as energy carrier (fuel), RPRM or PERM = Renewable primary resources with energy content used as material, RPRT or PERT = Total use of renewable primary resources with energy content, NRPRE or PENRE = Non-renewable primary resources used as an energy carrier (fuel), NRPRM or PENRM = Non-renewable primary resources with energy content used as material, NRPRT or PENRT = Total non-renewable primary resources with energy content, SM: Secondary materials, RSF = Renewable secondary fuels, NRSF = Non-renewable secondary fuels, RE = Recovered energy, ADPF = Abiotic depletion potential, FW = Use of net freshwater resources, VOCs = Volatile Organic Compounds.Page 13 / 18

Carbo���� �59 VOCCarbolineWaste a�d Output Flow I�d��atorsper 1 m2 of covered and protected substrate for 60 years.MarketI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4HWDkg5.48e-3000002.74e-2000002.90e-10NHWDkg1.18e-2000005.88e-20000002.74e+0Abbreviations:HWD = Hazardous waste disposed, NHWD = Non-hazardous waste disposed, RWD = Radioactive waste disposed, HLRW = High-level radioactive waste, ILLRW = Intermediate- and low-level radioactive waste, CRU = Components for re-use, MFR or MR = Materials for recycling, MER = Materials for energy recovery, MNER = Materials for incineration, no energy recovery, EE or EEE = Recovered energy exported from the product system, EET = Exported thermal energy.per 1 m2 of covered and protected substrate for 60 years.TechI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4HWDkg5.48e-3000001.10e-2000001.45e-10NHWDkg1.18e-2000002.35e-20000001.31e+0Abbreviations:HWD = Hazardous waste disposed, NHWD = Non-hazardous waste disposed, RWD = Radioactive waste disposed, HLRW = High-level radioactive waste, ILLRW = Intermediate- and low-level radioactive waste, CRU = Components for re-use, MFR or MR = Materials for recycling, MER = Materials for energy recovery, MNER = Materials for incineration, no energy recovery, EE or EEE = Recovered energy exported from the product system, EET = Exported thermal energy.Page 14 / 18

Carbo���� �59 VOCCarbolineCarbo� Em�ss�o�s a�d Removalsper 1 m2 of covered and protected substrate for 60 years.MarketI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4BCRPkg CO200000000000000BCEPkg CO200000000000000BCRKkg CO25.35e-4000002.67e-30000000BCEKkg CO2-5.35e-400000-2.67e-30000000BCEWkg CO200000000000000CCEkg CO200000000000000CCRkg CO200000000000000CWNRkg CO200000000000000Abbreviations:BCRP = Biogenic Carbon Removal from Product, BCEP = Biogenic Carbon Emission from Product, BCRK = Biogenic Carbon Removal from Packaging, BCEK = Biogenic Carbon Emission from Packaging, BCEW = Biogenic Carbon Emission from Combustion of Waste from Renewable Sources Used in Production Processes, CCE = Calcination Carbon Emissions, CCR = Carbonation Carbon Removals, CWNR = Carbon Emissions from Combustion of Waste from Non-Renewable Sources used in Production Processes, GWP-luc = Carbon Emissions from Land-use Change.per 1 m2 of covered and protected substrate for 60 years.TechI�d��atorU��tA1A2A3A4A5B1B2B3B4B5B6B7C1C2C3C4BCRPkg CO200000000000000BCEPkg CO200000000000000BCRKkg CO25.35e-4000001.07e-30000000BCEKkg CO2-5.35e-400000-1.07e-30000000BCEWkg CO200000000000000CCEkg CO200000000000000CCRkg CO200000000000000CWNRkg CO200000000000000Abbreviations:BCRP = Biogenic Carbon Removal from Product, BCEP = Biogenic Carbon Emission from Product, BCRK = Biogenic Carbon Removal from Packaging, BCEK = Biogenic Carbon Emission from Packaging, BCEW = Biogenic Carbon Emission from Combustion of Waste from Renewable Sources Used in Production Processes, CCE = Calcination Carbon Emissions, CCR = Carbonation Carbon Removals, CWNR = Carbon Emissions from Combustion of Waste from Non-Renewable Sources used in Production Processes, GWP-luc = Carbon Emissions from Land-use Change.Page 15 / 18

Carbo���� �59 VOCCarbolineS�e�ar�osTra�sport to the bu�ld��g/�o�stru�t�o� s�te (A4)A4 ModuleFuel Type:DieselVeh��le Type:Truck and TrailerTra�sport D�sta��e:3.163e+03 kmCapa��ty Ut�l��at�o�:33 %Pa�kag��g Mass:5.113e-02 kgGross de�s�ty of produ�ts tra�sported:3.142e+03 kg/m3We�ght of produ�ts tra�sported:4.834e-01 kgVolume of produ�ts tra�sported:1.538e-04 m3Capa��ty ut�l��at�o� volume fa�tor:1Assumpt�o�s for s�e�ar�o developme�t:Transport distance includes finished product to distribution center and distribution center to point of sale.I�stallat�o� �� to the bu�ld��g/�o�stru�t�o� s�te (A5)A5 ModuleProdu�t Lost per Fu��t�o�al U��t:0.04834 kgMass of Pa�kag��g Waste Spe��fied by Type:0.05113 kgVOC Em�ss�o�s:95000000000 ug/m3Assumpt�o�s for s�e�ar�o developme�t:As per the PCR, packaging waste management is reported in C1-C4 and VOC emissions in B1.The VOC content reported in this EPD is an estimated value and may not accurately represent the actual VOC emissions during the coating's curing process after installation. It is provided for informational purposes only and should not be used as a direct indicator of emissions under actual use conditions.VOC Test Method:ASTM D-2369Refere��e Serv��e L�feB1 ModuleRSL:60 YearsDe�lared Produ�t Propert�es:Rapid cure. Dry to recoat in 30 minutes at 75°F (24°C) and 50% relative humidity. Complies with SSPC Paint 20 (Type II). Meets Class B slip co-efficient and creep testing criteria for use on faying surfaces up to 3 mils dry (See "Dry Film Thickness" section). Low temperature cure down to 35°F (2°C). Excellent adhesion. Protects against undercutting corrosion. Available in ASTM D520, Type II zinc version. Field proven primer that applies well by spray methods. Excellent touch-up primer by brush or roll for small areas. Extremely low VOC (less than 100 g/l). Low HAPS (0.51 lbs/solid gal)Des�g� Appl��at�o� Parameters:Use an agitated pressure pot with dual regulators, a minimum 3/8” I.D. material hose, and a .070” I.D. fluid tip, or an airless sprayer with a 30:1 pump ratio, minimum 3.0 GPM output, 3/8” I.D. material hose, and a tip size between .017-.023” with 2000-2200 PSI output. Brush and roller application is recommended only for small areas and touch-ups, with spray being the preferred method for larger areas. Ensure substrate temperatures are 5°F (3°C) above the dew point to avoid issues like flash rusting, and expect curing times of 2 hours to handle and 30 minutes to topcoat at 75°F (24°C) based on a 3.0 mil (75 micron) dry film thickness; higher film thicknesses or cooler temperatures may extend cure times. Consult product technical data sheet for detailed application parameters. Consult a Carboline representative for more information.Page 16 / 18

Carbo���� �59 VOCCarbolineA� Assumed Qual�ty of Work, Whe� I�stalled �� A��orda��e w�th The Ma�ufa�turer’s I�stru�t�o�s:Long term protection is achieved when installed in accordance with manufacturer's instructions. Theoretical coverage is 1059 ft2/gal at 1.0 mils (26.0 m2/l at 25 microns).Repla�eme�t (B4)B4 ModuleRefere��e Serv��e L�fe:60 YearsRepla�eme�t Cy�le:5 (ESL/RSL)-1Further assumpt�o�s for s�e�ar�o developme�t:Product is assumed to be applied in an industrial environment. A market service lifetime and a technical service lifetime was adopted in the LCA model (see product specifications). Number of recoats is obtained by dividing the service lifetime. One initial coating application and subsequent recoats are required to maintain the average lifespan of a building, assumed to be 60 years.E�d of L�feC1 - C4 ModulesCollection ProcessColle�ted Separately:0.05113 kgColle�ted w�th M�xed Co�stru�t�o� Waste:0.4834 kgRecoveryRe�y�l��g:0.01738 kgLa�dfill:0.4351 kgI����erat�o�:0.04834 kgAssumpt�o�s for s�e�ar�o developme�t: I�terpretat�o� The manufacturing of Carboline's products involves the direct procurement of raw materials from suppliers. These materials are then transported to Carboline's manufacturing facilities in Green Bay, WI, Dayton, NV, and Lake Charles, LA where they are stored and mixed to produce the coatings. At the application site, coatings are spray or brush applied to various exterior steel structural components to add a protective barrier to the steel substrate. The use stage (stage 3) has a smaller contribution to the overall life cycle performance.. For the analysis, It was assumed that Carboline's coatings require one initial coating application and multiple recoats to achieve the recommended service life of 60 years, aligning with the building's life cycle. The results were presented per one square meter of covered and protected substrate at a recommended coating thickness. The greatest contribution can be found in the use and maintenance stage due to the effect of the required repaints that will multiply the contribution of the product and design & construction stages together with the product application by the required number of recoats. For one single recoat, production stage, has the highest impact across all impact categories due mainly to the manufacture and transport of raw material, with some contribution of the manufacturing stage. At the application site, coatings are spray or brush applied to various exterior steel structural components to add a protective Page 17 / 18

Carbo���� �59 VOCCarbolinebarrier to the steel substrate. This activity has a smaller contribution to the overall life cycle performance. End-of-life impacts are generally limited because most of the product is assumed to be landfilled, although impacts accumulate at each successive recoating. Given that the raw materials used in product manufacturing have the most significant impact, there are opportunities to substitute these materials with alternatives that have a lower environmental impact or to work with supplies in order to reduce impact along the supply chain. 0%20%40%60%�0%100% GWP-total ODP AP EP POCP Produ�t�o� (A1 - A3)Co�stru�t�o� (A4 - A5)Use (B1 - B7)E�d of L�fe (C1 - C4)Add�t�o�al E�v�ro�me�tal I�format�o� Before using this product, it is recommended that the operator read and follow all caution statements on the product data sheet and on the SDS for this product, and personal protective equipment must be used as directed. Refere��es• ISO 14040:2006/Amd 1:2020, “Environmental management - Life cycle assessment - Principles and framework”. • ISO 14044:2006/Amd 1:2017/Amd 2:2020, “Environmental management - Life cycle assessment - Requirements and guidelines”. • ISO 21930:2017, “Sustainability in buildings and civil engineering works - Core rules for environmental product declarations of construction products and services”. • NSF International, Product Category Rules for Environmental Product Declarations for Architectural Coatings, June 2015. • ISO 14025:2006, “Environmental labels and declarations - Type III environmental declarations - Principles and procedures”. • Bare, J. 2014. Tool for the Reduction and Assessment of Chemical and Other Environmental Impacts (TRACI) TRACI version 2.1 User’s Guide. US EPA Office of Research and Development, Washington, DC, EPA/600/R-12/554, http://nepis.epa.gov/Adobe/PDF/P100HN53.pdf • IPCC, 2013: Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Stocker, T.F., D. Qin, G.-K. Plattner, M. Tignor, S.K. Allen, J. Boschung, A. Nauels, Y. Xia, V. Bex and P.M. Midgley (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA, 1535 pp. https://www.ipcc.ch/report/ar5/wg1/ • ecoinvent v3.9.1, December 2022, https://ecoinvent.org/the-ecoinvent-database/data-releases/ecoinvent-3-9-1/ • US Environmental Protection Agency Waste Reduction Model (WARM) v15, September 2022, https://www.epa.gov/warm/versions-waste-reduction-mod-el-warm#15 • Ryberg, M., M. Vieira, M. Zgola, et al. Updated US and Canadian Normalization Factors for TRACI 2.1. CLEAN TECHNOLOGIES ENVIRONMENTAL POLICY. Springer, New York, NY, 16(2):329-339 (2014). http://dx.doi.org/10.1007/s10098-013-0629-z • Weidema B. P., C. Bauer, R. Hischier, et al. Overview and methodology. Data quality guideline for the ecoinvent database version 3. Ecoinvent Report 1(v3), St. Gallen: The ecoinvent Centre (2013). https://ecoinvent.org/wp-content/uploads/2021/09/dataqualityguideline_ecoinvent_3_20130506.pdf • Facts and figures about materials, waste and recycling (2018). https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling • Carboline Internal Report, Life Cycle Assessment of Carboquick 200 Coating, September 2023 • Carboline Internal Report, Amendment to Life Cycle Assessment of Carboquick 200 Coating for Sixteen Additional Coatings, March 2024 Page 18 / 18