How are Facility Risk Ratings calculated?
The article explains how Facility Risk Ratings within Facility Risk Scorecards are assigned in the RBA's Chemical Platform
Table of Contents
How are Facility Risk Ratings calculated?
RBA's Chemical Platform enables RBA members and their suppliers to determine qualitative Facility Risk Ratings of Very Low through Very High using the standardized Facility Risk Rating methodology. This methodology may be used to support materiality assessments and risk-based supply chain due diligence on chemical management risks. For Facility Risk Ratings to be accurate, comparable, and conformant to this methodology, Chemical Platform users must generate Facility Risk Scorecards that account for all chemical products (i.e., process chemicals, chemicals in products, and others) being consumed at the facilities. Although Custom Facility Risk Scorecards with limited chemical consumption and usage data may be generated to satisfy stakeholder demands such as materials restrictions assurance and ecolabel conformance, Facility Risk Scorecards must account for 100% of chemical products being consumed at the facility.
Facility Risk Ratings are primarily based on two factors; weighted average Product Hazard Ratings and weighted average Exposure Ratings, which are each weighted on the volume of chemical products being consumed. Facility Risk Ratings are determined using these two factors along with Chemical Risk Ratings matrix as described in the following 3 steps of the Facility Risk Rating methodology.
Facility Risk Rating Methodology
Step 1: Determine weighted average Product Hazard Rating
Product Hazard Ratings are based on formulation-level hazard data derived from Globally Harmonized System of Classification and Labelling of Chemicals (GHS)5F information disclosed in chemical products’ Safety Data Sheets (SDSs) and ingredient-level hazard data derived from ChemFORWARD Hazard Band ratings based on comprehensive, best-in-class chemical hazard assessments (CHAs). Using codified GHS hazard statements (H-codes) contained in Section 2: Hazard Identification of SDSs, formulation-level hazards are assigned hazard ratings of Very Low through Very High (quantified as 1 through 5) based on Table 1. Using substance CAS numbers contained in Section 3: Composition/Information on Ingredients of SDSs, ingredient-level hazards are assigned hazard ratings of Very Low through Very High (quantified as 1 through 5) using ChemFORWARD Hazard Band ratings based on Table 2. The highest hazard rating between all formulation-level hazard ratings and all ingredient-level hazard ratings is assigned as the Product Hazard Rating of the chemical product.
Table 1: Formulation-level Hazard Ratings
Hazard Class |
Hazard Category, Sub-Category |
H-Codes |
Hazard Rating |
|---|---|---|---|
Explosives |
Division 1.1 |
H201 |
Moderate (3) |
Explosives |
Division 1.2 |
H202 |
Moderate (3) |
Explosives |
Division 1.3 |
H203 |
Moderate (3) |
Explosives |
Division 1.4 |
H204 |
Low (2) |
Explosives |
Division 1.5 |
H205 |
Very Low (1) |
Explosives |
Division 1.6 |
None |
Very Low (1) |
Explosives |
Unstable Explosive |
H200 |
High (4) |
Flammable gases |
Category 1A, Flammable gas |
H220 |
High (4) |
Flammable gases |
Category 1A, Pyrophoric gas |
H220, H232 |
High (4) |
Flammable gases |
Category 1A, Chemically unstable gas A |
H220, H230 |
High (4) |
Flammable gases |
Category 1A, Chemically unstable gas B |
H220, H231 |
High (4) |
Flammable gases |
Category 1B |
H221 |
Moderate (3) |
Flammable gases |
Category 2 |
H221 |
Low (2) |
Aerosols |
Category 1 |
H222, H229 |
Moderate (3) |
Aerosols |
Category 2 |
H223, H229 |
Moderate (3) |
Aerosols |
Category 3 |
H229 |
Low (2) |
Gases under pressure |
Compressed gas |
H280 |
Low (2) |
Gases under pressure |
Dissolved gas |
H280 |
Low (2) |
Gases under pressure |
Liquefied gas |
H280 |
Low (2) |
Gases under pressure |
Refrigerated liquefied gas |
H281 |
Low (2) |
Flammable liquids |
Category 1 |
H224 |
High (4) |
Flammable liquids |
Category 2 |
H225 |
Moderate (3) |
Flammable liquids |
Category 3 |
H226 |
Low (2) |
Flammable liquids |
Category 4 |
H227 |
Very Low (1) |
Flammable solids |
Category 1 |
H228 |
Moderate (3) |
Flammable solids |
Category 2 |
H228 |
Low (2) |
Self-reactive substances and mixtures |
Type A |
H240 |
High (4) |
Self-reactive substances and mixtures |
Type B |
H241 |
High (4) |
Self-reactive substances and mixtures |
Type C |
H242 |
Moderate (3) |
Self-reactive substances and mixtures |
Type D |
H242 |
Moderate (3) |
Self-reactive substances and mixtures |
Type E |
H242 |
Low (2) |
Self-reactive substances and mixtures |
Type F |
H242 |
Low (2) |
Self-reactive substances and mixtures |
Type G |
None |
Low (2) |
Pyrophoric liquids |
Category 1 |
H250 |
Moderate (3) |
Pyrophoric solids |
Category 1 |
H250 |
Moderate (3) |
Self-heating substances and mixtures |
Category 1 |
H251 |
Moderate (3) |
Self-heating substances and mixtures |
Category 2 |
H252 |
Low (2) |
Substances and mixtures, which in contact with water, emit flammable gases |
Category 1 |
H260 |
Moderate (3) |
Substances and mixtures, which in contact with water, emit flammable gases |
Category 2 |
H261 |
Low (2) |
Substances and mixtures, which in contact with water, emit flammable gases |
Category 3 |
H261 |
Low (2) |
Oxidizing gases |
Category 1 |
H270 |
Moderate (3) |
Oxidizing liquids |
Category 1 |
H271 |
Moderate (3) |
Oxidizing liquids |
Category 2 |
H272 |
Low (2) |
Oxidizing liquids |
Category 3 |
H272 |
Very Low (1) |
Oxidizing solids |
Category 1 |
H271 |
Moderate (3) |
Oxidizing solids |
Category 2 |
H272 |
Low (2) |
Oxidizing solids |
Category 3 |
H272 |
Very Low (1) |
Organic peroxides |
Type A |
H240 |
High (4) |
Organic peroxides |
Type B |
H241 |
High (4) |
Organic peroxides |
Type C |
H242 |
Moderate (3) |
Organic peroxides |
Type D |
H242 |
Moderate (3) |
Organic peroxides |
Type E |
H242 |
Low (2) |
Organic peroxides |
Type F |
H242 |
Low (2) |
Organic peroxides |
Type G |
None |
Low (2) |
Corrosive to metals |
Category 1 |
H290 |
Low (2) |
Desensitized explosives |
Category 1 |
H206 |
Moderate (3) |
Desensitized explosives |
Category 2 |
H207 |
Moderate (3) |
Desensitized explosives |
Category 3 |
H207 |
Low (2) |
Desensitized explosives |
Category 4 |
H208 |
Low (2) |
Acute toxicity |
Dermal, Category 1 |
H310 |
Very High (5) |
Acute toxicity |
Dermal, Category 2 |
H310 |
High (4) |
Acute toxicity |
Dermal, Category 3 |
H311 |
Moderate (3) |
Acute toxicity |
Dermal, Category 4 |
H312 |
Low (2) |
Acute toxicity |
Dermal, Category 5 |
H313 |
Very Low (1) |
Acute toxicity |
Inhalation, Category 1 |
H330 |
Very High (5) |
Acute toxicity |
Inhalation, Category 2 |
H330 |
High (4) |
Acute toxicity |
Inhalation, Category 3 |
H331 |
Moderate (3) |
Acute toxicity |
Inhalation, Category 4 |
H332 |
Low (2) |
Acute toxicity |
Inhalation, Category 5 |
H333 |
Very Low (1) |
Acute toxicity |
Oral, Category 1 |
H300 |
High (4) |
Acute toxicity |
Oral, Category 2 |
H300 |
Moderate (3) |
Acute toxicity |
Oral, Category 3 |
H301 |
Low (2) |
Acute toxicity |
Oral, Category 4 |
H302 |
Very Low (1) |
Acute toxicity |
Oral, Category 5 |
H303 |
Very Low (1) |
Skin corrosion/irritation |
Category 1 |
H314 |
High (4) |
Skin corrosion/irritation |
Category 1A |
H314 |
High (4) |
Skin corrosion/irritation |
Category 1B |
H314 |
High (4) |
Skin corrosion/irritation |
Category 1C |
H314 |
High (4) |
Skin corrosion/irritation |
Category 2 |
H315 |
Moderate (3) |
Skin corrosion/irritation |
Category 3 |
H316 |
Low (2) |
Serious eye damage/eye irritation |
Category 1 |
H318 |
High (4) |
Serious eye damage/eye irritation |
Category 2 |
H319 |
Moderate (3) |
Serious eye damage/eye irritation |
Category 2A |
H319 |
Moderate (3) |
Serious eye damage/eye irritation |
Category 2B |
H320 |
Low (2) |
Respiratory sensitization |
Category 1 |
H334 |
High (4) |
Respiratory sensitization |
Category 1A |
H334 |
High (4) |
Respiratory sensitization |
Category 1B |
H334 |
High (4) |
Skin sensitization |
Category 1 |
H317 |
High (4) |
Skin sensitization |
Category 1A |
H317 |
High (4) |
Skin sensitization |
Category 1B |
H317 |
High (4) |
Germ cell mutagenicity |
Category 1 |
H340 |
Very High (5) |
Germ cell mutagenicity |
Category 1A |
H340 |
Very High (5) |
Germ cell mutagenicity |
Category 1B |
H340 |
Very High (5) |
Germ cell mutagenicity |
Category 2 |
H341 |
High (4) |
Carcinogenicity |
Category 1 |
H350 |
Very High (5) |
Carcinogenicity |
Category 1A |
H350 |
Very High (5) |
Carcinogenicity |
Category 1B |
H350 |
Very High (5) |
Carcinogenicity |
Category 2 |
H351 |
High (4) |
Reproductive toxicity |
Additional category for effects on or via lactation |
H362 |
High (4) |
Reproductive toxicity |
Category 1 |
H360 |
Very High (5) |
Reproductive toxicity |
Category 1A |
H360 |
Very High (5) |
Reproductive toxicity |
Category 1B |
H360 |
Very High (5) |
Reproductive toxicity |
Category 2 |
H361 |
High (4) |
Specific target organ toxicity – single exposure |
Category 3, Narcotic effects |
H336 |
Low (2) |
Specific target organ toxicity – single exposure |
Category 3, Respiratory tract irritation |
H335 |
Low (2) |
Specific target organ toxicity – single exposure |
Category 1 |
H370 |
High (4) |
Specific target organ toxicity – single exposure |
Category 2 |
H371 |
Moderate (3) |
Specific target organ toxicity – repeated exposure |
Category 1 |
H372 |
High (4) |
Specific target organ toxicity – repeated exposure |
Category 2 |
H373 |
Moderate (3) |
Aspiration hazard |
Category 1 |
H304 |
High (4) |
Aspiration hazard |
Category 2 |
H305 |
Moderate (3) |
Hazardous to aquatic environment, long-term |
Chronic 1 |
H410 |
Moderate (3) |
Hazardous to aquatic environment, long-term |
Chronic 2 |
H411 |
Low (2) |
Hazardous to aquatic environment, long-term |
Chronic 3 |
H412 |
Very Low (1) |
Hazardous to aquatic environment, long-term |
Chronic 4 |
H413 |
Very Low (1) |
Hazardous to aquatic environment, short term |
Acute 1 |
H400 |
Moderate (3) |
Hazardous to aquatic environment, short term |
Acute 2 |
H401 |
Low (2) |
Hazardous to aquatic environment, short term |
Acute 3 |
H402 |
Very Low (1) |
Hazardous to the ozone layer |
Category 1 |
H420 |
High (4) |
Table 2: Ingredient-level Hazard Ratings
ChemFORWARD Hazard Band |
Implications |
Hazard Rating |
|
Low hazard and low risk
|
Very Low (1)
|
|
Some moderate hazards but low risk
|
Low (2)
|
|
Moderate hazard, moderate risk or uncertainty that could result in moderate risk
|
Moderate (3)
|
|
Moderate to high hazard; emerging regulatory risk (classification may be based on a chemical class/group approach)
|
High (4)
|
|
High hazards and high risk in most scenarios
|
Very High (5)
|
|
CHA completed with excessive data gaps, rating is not possible
|
Moderate (3)
|
|
Unknown; Request a CHA to inform decision
|
Moderate (3)
|
Note – If a chemical product’s SDS doesn’t disclose any CAS numbers for ingredients or H-Codes for the formulation, a Product Hazard Rating of Very Low (1) is assigned to the chemical product.
Note – If substances result in ChemFORWARD Hazard Band ratings of “U” or “?”, ingredient-level hazard ratings of Moderate (3) are assigned to those substances to avoid over- or under-rating such substances and ChemFORWARD uses this information to help prioritize future development of CHAs.
After determining Product Hazard Ratings (PHRs) and annual volumes consumed for all chemical products, facilities' weighted average PHR may be determined using the following formula:

Note – Calculated weighted average PHR must be rounded up to the nearest whole number (e.g., weighted average PHR of 2.5 is rounded up to 3 for Moderate).
The below example demonstrates how a weighted average PHR may be determined based on the given data.
Given:
- Chemical A has a PHR of High (4) and annual consumption of 1,000 kg
- Chemical B has a PHR of Low (2) and annual consumption of 300 kg
- Chemical C has a PHR of Very High (5) and annual consumption of 500 kg
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Step 2: Determine weighted average Exposure Rating
Exposure Ratings are based on three data variables originally derived from CEPN’s PCDC Tool and now also collected by RBA’s Chemical Platform; the number of persons with potential exposures to the chemical product (P rating) based on Table 3, the application method of the chemical product usage (A rating) based on Table 4, and the ventilation control measure in place (V rating) based on Table 5. Exposure Ratings for each chemical usage are calculated by the following formula:

Table 3: Persons with Potential Exposures
# of Persons |
P Rating |
0-10 |
1 |
10-20 |
2 |
20-50 |
3 |
50-100 |
5 |
100-500 |
7 |
500-1,000 |
9 |
Over 1,000 |
10 |
Table 4: Application Methods
Application Method |
A Rating |
Manual |
10 |
Both |
5 |
Automated |
0.1 |
Table 5: Ventilation Control Measures
Ventilation Control Measure |
V Rating |
Outdoor location with no local exhaust ventilation |
5 |
Indoor location with no ventilation |
10 |
Indoor with general room ventilation |
5 |
Indoor or outdoor with local exhaust ventilation |
2 |
Indoor or outdoor with exhausted enclosure |
0.1 |
Similar to PHRs, calculated Exposure Ratings are assigned qualitative Exposure Ratings of Very Low through Very High (quantified as 1 through 5) based on Table 6.
Table 6: Qualitative Exposure Ratings
Calculated Exposure Rating |
Qualitative Exposure Rating |
≤ 1 |
Very Low (1) |
>1 to ≤10 |
Low (2) |
>10 to ≤25 |
Moderate (3) |
>25 to ≤100 |
High (4) |
>100 |
Very High (5) |
After determining qualitative Exposure Ratings (ERs) and annual volumes consumed for all chemical products, facilities' weighted average ER may be determined using the following formula:
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Note – Calculated weighted average ER must be rounded up to the nearest whole number (e.g., weighted average ER of 1.5 is rounded up to 2 for Low).
The below example demonstrates how a weighted average ER may be determined based on the given data.
Given:
- Chemical A has a ER of High (4) and annual consumption of 1,000 kg
- Chemical B has a PHR of Low (2) and annual consumption of 300 kg
- Chemical C has a PHR of Very High (5) and annual consumption of 500 kg
![]()
Step 3: Determine overall Facility Risk Rating using Chemical Risk Ratings matrix
After both the weighted average PHR and weighted average ER are determined, the overall Facility Risk Rating may be determined by using the Chemical Risk Ratings matrix illustrated in Figure 1.
Figure 1: Chemical Risk Ratings Matrix

The below example demonstrates how an overall Facility Risk Rating may be determined using the Chemical Risk Ratings matrix based on the given data.
Given:
- Weighted average PHR is High (4)
- Weighted average ER is Low (2)

In this example, the Facility Risk Rating = Moderate






