AI is not coming to the restoration industry — it is already here. From automated estimating to AI-powered content generation to predictive analytics on storm seasons, the companies that adopt intelligently will dominate the next decade. We cut through the hype and show what is real, what works, and what is just noise. No fluff, no fear — just the tools and strategies that give restoration operators an unfair advantage.
AI in Restoration covers artificial intelligence applications, machine learning tools, automation workflows, AI-powered estimating, predictive analytics, chatbot deployment, content generation, operational AI, and technology adoption strategies for water damage, fire restoration, mold remediation, and commercial restoration companies.
Federal disaster response contracting represents one of the largest and most reliable revenue streams for commercial restoration companies. It is also the procurement category where ESG requirements are evolving fastest at the federal level.
The Current Federal ESG Procurement Landscape
The 2022 proposed Federal Supplier Climate Risks and Resilience Rule would have required major federal contractors (those with $50 million or more in annual federal contract obligations) to disclose Scope 1, 2, and 3 GHG emissions and set science-based targets. The rule’s implementation was paused pending legal and regulatory review. FEMA does not currently mandate Scope 3 reporting from its restoration contractors — but the direction of federal procurement policy is clear.
Where ESG Capability Matters in Federal Work Now
State and local government agencies administering FEMA Public Assistance funds are building ESG criteria into their own procurement. California, New York, and states with active sustainability procurement programs are leading this shift. Contractors who can demonstrate documented emissions reporting capability have an advantage in state-level preferred vendor programs that feed FEMA-funded disaster response work.
Large general contractors and program managers participating in federal disaster response are also increasingly applying ESG supply chain criteria to their subcontractor base — even where FEMA itself doesn’t require it. If you’re subcontracting to a large GC on federal disaster response, that GC may already have ESG supply chain requirements flowing to you.
The Organizational Maturity Signal
The value of ESG documentation in federal contracting — even where not formally required — is as an organizational maturity signal. Large-scale federal disaster response contracts go to companies that can demonstrate systems, documentation practices, and operational discipline to work at scale under federal oversight. RCP implementation demonstrates exactly the systematic operational approach that federal contracting officers look for in large-scale CAT deployments.
Does FEMA currently require Scope 3 emissions reporting?
No, not formally. The proposed Federal Supplier Climate Risks and Resilience Rule was paused. However, large GCs participating in federal disaster response are increasingly applying ESG criteria to their subcontractors, and state-level requirements vary significantly.
How does the RCP help with federal contracting specifically?
RCP documentation demonstrates the systematic data capture and reporting discipline that federal contracting values. For contractors pursuing large-scale federal work, structured per-job emissions documentation at scale signals the operational infrastructure and management systems that large federal deployments require.
Which states have the most active ESG procurement requirements for disaster response?
California and New York have the most developed sustainability procurement programs. States under EU investor influence (those with significant European institutional investment in public infrastructure) are also ahead of the national average on ESG vendor requirements.
Having the data is not enough. The way you package and deliver per-job carbon data determines whether your commercial clients can use it or whether it becomes a research project for their ESG team. Usable data arrives in the right format, at the right time, with enough context to slot directly into their Scope 3 inventory without additional processing.
What Commercial Clients Actually Need
A commercial property manager’s ESG team needs: emissions in metric tons of CO2 equivalent (tCO2e), broken down by GHG Protocol Scope 3 category, attributed to a specific property and time period, with a methodology citation they can use in their disclosure documentation. Everything else is secondary. Lead with the numbers in the right format.
The RCP Per-Job Carbon Report Format
The RCP per-job carbon report is a single-page document containing: job identification (contractor, job ID, property address, job type, dates), emissions summary (total tCO2e with subtotals by Scope 3 category), category breakdown with activity data and emission factors, methodology citation (“Restoration Carbon Protocol v1.0, GHG Protocol Corporate Value Chain Standard, EPA/DEFRA emission factors”), and data quality notation flagging any estimated data points.
Delivery Timing and Format
Deliver within 30 days of job completion for planned maintenance work, 60 days for emergency loss events. Delivery timing matters because commercial clients aggregate Scope 3 data on an annual cycle — reports received after their cut-off date get pushed to the following year’s inventory.
Format options in order of preference: structured data file (CSV or JSON) feeding directly into ESG software, PDF carbon report for manual entry, standardized email summary with required fields clearly labeled. Ask which format the client’s ESG team prefers.
Building the Report Into Job Close-Out
Treat the per-job carbon report as a standard job deliverable — same category as moisture readings or job completion certificate. Adding it to your close-out checklist as a required item for commercial jobs ensures consistent delivery and builds the data discipline needed for reliable ESG reporting.
Handling Historical Data Requests
Commercial clients building their first Scope 3 inventory often request historical data going back two or three years. For jobs completed before RCP implementation, produce a retrospective estimate using RCP methodology applied to available historical records. Flag as estimated with documentation of what records were used. A documented estimate is more useful than a refusal to provide historical data.
Do you need to provide a carbon report for every job?
For SB 253 and GRESB purposes, only commercial clients have reporting obligations requiring contractor data. Building the data capture habit across all jobs reduces administrative burden and builds the operational discipline that makes commercial reporting reliable.
What if the client’s ESG team doesn’t know what to do with the data?
Include a brief explanatory cover note explaining which GHG Protocol Scope 3 categories the data covers and how to incorporate it into a portfolio-level Scope 3 inventory. The RCP will publish a standard client guidance document for this purpose.
Should you provide carbon data proactively or only when requested?
Proactive delivery — including the carbon report with standard close-out documentation for all commercial clients — is recommended. It demonstrates ESG maturity, avoids chasing data requests retroactively, and establishes you as a vendor who thinks about supply chain sustainability without being prompted.
The most common objection restoration contractors raise to Scope 3 emissions reporting is that it requires tracking data they don’t have. In most cases, the data exists — it’s just not being retained in a form usable for emissions calculation. The RCP 12-point standard formalizes what every job ticket should contain.
Group 1: Transportation Data (Category 4)
Data point 1 — Vehicle log: For each vehicle used (crew vehicles, equipment trailers, pack-out trucks, heavy equipment), record vehicle type, number of round trips to the job site, and round-trip mileage. Source: dispatch records, GPS fleet data, or driver logs.
Data point 2 — Waste transport log: Separately from crew/equipment transportation, record vehicle type, trips, and mileage for all waste hauling — to landfills, transfer stations, hazmat facilities, or wastewater treatment facilities. Often omitted from job documentation when waste hauling is subcontracted, but emissions belong to the job regardless.
Data point 3 — Equipment power source: Document whether drying/filtration/processing equipment operated on building electrical supply or contractor-supplied generators. If generators, record fuel type and quantity consumed. Determines whether equipment energy is Scope 2 (building electricity, property owner) or included in contractor’s Scope 3 calculation.
Group 2: Materials Data (Category 1)
Data point 4 — Chemical treatments log: Volume of each chemical product applied: antimicrobials (liters by product type), biocides, encapsulants, deodorizing compounds, wetting agents. Can be estimated from square footage and application rate if purchase records are not job-specific.
Data point 5 — PPE consumption log: Units of disposable PPE consumed: Tyvek suits, gloves (pairs), N95/P100 respirators, boot covers, eye protection. Can be reconstructed from supply orders or estimated from job duration and crew size using standard consumption rates.
Data point 6 — Containment materials log: Meters of polyethylene sheeting, number of zipper doors installed, HEPA filter media units replaced. Primarily relevant for mold remediation, hazmat abatement, and Category 3 water damage.
Group 3: Waste Data (Category 5)
Data point 7 — Debris volume by waste category: Weight or volume by category: standard C&D debris (tons), regulated hazardous materials (tons by type), contaminated water (liters or gallons). Source: disposal facility receipts, dumpster manifests, or tank/extractor volume logs.
Data point 8 — Disposal method and facility: For each waste category, record the disposal facility used and disposal method (landfill, recycling, hazmat incineration, wastewater treatment). Facility name is sufficient — national average emission factors apply where facility-specific factors are unavailable.
Group 4: Demolished Materials (Category 12) and Context
Data point 9 — Demolished materials log by type: Weight of each building material type removed: drywall (tons), flooring by type, insulation by type (tons), wood framing (tons). Source: demolition scope documentation, dumpster weight receipts.
Data point 10 — Installed replacement materials (reconstruction only): Weight of new building materials installed if reconstruction is within the contractor’s scope. Available from purchase orders or materials delivery receipts.
Data point 11 — Job classification: Job type, damage category/class, affected area in square feet, building construction type (pre/post-1980 for hazmat assumptions).
Data point 12 — Job timeline: Start date, completion date, client property identifier. Assigns emissions to the correct reporting year and property for portfolio-level Scope 3 inventory.
What if some data points are unavailable?
Use RCP’s proxy estimation methodology — standard consumption rates by job type and damage class. Document which data points were estimated and the basis for each estimate. A documented estimate is far more useful to your client than no data.
Who should be responsible for capturing these data points?
Data points 1-3 and 11-12 at the project management level. Data points 4-10 may require field crew input. Designating a data capture owner at job setup and building capture into the close-out checklist is the most reliable approach.
Can existing job management software capture these data points?
Most major restoration platforms (ServiceMonster, Xactimate, Jonas) can accommodate these as custom fields. The RCP will publish integration guidance for common platforms as the standard matures.
Asbestos and hazmat abatement generates the highest emissions per unit of material removed of any restoration job type. The combination of specialized transportation to licensed disposal facilities, extreme PPE consumption, and high-emissions disposal methods (including incineration for some regulated materials) produces an emissions profile that is fundamentally different from standard C&D work. This guide provides the emission factors, calculation methodology, and a worked example for a commercial ACM abatement project.
Regulated Materials: Classification Before Calculating
Hazmat abatement transportation has two components with fundamentally different emission profiles: crew and equipment mobilization (standard restoration factors) and regulated waste transportation (elevated factors due to distance to licensed facilities and loaded vehicle weight).
Vehicle Type
kg CO2e per mile
Use
Crew vehicles (light truck, van)
0.503
Daily crew transport
Decontamination unit (trailer-mounted)
1.084
Mobilization and demobilization
Negative air pressure / HEPA equipment trailer
1.084
Equipment mobilization
Licensed hazmat waste hauler (ACM, lead)
3.20
Regulated C&D to licensed landfill — loaded
Licensed hazmat waste hauler (PCB, mercury)
3.80
High-hazard regulated waste — specialty vehicle
Licensed disposal facility distance note: Licensed hazmat landfills capable of receiving friable ACM are significantly less common than standard C&D landfills. Average transport distance to a licensed ACM facility is 45–90 miles in most US metro areas, compared to 10–25 miles for standard C&D. Use actual haul distances from your waste manifests. If unavailable, use 60 miles as the default for ACM waste and 80 miles for PCB/high-hazard waste.
Category 1: Materials Emission Factors
Material
Unit
kg CO2e per unit
Notes
Level C PPE kit (Tyvek, gloves, boot covers, goggles)
Kit per entry
1.8
Full replacement required each decon exit
Level B PPE (supplied air + full encapsulating suit)
Kit per entry
4.2
Higher-grade suit + air supply equipment
Half-face respirator, P100 + OV cartridges (pair)
Pair
0.8
EPA EEIO — medical equipment
Full-face respirator cartridges (pair)
Pair
1.2
EPA EEIO — medical equipment
HEPA filter (negative air machine)
Each
3.2
EPA EEIO — industrial machinery
Wetting agent / amended water (surfactant)
Liter
1.4
EPA EEIO — chemical manufacturing (applied during ACM removal to suppress fibers)
Changed more frequently under hazmat conditions — typically every 8–12 hours
Disposal bags (6-mil, ACM-labeled)
Each (33 gallon)
0.55
EPA EEIO — plastics manufacturing
PPE consumption rate for hazmat abatement: Unlike standard restoration where PPE may last a full shift, hazmat abatement requires full PPE replacement each time a worker exits the work area through the decontamination unit. A standard 8-hour ACM abatement shift with 3 exits per worker produces 3 complete PPE kit replacements per worker. For crew of 4: 4 workers × 3 exits × 1.8 kg/kit = 21.6 kg CO2e in PPE alone per day.
Municipal wastewater (if non-hazardous) or permitted facility
0.000272 per liter
EPA WARM — wastewater treatment
Spent PPE (hazmat grade)
Licensed hazmat landfill
0.30
Higher than standard PPE due to contamination classification
Complete Worked Example: Pre-1970 Commercial Office Building, Floor Tile and Ceiling Tile ACM Abatement
Job profile: 5,000 sq ft floor tile removal (non-friable ACM, 9″ floor tiles) and 5,000 sq ft suspended ceiling tile replacement (non-friable ACM) in a 1967 office building being renovated. No pipe insulation abatement in scope. Crew: 4 abatement technicians, 8-day project. Air monitoring by third-party IH (not in contractor scope). Facility: 28 miles from job site. Licensed C&D landfill with ACM cell: 54 miles from job site.
Category 4 — Transportation
Crew vehicles: 2 light trucks × 56 mi RT × 9 trips (8 work days + equipment pickup) = 504 mi × 0.503 = 254 kg CO2e
Decontamination unit (trailer): 1 × 56 mi × 2 trips = 112 mi × 1.084 = 121 kg CO2e
Negative air / HEPA equipment trailer: 1 × 56 mi × 2 trips = 112 mi × 1.084 = 121 kg CO2e
ACM waste haul (non-friable floor + ceiling tiles, 2 loads): 2 × 108 mi RT to licensed facility × 3.20 kg/mi = 691 kg CO2e
Category 4 total: 1,187 kg CO2e = 1.19 tCO2e
Category 1 — Materials
PPE (Level C, 4 workers × 8 days × 3 exits/day = 96 kit replacements): 96 × 1.8 kg = 173 kg CO2e
P100 respirator cartridges: 4 workers × 8 days × 1 replacement/day = 32 pairs × 0.8 = 26 kg CO2e
6-mil poly sheeting (double-layer containment, 500 sq ft decon area + staging): 200 m² × 1.10 kg/m² = 220 kg CO2e
HEPA filters (4 negative air machines × 2 changes/day × 8 days = 64 filters): 64 × 3.2 = 205 kg CO2e
Wetting agent for tile removal (applied to floor tiles before removal): 5,000 sq ft × 0.003 L/sq ft = 15 liters × 1.4 = 21 kg CO2e
ACM disposal bags (33-gallon, for ceiling tile bagging): estimated 80 bags × 0.55 = 44 kg CO2e
Category 1 total: 689 kg CO2e = 0.69 tCO2e
Category 5 — Waste
Floor tiles (non-friable ACM, 5,000 sq ft × 4 lbs/sq ft = 10 tons): 10 × 0.28 = 2.80 tCO2e
Ceiling tiles (non-friable ACM, 5,000 sq ft × 1.5 lbs/sq ft = 3.75 tons): 3.75 × 0.28 = 1.05 tCO2e
Decontamination wastewater (~800 liters over 8 days): 800 × 0.000272 = 0.22 kg CO2e (negligible)
Category 5 total: 4.09 tCO2e
Category 12 — Demolished Hazardous Building Materials
For ACM floor and ceiling tiles, the material itself is the hazardous waste — it flows to Category 5 disposal accounting. Category 12 is not separately calculated for ACM materials that are classified as hazardous waste upon removal, since the disposal emissions are already captured in Category 5. This is a key distinction from standard demolition: ACM materials do not generate both Category 5 and Category 12 emissions — they generate Category 5 only.
Category 12 total: 0 tCO2e (ACM materials classified as regulated waste at removal — captured in Category 5)
Job Total
Category
tCO2e
% of Total
Category 4 — Transportation
1.19
20%
Category 1 — Materials
0.69
12%
Category 5 — Waste disposal (regulated)
4.09
68%
Category 12 — Demolished materials
0.00
0%
Total
5.97 tCO2e
100%
Key observation: For hazmat abatement, Category 5 waste disposal is the dominant emission source at 68% of total — confirming that reduction strategies for this job type should focus on waste minimization (reducing the volume of regulated material requiring licensed disposal) rather than fleet or materials optimization. In practice, this means accurate pre-abatement survey to confirm material quantities precisely, minimizing unnecessary demolition scope, and pursuing licensed recycling options for non-friable ACM where available.
Why are Category 12 emissions zero for ACM materials in this example?
When building materials are classified as hazardous waste at the point of removal, their disposal emissions are captured entirely in Category 5 (Waste Generated in Operations) using the hazmat disposal emission factors. Counting them in both Category 5 and Category 12 would be double-counting. The RCP applies the more specific category (5, with hazmat factors) and zeros out Category 12 for regulated materials.
What if only some floor tiles test positive for ACM — how do I split the waste calculation?
Apply ACM disposal emission factors (0.28 tCO2e/ton) only to the confirmed ACM material quantity. Apply standard C&D disposal factors (0.16 tCO2e/ton) to confirmed non-ACM material. If testing was not performed and the building construction date is pre-1980, use ACM factors for all suspect materials and document the assumption in your data quality notes.
How do I handle a job where PCB-containing caulk is discovered mid-project?
Document the discovery date and quantity. If PCB caulk removal was not in your original scope, calculate those emissions separately as a scope addition and note in the RCP report that PCB materials were encountered. Apply the PCB incineration emission factor (1.85 tCO2e/ton) to all PCB-classified material — the difference from standard C&D factors is significant enough to materially affect the job total and should be clearly identified.
Mold remediation has a different emissions signature than water damage or fire restoration — it is slower, more materials-intensive per square foot, and dominated by chemical treatments and containment infrastructure rather than vehicle transportation. This guide provides the emission factors, calculation methodology, and a complete worked example for a Condition 3 commercial mold remediation.
Job Classification Before Calculating
Condition (IICRC S520)
Scope
Emissions Profile
Typical Range
Condition 1 — Normal fungal ecology
No remediation
N/A
0 tCO2e
Condition 2 — Settled spores, no active growth
HEPA vacuum + antimicrobial wipe-down
Transportation dominant, minimal materials
0.1–0.4 tCO2e
Condition 3 — Active growth, limited area (<100 sq ft)
Containment, demolition, remediation, clearance
Materials + transportation balanced
0.3–1.0 tCO2e
Condition 3 — Active growth, large area (100–1,000 sq ft)
Full remediation protocol
Materials dominant, transportation secondary
0.8–4.0 tCO2e
Condition 3 — Large commercial HVAC system affected
Full remediation + duct cleaning/replacement
All four categories significant
2.0–8.0 tCO2e
Category 4: Transportation Emission Factors
Mold remediation typically involves more crew trips relative to equipment trips than fire or water jobs — the slower pace means daily crew mobilization across an extended project without proportionally heavy equipment deployment.
Vehicle Type
kg CO2e per mile
Typical Use
Light truck / work van
0.503
Daily crew transport
Cargo van (containment materials)
0.503
Poly sheeting, negative air machines
Medium equipment trailer
1.084
Air scrubbers, negative air pressure units
Dump truck (debris)
2.25 (loaded) / 1.612 (empty)
Demolition debris removal
Category 1: Materials Emission Factors
Mold remediation is the most materials-intensive restoration job type per square foot of affected area. Containment infrastructure, biocidal treatments, and HEPA filtration media represent significant Category 1 emissions even on smaller jobs.
Material
Unit
kg CO2e per unit
Notes
Quaternary ammonium biocide (liquid)
Liter
2.8
EPA EEIO — chemical manufacturing
Hydrogen peroxide biocide (liquid)
Liter
1.9
EPA EEIO — chemical manufacturing
Borax-based mold treatment
kg
1.1
EPA EEIO — inorganic chemical
Encapsulant (antimicrobial-infused sealant)
Gallon
4.2
EPA EEIO — paint and coatings
6-mil polyethylene sheeting
m²
0.55
EPA EEIO — plastics product manufacturing
4-mil polyethylene sheeting
m²
0.37
EPA EEIO — plastics product manufacturing
Zipper door (containment, reusable)
Each
1.8 (amortized over 20 uses)
EPA EEIO — plastics/hardware — divide by use count
Zipper door (disposable)
Each
1.8
Full factor per use
HEPA filter (air scrubber, negative air)
Each
3.2
EPA EEIO — industrial machinery
HEPA vacuum bag (commercial)
Each
0.4
EPA EEIO — paper/plastics
Full Tyvek suit (Level C minimum)
Each
1.2
EPA EEIO — apparel manufacturing
Half-face respirator + P100 cartridges (pair)
Pair
0.8
EPA EEIO — medical equipment
Nitrile gloves (pair)
Pair
0.3
EPA EEIO — rubber/plastics
Biocide application rate proxies by condition and surface type: Condition 3 porous surfaces (drywall, wood framing) — 0.020 liters/sq ft for first application, 0.015 liters/sq ft for second application. Non-porous surfaces — 0.008 liters/sq ft. HVAC duct interiors — 0.012 liters/linear ft.
Containment materials proxy: Standard containment setup for a single affected room uses approximately 50 linear feet of 6-mil poly at ceiling height (8 ft average) = 120 m² of sheeting. Add 20 m² per additional doorway or penetration. Reusable zipper doors amortize over approximately 20 uses before replacement.
EPA WARM + contamination premium for bagged disposal
Mold-contaminated insulation
Standard landfill
0.33
EPA WARM v16 — fiberglass category
HEPA filter media (spent)
Standard landfill
0.28
EPA WARM — mixed synthetic materials
HEPA vacuum bags (spent)
Standard landfill
0.25
EPA WARM — mixed materials
Disposable PPE and containment
Standard landfill
0.25
EPA WARM — mixed plastics
Mold-contaminated materials with concurrent ACM
Licensed hazmat landfill
0.38
Apply when ACM present — hazmat transport factor
Category 12: Demolished Building Materials
Material
tCO2e per ton (landfill)
Gypsum drywall
0.16
Wood framing (dimensional lumber)
-0.07 (carbon storage credit)
Fiberglass batt insulation
0.33
Cellulose insulation (spray-applied)
0.06
OSB sheathing
-0.05 (carbon storage credit)
Carpet + pad
0.33
Complete Worked Example: Condition 3 Commercial Mold — Server Room and Adjacent Office
Job profile: HVAC condensate leak caused active mold growth behind drywall in a server room (200 sq ft) and adjacent office (300 sq ft). Total affected area: 500 sq ft. Scope: containment setup, demolition of all affected drywall (both rooms) and insulation (server room only), biocide treatment, HEPA vacuuming, clearance prep. No HVAC duct work in scope. Duration: 5 days. Crew: 2 technicians. Facility: 19 miles from job site.
Category 4 — Transportation
Crew van: 1 cargo van × 38 mi RT × 6 trips (5 work days + equipment pickup) = 228 mi × 0.503 = 115 kg CO2e
Equipment delivery (negative air machines): 1 × 38 mi × 2 trips = 76 mi × 1.084 = 82 kg CO2e
Debris removal (one load, dump truck): 1 × 22 mi × 2.25 = 50 kg CO2e
Category 4 total: 247 kg CO2e = 0.25 tCO2e
Category 1 — Materials
Biocide (first application — 500 sq ft porous surfaces): 500 × 0.020 = 10 L × 2.8 = 28 kg CO2e
Biocide (second application): 500 × 0.015 = 7.5 L × 2.8 = 21 kg CO2e
Key observation from this example: Category 1 (materials) and Category 4 (transportation) are nearly equal at 0.25 tCO2e each — confirming that mold remediation has a more balanced emissions profile than water or fire jobs where transportation typically dominates. This means reduction strategies that focus on materials (lower-emission biocide formulations, reusable containment systems) have comparable impact to fleet electrification for this job type.
Why does containment sheeting (Category 1) generate significant emissions?
Polyethylene is a petroleum-derived product with non-trivial manufacturing emissions. At 0.55 kg CO2e per m², a large commercial remediation using 300–500 m² of poly sheeting generates 165–275 kg CO2e from containment materials alone. Switching to thinner sheeting where conditions allow or reusing containment systems across jobs reduces this meaningfully.
How do I handle clearance testing in the RCP calculation?
Clearance testing by an independent industrial hygienist is a separate purchased service — the IH’s transportation and testing are Scope 3 Category 1 for the property owner (as a directly purchased service), not part of the remediation contractor’s RCP calculation. The RCP boundary is the remediation contractor’s own scope of work.
Does the presence of moisture in the affected materials affect the waste emission factor?
Use dry weight for emission factor calculations, not wet weight. Wet demolished drywall weighs approximately 50% more than dry drywall due to absorbed moisture. If you’re estimating weight from area (2.5 lbs/sq ft), this factor already accounts for typical dry weight — apply it directly without adjusting for moisture content.
Fire and smoke restoration generates the most variable Scope 3 emissions of any restoration job type. A contained single-room smoke job and a multi-floor structural fire with hazmat abatement and full reconstruction can both appear on your P&L as “fire restoration” — but their emissions differ by a factor of 20 or more. This guide gives you the emission factors, the calculation methodology, and a complete worked example to produce an accurate per-job figure regardless of where on that spectrum your job falls.
Job Classification: Phase and Scope
Before calculating, identify which phases are in your scope of work and document them separately. Emissions from mitigation and reconstruction phases should be tracked separately even if invoiced together — they may occur in different reporting years.
Fire restoration deploys more vehicle types per job than any other restoration category. Account for each separately.
Vehicle Type
kg CO2e per mile
Common Use in Fire Restoration
Light truck / work van
0.503
Crew transportation, initial response
Medium equipment trailer
1.084
Air scrubbers, ozone generators, thermal foggers
Box truck / pack-out truck
1.084
Content pack-out and storage transport
Heavy dump truck (unloaded)
1.612
Debris removal mobilization
Heavy dump truck (loaded)
2.25
Debris removal trips to landfill/transfer
Specialty hazmat transport (ACM)
2.80
Asbestos or lead waste to permitted facility
Content pack-out note: Pack-out is frequently the second-largest transportation source on large fire jobs. Track pack-out truck trips separately from crew mobilization and debris removal trips. Pack-out involves loaded trucks going to storage and returning empty — apply loaded emission factor for outbound, unloaded for return.
Category 1: Materials Emission Factors
Material
Unit
kg CO2e per unit
Notes
Chemical sponge (dry soot sponge)
Each
0.15
EPA EEIO — cleaning products
Dry ice (CO2 pellets for blasting)
kg
0.85
Industrial CO2 production — use with caution; CO2 is released on use, but EPA factors cover production
Hydroxyl generator treatment (per day-unit)
Day-unit
0.40
Equipment embodied carbon, negligible per use
Ozone generator treatment (per day-unit)
Day-unit
0.35
Equipment embodied carbon, negligible per use
Encapsulant / sealant (smoke blocking primer)
Gallon
4.2
EPA EEIO — paint and coating manufacturing
Thermal fogging agent
Liter
2.1
EPA EEIO — chemical manufacturing
HEPA filter (air scrubber)
Each
3.2
EPA EEIO — industrial machinery
Full Tyvek suit (Level C)
Each
1.2
EPA EEIO — apparel manufacturing
Half-face respirator with organic vapor/P100 cartridges (pair)
Pair
0.8
EPA EEIO — medical equipment
Nitrile gloves (pair)
Pair
0.3
EPA EEIO — rubber/plastics
Reconstruction phase materials — installed building components: If your scope includes reconstruction, the embodied carbon of installed materials belongs in Category 1. Use these EPA EEIO factors: drywall $0.42 per board foot × board feet; dimensional lumber $0.55 per board foot; paint and primer $4.2 per gallon. For complex reconstruction, request embodied carbon data from your materials supplier or use the Athena Impact Estimator for buildings as a secondary source.
Category 5: Waste Emission Factors
Waste Type
Disposal Method
tCO2e per ton
Source
Smoke-contaminated C&D debris (non-hazardous)
Standard landfill
0.16
EPA WARM v16
Smoke-contaminated C&D debris (regulated)
Licensed C&D landfill
0.20
EPA WARM + transport premium
Asbestos-containing materials (ACM)
Licensed hazmat landfill
0.38
EPA WARM + hazmat transport + licensed facility
Lead paint debris (regulated)
Licensed hazmat landfill
0.35
EPA WARM + hazmat premium
PCB-containing materials
Licensed hazmat incineration
1.85
EPA hazardous waste incineration factors
Disposable PPE and consumables
Standard landfill
0.25
EPA WARM v16 — mixed plastics
ACM identification rule: If the building was constructed before 1980 and your demolition scope touches floor tiles, ceiling tiles, pipe insulation, or joint compound, assume ACM until tested. Apply the ACM emission factor (0.38 tCO2e/ton) to all potentially ACM-containing demolition waste in buildings where testing was not completed before demolition. Document the assumption in your data quality notes.
Category 12: Demolished Building Materials
Material
tCO2e per ton landfilled
Notes
Gypsum drywall
0.16
EPA WARM v16
Dimensional lumber
-0.07
Carbon storage credit (if landfilled, not incinerated)
Carpet + pad
0.33
EPA WARM v16
Acoustic ceiling tile
0.12
EPA WARM v16 — ceiling tile category
Fiberglass insulation
0.33
EPA WARM v16
Electrical components (non-hazardous)
0.28
EPA WARM v16 — mixed electronics
Structural steel (salvaged)
-0.85
EPA WARM v16 — recycled metal credit
Complete Worked Example: Commercial Suite Fire — Single Floor
Job profile: Kitchen fire in a 3,200 sq ft commercial restaurant. Scope: smoke damage treatment throughout, selective demolition of kitchen (800 sq ft, including drywall, ceiling tiles, hood system). No ACM (post-1985 building). Reconstruction not in contractor scope. Pack-out of kitchen equipment. Crew: 4 technicians, 6 days. Facility: 31 miles from job site.
Category 4 — Transportation
Crew trucks: 2 light trucks × 62 mi RT × 8 trips (6 work days + mobilization + equipment pickup) = 992 mi × 0.503 = 499 kg CO2e
Equipment trailer (air scrubbers, ozone gen): 1 × 62 mi × 2 trips = 124 mi × 1.084 = 134 kg CO2e
Pack-out truck (kitchen equipment): 1 loaded trip × 62 mi = 62 mi × 2.25 + 1 return trip × 62 mi × 1.612 = 140 + 100 = 240 kg CO2e
Debris dump truck: 2 loads to transfer station × 18 mi × 2.25 kg/mi = 81 kg CO2e
Category 4 total: 954 kg CO2e = 0.95 tCO2e
Category 1 — Materials
Chemical sponges: 3,200 sq ft ÷ 50 sq ft/sponge = 64 sponges × 0.15 kg = 10 kg CO2e
Encapsulant/smoke blocking primer (kitchen surfaces): 12 gallons × 4.2 kg/gallon = 50 kg CO2e
Acoustic ceiling tiles: 800 sq ft × 1.8 lbs/sq ft = 0.65 tons × 0.12 = 0.08 tCO2e
Category 12 total: 0.23 tCO2e
Job Total
Category
tCO2e
Category 4 — Transportation
0.95
Category 1 — Materials
0.18
Category 5 — Waste disposal
0.47
Category 12 — Demolished materials
0.23
Total
1.83 tCO2e
How does the presence of asbestos-containing materials change the total emissions?
Significantly. In the example above with no ACM, Category 5 waste totals 0.47 tCO2e. If the same job involved 1.5 tons of ACM abatement, that adds 1.5 × 0.38 = 0.57 tCO2e to Category 5 alone — a 121% increase in waste emissions — plus additional transportation for hazmat hauling. Always identify ACM status before calculating.
Are dry ice blasting emissions included in Category 1 or treated differently?
Use the dry ice production emission factor (0.85 kg CO2e/kg) for Category 1. The CO2 released when dry ice sublimates during blasting is not separately counted — it’s included in the production emission factor. Note in your data quality section that dry ice CO2 release is accounted for through production factors per EPA guidance.
How do I calculate emissions when reconstruction is performed by a separate GC?
The reconstruction contractor calculates their own RCP emissions separately. Your calculation ends at the boundary of your scope of work. Note in your job report that reconstruction was performed by a separate contractor and reference their separate RCP report if available.
This guide is the working document for calculating Scope 3 greenhouse gas emissions from water damage mitigation jobs under the Restoration Carbon Protocol. It contains the actual emission factors, the calculation methodology for each Scope 3 category, and a complete worked example from a real job type. A contractor who follows this guide will produce a per-job carbon figure that is defensible in a third-party ESG audit.
Job Classification: Why It Matters Before You Calculate
Your emissions total will vary by a factor of 10 or more depending on water category and drying class. Before calculating, classify the job correctly using IICRC S500 definitions:
Category
Source
Emissions Driver
Typical Total Range
Cat 1 / Class 1–2
Clean supply water, limited area
Transportation dominant
0.1–0.5 tCO2e
Cat 2 / Any class
Gray water (washing machine, dishwasher, toilet overflow without feces)
Materials + transportation
0.3–1.5 tCO2e
Cat 3 / Any class
Black water (sewage, floodwater, standing water)
Hazmat disposal + transportation
1.0–8.0 tCO2e
Cat 3 / Class 3–4
Black water, large affected area requiring demolition
All four categories significant
3.0–12.0 tCO2e
Category 4: Transportation Emissions
Transportation is typically the largest or second-largest emission source on water damage jobs. Calculate every vehicle separately.
Emission Factors (EPA Mobile Combustion, 2024)
Vehicle Type
Fuel
kg CO2e per mile
Source
Passenger car / cargo van
Gasoline
0.355
EPA Table 2
Light-duty truck (crew cab, work van)
Gasoline
0.503
EPA Table 2
Light-duty truck
Diesel
0.523
EPA Table 2
Medium-duty truck (equipment trailer)
Diesel
1.084
EPA Table 2
Heavy-duty truck (dump truck, tanker)
Diesel
1.612
EPA Table 2
Heavy-duty truck (loaded, waste hauling)
Diesel
2.25
EPA Table 2 + load factor
Calculation formula: Vehicle miles × emission factor = kg CO2e. Convert to tCO2e by dividing by 1,000.
What counts as “vehicle miles”: Round-trip distance from your facility or previous job to the loss site, multiplied by the number of trips. Include equipment pickup trips, progress check visits, and equipment retrieval trips. Do not include the vehicle miles of subcontractors — their emissions are captured in their own RCP calculation.
Category 1: Materials Emissions
Emission Factors for Common Water Damage Materials
Material
Unit
kg CO2e per unit
Source
Quaternary ammonium antimicrobial (liquid)
Liter
2.8
EPA EEIO — Chemical manufacturing
Hydrogen peroxide-based antimicrobial
Liter
1.9
EPA EEIO — Chemical manufacturing
Desiccant drying agent (silica gel)
kg
1.4
EPA EEIO — Chemical manufacturing
Disposable Tyvek suit (Category B)
Each
1.2
EPA EEIO — Apparel manufacturing
Nitrile gloves (pair)
Pair
0.3
EPA EEIO — Rubber/plastics
N95 respirator
Each
0.4
EPA EEIO — Medical equipment
P100 half-face respirator cartridge (pair)
Pair
0.8
EPA EEIO — Medical equipment
6-mil polyethylene sheeting
m²
0.55
EPA EEIO — Plastics product manufacturing
HEPA filter (air scrubber, standard)
Each
3.2
EPA EEIO — Industrial machinery
Note on antimicrobial volumes: If you don’t track liters applied per job, use these application rate proxies: Cat 2 jobs — 0.015 liters per sq ft of affected area. Cat 3 jobs — 0.025 liters per sq ft (double application typically required).
Category 5: Waste Emissions
Emission Factors by Waste Type and Disposal Method
Waste Type
Disposal Method
tCO2e per ton
Source
Mixed C&D debris (non-hazardous)
Landfill
0.16
EPA WARM v16
Contaminated porous materials (Cat 2)
Landfill (standard)
0.18
EPA WARM v16 + contamination premium
Contaminated porous materials (Cat 3)
Landfill (regulated)
0.22
EPA WARM v16 + hazmat transport
Disposable PPE and consumables
Landfill
0.25
EPA WARM v16 — mixed plastics
Contaminated water (Cat 3)
Municipal wastewater treatment
0.000272 per liter
EPA WARM v16 — wastewater treatment
Contaminated water (Cat 3)
Permitted treatment facility (tanker)
0.000272 per liter + transport
EPA WARM + tanker transport
Estimating waste weight when you don’t have disposal receipts: Use 2.5 lbs per sq ft of demolished drywall (standard 1/2″ drywall), 3.0 lbs per sq ft of demolished flooring (carpet + pad), 0.8 lbs per sq ft of demolished wood subfloor. For Cat 3 contaminated water: estimate from extractor tank fill cycles × tank capacity.
Category 12: Demolished Building Materials
Material
tCO2e per ton (landfill)
tCO2e per ton (recycled)
Source
Gypsum drywall
0.16
0.02
EPA WARM v16
Carpet + pad
0.33
0.05
EPA WARM v16
Hardwood flooring
-0.12 (carbon storage credit)
-0.18
EPA WARM v16
Vinyl/LVP flooring
0.28
0.08
EPA WARM v16 — plastics
Ceramic tile
0.04
0.01
EPA WARM v16 — inert material
Fiberglass batt insulation
0.33
0.05
EPA WARM v16
Cellulose insulation
0.06
-0.02
EPA WARM v16
Dimensional lumber (framing)
-0.07 (carbon storage credit)
-0.15
EPA WARM v16
Important: Negative values for wood-based materials reflect carbon storage credits under EPA WARM methodology — lumber and hardwood store carbon that is not immediately released when landfilled. Apply these credits only if the material is being landfilled rather than incinerated.
Complete Worked Example: Category 2, Class 3 Commercial Water Loss
Job profile: Washing machine supply line failure, 2,400 sq ft commercial office, second floor. Affected area includes cubicle space and server room (contents moved). Required demolition: 800 sq ft drywall, 600 sq ft carpet. Crew: 2 technicians, 3-day mitigation. Your facility is 24 miles from the job site.
Category 4 — Transportation
2 light trucks × 48 miles round trip × 4 trips (initial, day 2, day 3, equipment pickup) = 384 vehicle-miles 384 × 0.503 kg CO2e/mile = 193 kg CO2e
1 equipment trailer (dehumidifiers, air movers) × 48 miles × 2 trips (drop-off + pickup) = 96 vehicle-miles 96 × 1.084 kg CO2e/mile = 104 kg CO2e
1 dump truck for debris × 14 miles to transfer station × 1 trip = 14 vehicle-miles 14 × 2.25 kg CO2e/mile = 32 kg CO2e
Equipment power source: building electrical supply (Scope 2 — property owner, not included here)
Category 4 total: 329 kg CO2e = 0.33 tCO2e
Category 1 — Materials
Quaternary ammonium antimicrobial: 2,400 sq ft × 0.015 L/sq ft = 36 liters × 2.8 kg CO2e/L = 101 kg CO2e
PPE: 2 technicians × 3 days × 2 Tyvek suits/day = 12 suits × 1.2 kg = 14 kg; 2 × 3 × 4 glove pairs = 24 pairs × 0.3 kg = 7 kg; 2 × 3 × 2 N95 = 12 respirators × 0.4 kg = 5 kg. PPE total: 26 kg CO2e
HEPA filter replacement (2 air scrubbers, 1 filter change each): 2 × 3.2 kg = 6 kg CO2e
This figure — 1.11 tCO2e — is what goes in the Category 4, 1, 5, and 12 rows of the RCP Job Carbon Report delivered to the property manager. The spend-based estimate for a $28,000 job like this (using EPA Services to Buildings factor of approximately 0.10 kg CO2e per dollar) would produce 2.8 tCO2e — more than 2.5x the actual calculated figure. This is why primary data matters.
What is the single most important data point to capture for accurate water damage Scope 3 calculation?
Vehicle mileage. Transportation is typically the largest single emission source and is the most accurately calculated when mileage is documented. All other data points can be estimated from proxies, but vehicle mileage should be captured from actual dispatch records or GPS fleet data for every job.
Can I use the same emission factors for all antimicrobial products?
The EPA EEIO factor for chemical manufacturing (2.8 kg CO2e/liter for quaternary ammonium compounds) is an appropriate default for most antimicrobial treatments. Hydrogen peroxide-based products have a lower factor (1.9 kg CO2e/liter). If your company has specific product lifecycle assessment data, use that in place of the EEIO factor and note the source in your data quality section.
How do I handle a multi-week job that spans two calendar years?
Calculate total emissions for the full job and report the portion attributable to each calendar year based on the percentage of work performed in each year. For most clients, the simpler approach is to report the full job total in the year the job was completed — check with your client’s ESG team which convention they prefer for their Scope 3 inventory.
There is no industry standard for how a restoration contractor should calculate, document, and report the carbon emissions from their work. Not from IICRC. Not from RIA. Not from any trade association or certifying body in the restoration industry.
That absence is becoming a problem. Commercial property managers are facing mandatory Scope 3 emissions disclosures — and restoration contractor activity is squarely in their value chain. Insurance carriers are building ESG criteria into preferred vendor programs. FEMA and federal contracting bodies are increasingly asking about emissions documentation for large-scale disaster response contracts.
When your clients need Scope 3 data from you and there’s no standard for what that data should include or how it should be calculated, everyone loses. The property manager files an inaccurate disclosure. The contractor gets treated as a data gap. The auditor flags the methodology. Nobody benefits.
The Restoration Carbon Protocol exists to fix that.
What the Restoration Carbon Protocol Is
The Restoration Carbon Protocol (RCP) is an industry self-standard for Scope 3 emissions calculation, documentation, and reporting specific to property restoration work. It is built on the GHG Protocol Corporate Value Chain Standard — the globally accepted framework for Scope 3 accounting — and adapted to the specific job types, material categories, waste streams, and operational patterns of the restoration industry.
RCP v1.0 will cover five core restoration job types: water damage mitigation, fire and smoke restoration, mold remediation, asbestos and hazmat abatement, and biohazard cleanup. For each job type, the protocol defines:
Which GHG Protocol Scope 3 categories are relevant
What data points need to be captured per job
What calculation methodology to use for each emissions source
What emission factors apply, sourced from EPA, DEFRA, and ecoinvent databases
What the output format looks like for client delivery
The output is a per-job carbon report — a standardized one-page document any restoration contractor can complete and provide to their commercial clients for their GRESB, CDP, or SB 253 disclosure.
Why a Self-Standard and Not a Trade Association Standard
Trade association standards take years to develop through committee processes. The 2027 deadline doesn’t allow for that timeline. Commercial property managers need something workable now — in 2025 and 2026, as they build their data collection infrastructure ahead of the first required filings.
A published, rigorous, publicly available self-standard that is built on GHG Protocol methodology and uses credible emission factors is more useful to the market right now than a committee process that might produce something better in 2028. The goal of RCP is not to be the final word — it’s to be the first rigorous word, and to create the foundation that a trade association standard can build on when the bandwidth exists.
Self-published standards have established category leadership in other industries. The GHG Protocol itself started as a self-published standard by the World Resources Institute and the World Business Council for Sustainable Development before becoming the global norm. The precedent for rigorous self-published standards setting the terms of an industry conversation is well-established.
The 30-Day Build
RCP v1.0 is being built over 30 days through a structured series of knowledge nodes — each one establishing a piece of the technical framework, validated against GHG Protocol methodology, and published here on Tygart Media as it’s completed.
The publication sequence runs from foundation (what Scope 3 is and why it matters for restoration) through technical framework (job-type-specific calculation methodologies) to commercial application (how to use the framework with clients and in RFP responses) to the full framework document publication.
The Restoration Golf League network of independent restoration contractors will serve as the pilot cohort — providing feedback on the calculation methodology, testing the per-job carbon report format against their actual job data, and validating that the framework is workable for contractors who are running businesses, not sustainability departments.
How to Get Involved
If you are a restoration contractor who wants to be involved in the RCP pilot, a commercial property manager looking for Scope 3 data from your restoration vendor network, an ESG consultant working with commercial real estate clients, or an insurance carrier building ESG criteria into your preferred vendor program — this standard is being built with your needs in mind.
The RCP framework will be published open-access. The knowledge nodes building toward it are published here as they’re completed. Follow along, contribute feedback, and contact Tygart Media if you want to be part of the pilot cohort that validates the framework before v1.0 publication.
What is the Restoration Carbon Protocol?
An industry self-standard for calculating, documenting, and reporting Scope 3 emissions from property restoration work. Built on GHG Protocol methodology, covering five core restoration job types, producing a standardized per-job carbon report that contractors can provide to commercial clients for their ESG disclosures.
Who is building the Restoration Carbon Protocol?
Tygart Media, in collaboration with the Restoration Golf League contractor network. The framework is being developed through a 30-day structured publication process with input from restoration contractors, commercial property managers, and ESG practitioners.
Why isn’t a trade association building this standard?
Trade association standards take years through committee processes. The 2027 deadline requires something workable now. A rigorous self-published standard built on GHG Protocol methodology creates the foundation that a formal trade association process can build on.
Will the RCP be free to use?
Yes. The framework will be published open-access. The goal is adoption, not monetization of the standard itself. Value accrues to contractors who adopt it early and build it into their commercial service offering.
California Senate Bill 253 — the Climate Corporate Data Accountability Act — is the most significant climate disclosure law in US history. It applies to public and private companies with over $1 billion in annual revenue that do business in California. It requires them to disclose Scope 1 and 2 emissions starting in 2026 and Scope 3 emissions starting in 2027. More than 5,000 companies fall within its scope.
Those companies include most of the institutional property owners, REITs, hospital systems, hotel chains, university systems, and commercial real estate operators that hire restoration contractors for their facilities. When they disclose their Scope 3 emissions in 2027, your work will be part of what they’re accounting for.
What SB 253 Actually Requires
SB 253 requires covered companies to publish annual GHG emissions reports, verified by an independent third party, using the GHG Protocol Corporate Standard methodology. The Scope 3 reporting requirement — which takes effect for the 2027 reporting year — means companies must inventory and disclose emissions across all relevant value chain categories, including emissions from their contractors and suppliers.
The California Air Resources Board (CARB) is developing implementing regulations that will specify the exact requirements. What’s already clear from the statute is that companies cannot simply exclude contractor emissions because data is hard to collect — they must make good-faith efforts to obtain primary data from their supply chain, and where primary data isn’t available, they must use approved estimation methodologies.
The third-party verification requirement is significant. Unlike voluntary ESG reporting where companies self-certify their numbers, SB 253 disclosures will be reviewed by independent auditors. That means the quality of the underlying data — including contractor-provided emissions data — will be scrutinized in a way it hasn’t been before.
The Timeline That Matters for Contractors
The 2027 reporting year means companies will begin collecting 2027 emissions data in early 2027 and filing reports by the deadline established in CARB regulations. To provide verified, primary-data emissions figures from their restoration contractors, property managers need to have data collection processes in place before the jobs happen — not after.
That means the real action window for restoration contractors is now. Property managers who are serious about their SB 253 compliance are already building vendor data collection systems and ESG questionnaires. Contractors who can respond to those questionnaires with actual per-job emissions data will be in a materially different position than contractors who can’t.
The companies that are largest in terms of SB 253 coverage — large REITs, national property management companies, institutional operators — are the ones most likely to make ESG data capability a formal criterion in vendor selection. They’re also the clients where losing a preferred vendor designation costs the most.
What SB 253 Means Beyond California
California’s disclosure laws have historically set national standards. SB 253 applies to companies “doing business in California” — which includes companies headquartered elsewhere that have California operations or customers. Many of the large commercial real estate operators that SB 253 covers operate nationally, which means their vendor data requirements will apply nationally even if the law itself is California-specific.
The EU’s Corporate Sustainability Reporting Directive (CSRD) is already in effect and is pulling US companies with European operations into Scope 3 reporting as well. The direction of travel is global and accelerating regardless of what happens with US federal climate policy.
For restoration contractors that do any commercial work with institutional property owners, the 2027 deadline should be on their planning horizon now — not in 2026 when their largest clients are scrambling to collect data before the filing deadline.
What is California SB 253?
The Climate Corporate Data Accountability Act, signed in 2023. It requires companies with over $1 billion in annual revenue doing business in California to report Scope 1 and 2 emissions starting 2026 and Scope 3 emissions starting 2027, verified by an independent third party using the GHG Protocol methodology.
How many companies does SB 253 affect?
More than 5,000 companies. Critically, the law applies to companies “doing business in California” regardless of where they are headquartered — capturing national and multinational companies with California operations or customers.
Does SB 253 directly require restoration contractors to report emissions?
Not directly — the law applies to companies with over $1 billion in revenue. But those companies must collect Scope 3 emissions data from their supply chain, which includes restoration contractors. The obligation on the contractor is indirect but practically significant for commercial work.
What happens if a restoration contractor can’t provide emissions data to their commercial clients?
The property manager will use spend-based estimates instead, which are less accurate and more difficult to defend in a third-party audit. Over time, inability to provide primary emissions data is likely to become a disadvantage in commercial vendor selection processes.
The GHG Protocol Corporate Value Chain Standard — the framework that governs Scope 3 emissions accounting globally — defines 15 categories of indirect emissions across the upstream and downstream value chain. Understanding which of these categories apply to restoration work is the first step in building a calculation methodology that ESG auditors will accept.
Restoration work is unusual in that it touches multiple categories simultaneously. A single significant job can generate measurable emissions across four or more categories — which is exactly why restoration needs its own calculation framework rather than a generic contractor template.
The Four Primary Categories for Restoration Work
Category 1 — Purchased Goods and Services
This category covers the emissions associated with producing the goods and services a company purchases. For a commercial property manager hiring a restoration contractor, this means the emissions embedded in everything the contractor uses on the job: antimicrobial treatments, drying agents, HEPA filters, packaging materials, replacement drywall, subflooring materials.
In practice, Category 1 is the hardest to calculate precisely because it requires knowing the embodied carbon of specific materials. The Restoration Carbon Protocol approach uses established emission factor databases (EPA, ecoinvent) to assign representative values to the most common restoration material categories, allowing contractors to calculate Category 1 contributions from their materials list without commissioning a lifecycle assessment.
Category 4 — Upstream Transportation and Distribution
This category covers transportation emissions upstream of the reporting company — meaning the emissions from moving goods and equipment to the job site. For restoration contractors, this primarily means vehicle fleet emissions: the fuel burned driving trucks, vans, and equipment trailers to the loss site and back.
Category 4 is typically the easiest restoration emissions category to calculate. Vehicle emissions can be calculated from fuel consumption records or from mileage multiplied by vehicle-type emission factors. Most fleet management systems already capture this data.
Category 5 — Waste Generated in Operations
This category covers emissions from waste generated during the contractor’s service delivery — the debris, damaged materials, contaminated water, and hazardous materials that restoration work produces and that are disposed of on behalf of the property owner.
Category 5 is highly variable by job type. A Category 3 water loss with sewage contamination generates different waste streams than a Category 1 clean water extraction. A fire loss generates smoke-contaminated debris with different disposal requirements than mold remediation waste. The Restoration Carbon Protocol maps waste types by job category to appropriate disposal emission factors from EPA and industry waste management data.
Category 12 — End-of-Life Treatment of Sold Products
This category applies when restoration work involves removing and disposing of building components — flooring, drywall, insulation, ceiling tiles, cabinetry — that are treated as end-of-life materials. The emissions from disposing of these materials are counted here rather than in Category 5 when the materials originated as “sold products” rather than process waste.
For large reconstruction-phase restoration projects, Category 12 can be a significant emissions source. The distinction between Category 5 and Category 12 matters for accurate reporting; the Restoration Carbon Protocol provides decision criteria for classifying demolition debris correctly.
Two Secondary Categories That Apply in Specific Situations
Category 2 — Capital Goods
Relevant when restoration work involves the purchase and installation of new equipment on behalf of the property — replacement HVAC components, new water heaters, emergency generators. The embodied carbon of newly installed capital equipment counts under this category for the property manager’s disclosure.
Category 13 — Downstream Leased Assets
Relevant for property management companies that own the buildings being restored. When restoration work affects leased spaces and the property manager is accounting for emissions from tenant operations, the restoration work’s contribution to improving (or temporarily worsening) building energy performance can affect Category 13 calculations.
The Practical Implication for Contractors
The four primary categories — 1, 4, 5, and 12 — are present in virtually every significant restoration job. A contractor who can calculate and report emissions in these four categories for each job has 85 to 90 percent of what most commercial property managers need for their Scope 3 disclosure.
The Restoration Carbon Protocol v1.0 focuses exclusively on these four categories, with secondary categories addressed in supplemental guidance. The goal is a framework that produces defensible, auditor-acceptable numbers from data that restoration contractors already capture in their job management systems.
How many GHG Protocol Scope 3 categories apply to restoration work?
At minimum four primary categories on most significant jobs: Category 1 (purchased goods and services), Category 4 (upstream transportation), Category 5 (waste generated in operations), and Category 12 (end-of-life treatment of materials). Two additional categories apply in specific situations.
Which Scope 3 category covers the emissions from driving to job sites?
Category 4 — Upstream Transportation and Distribution. Vehicle emissions from driving to and from job sites are typically the easiest restoration emissions to calculate and are often the largest single category for smaller jobs.
How are waste disposal emissions classified?
Process waste from restoration operations falls under Category 5 (Waste Generated in Operations). Building materials removed and disposed of during reconstruction may fall under Category 12 (End-of-Life Treatment of Sold Products). The Restoration Carbon Protocol provides decision criteria for classifying demolition debris correctly.
What is the Restoration Carbon Protocol’s approach to Category 1 materials emissions?
Rather than requiring lifecycle assessments, the RCP uses established emission factor databases (EPA EEIO, ecoinvent) to assign representative carbon intensities to common restoration material categories, allowing calculation from a standard materials list.