Occupational Exposure Banding and Exposure Risk

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Susan Ripple, MS, CIH, Fellow

Global Manager – Industrial Hygiene

The Dow Chemical Company

Midland, MI

 Value of Occupational Exposure Bands (OEB) to supplement other authoritative OELs

 Value of OEBs to the industrial hygiene process

(ERAM)

 OEB Framework

 Exposure Risk Assessment & Management

(ERAM)

How many of you are familiar with the AIHA

Exposure Assessment

Strategies” for performing “qualitative exposure assessment”?

Traditional IH Definition:

Anticipate

Recognize

Evaluate

Risk Assessment

(Qualitative or Quantitative)

Control

Risk Management

 “ERAM is a concise framework to help illustrate the core skills of the industrial hygiene profession.

Taken at a high level, ERAM is the anticipation, recognition, evaluation and control of chemical, physical and biological hazards to prevent illness and injury in workers, customers and communities.”

 It is the science of understanding and managing human exposure risks.

 ERAM is the core competency of IH. Owning the science of ERAM both strengthens our CORE and expands our market opportunities.

 ERAM is an important skill set needed for parts of…

▪ Sustainability

▪ Product Stewardship

▪ EHS Management

 When we are viewed as being ERAM experts, these

Allied Professions will put a higher value on our services. This creates greater need for internal and external IH Consultants

IH

Expert

IH Generalist

EHS Generalist

Affiliated Professionals

Level of

ERAM

Expertise

Hypothetical Amount of “ERAM Expertise” for each job type…. (illustration only)

Percent of ERAM needed in job

100%

IH

Expert

IH Generalist

50-100%

5-50%

EHS Generalist

Affiliated Professionals 1-15%

Exposure Management

Exposure risk assessment knowledge gaps

(Controls & Programs)

<2000 OELs

<2% REACH

HAZARD

Assessment

EXPOSURE

Assessment

Chemicals with OELs

Occupational

Exposure

Bands (OEBs)

& Exposure

Limits (OELs)

Occupational

Health Hazard

Criteria & Process

~21,000,000 commercialavailable chemicals; >107,000

REACH

Exposure Risk

Assessment

( modeling, monitoring, analogy)

Courtesy of

Elizabeth Pullen and ERAM

Working Group

IH Expertise

Understanding

Exposure & Controls

“Exposure Gap”

~21,000,000 commercially available chemicals

107,067 REACH* registrations (1-3-

11) for >1000 tons production volume or those of high concern

 But…only ~ 500 PELs, ~ 650 RELs, ~

125 WEELs, ~ 650 TLVs

*REACH – Registration, Evaluation, Authorization, and Restriction of Chemicals

~21,000,000 commercially available chemicals

107,067 REACH* registrations (1-3-

11) for >1000 tons production volume or those of high concern

But…only ~ 500 PELs, ~ 650 RELs, ~

125 WEELs, ~ 650 TLVs

*REACH – Registration, Evaluation, Authorization, and Restriction of Chemicals

 Hygienists prefer the more official peerreviewed Traditional OELs ,

“You can’t always get what you want, but if you try some times you might find, you’ll get what you need” – Mick

Jaeger

14

 Occupational Exposure Banding provides a mechanism for the evaluation of hazard and risk to offset the misconceptions by employers and workers that a substance must be non-toxic if there is not an OEL!

MIHS

 “Hazard banding is simply the first step in the

control banding process

Susan D. Ripple. The Synergist: October 2009

 “Occupational Exposure Bands” are a more appropriate description of Hazard Grouping or

Hazard Banding

Donna Heidel and Susan Ripple. The Synergist: April 2012

BOHS OEL-Setting Plenary

OEBs for a chemical provide a range of acceptable exposure levels based on expert evaluation of the doseresponse relationships provided through animal testing.

Develop the framework to systematically evaluate occupational hazards of chemicals without authoritative OELs (PELs, RELs,

TLVs, etc.) and communicate the hazards in terms of occupational exposure bands

(OEBs).

Facilitates more rapid evaluation of health risk & provides guidance for many materials without OELs

Highlights areas where data are missing (highlights uncertainties)

Identifies hazards to be evaluated for elimination or substitution

Aligned with GHS for hazard communication

Supports the definition of OEL-ranges for families of materials

1.

2.

3.

4.

5.

6.

Establish minimum viable dataset, including data quality requirements

Establish process and decision logic

Validate data endpoints and band cut points, process, and decision logic

Identify data sources

Develop NIOSH guidance

Educate stakeholders

 Criteria include qualitative, semi-quantitative, and quantitative data for each toxicological endpoint

Acute toxicity

Skin corrosion/irritation

Serious eye damage/eye irritation

Respiratory and skin sensitization

Germ cell mutagenicity

Carcinogenicity

Specific target organ toxicity, both single and repeated exposure

Reproductive toxicity

 OEB toxicological endpoints are aligned with

GHS classification and labeling system*

 Important goal is to relate potency of each toxicological hazard-banding endpoint to

GHS hazard statements and categories, when possible

 Data quality is also considered

Band

Signal Word

A

Warning

> 1,000 µg/m 3

B

Warning

C (default)

Danger

> 100 and < 1,000 µg/m 3 > 10 and < 100 µg/m 3

D

Danger

> 1 and < 10 µg/m 3

E

Danger

< 1 µg/m 3

OEL Ranges

Examples of Health

Outcomes and

Potency

Considerations

Minor, reversible health effects occurring at high doses. Skin and eye irritation.

Examples of GHS

Hazard Statements and Hazard

Categories

> 1000 ppm

May cause drowsiness or dizziness

> 100 - < 1000 ppm > 10 - < 100 ppm > 1 - < 10 ppm < 1 ppm

Reversible organ toxicity, skin and eye corrosion

(reversible), possible dermal sensitizer at high doses.

Irreversible organ toxicity at high doses, irreversible skin and eye corrosion, dermal sensitizer at moderate doses.

Irreversible organ toxicity at low doses, in vivo genotoxicity, dermal sensitizer at low doses, evidence of mutagenicity, potential developmental and reproductive toxicants.

Human carcinogens at low doses, respiratory sensitization

Harmful if inhaled (4).

Harmful in contact with skin (4).

Toxic if inhaled (3).

Toxic in contact with skin (3). Suspected of causing cancer (2).

May cause damage to organs (2)

Fatal if inhaled (2).

Fatal in contact with skin (1). Causes damage to organs (1).

May cause cancer (by route of exposure) —1A or B. Presumed or known human reproductive toxicant

(1A or 1B). Causes damage to organs through prolonged or repeated exposure (1)

Fatal if inhaled (1).

Fatal in contact with skin (1). May cause cancer (by route of exposure) —1A. May cause allergy or asthma symptoms or breathing difficulties if inhaled (1A resp.).

Known human repro toxicant (1A). Causes damage to organs through prolonged or repeated exposure (1)

MIHS

A B

A B

C

C D

D-E

E

A B C D E

A B C D E

Tier 1a—Qualitative

Use GHS Hazard Phrases to identify chemicals with potential for irreversible health effects at relatively low doses (Band

D-E) or remain at default Band C

Tier 1b—Semi-quantitative

Use GHS Hazard Categories to assign chemicals into Bands D or E or remain at default Band C

Tier 2—Quantitative

Determine point of departure, factoring data availability, hierarchy, and quality to support assigning chemicals into Bands

A, B, or C

Tier 3—Weight of Evidence

Involves integration of all available data and determining the degree of conviction of the outcome.

• Tier 1 a & b: GHS hazard code or statement from SDS or the preferred GHS database (Annex VI, REACH, GESTIS, etc.).

Hazard category will further define Bands D and E

— User: H&S generalist; may overestimate risk

Warning – negative results vs. absence of data

• Tier 2: quantitative data from authoritative sources

— User: skilled industrial hygienist

• Tier 3: toxicological weight of evidence – determine the critical study from which a scientifically sound point of departure (POD) can be determined

— User: toxicologist or experienced industrial hygienist

Chemical for

OEB

Tier 1 a & b

Identify Bands D-E from Default Band C

Authoritative

OEL available?

no

Health statements available?

yes

D or E statement?

yes

Band D-E assigned yes no no

No OEB necessary

Band C default assigned

Band C default assigned

Tier 2 process to determine

Band A or B

Need to define

Band D vs.

E?

yes

Review available

Hazard categories no

Remain at Band

D-E

E Hazard categories

?

no

D Hazard categories

?

yes

Assign Band E yes

Assign Band D

 Using GHS hazard statements or codes (qualitative hazard banding), for most criteria, cannot separate the “D” from the “E” bands

Acute toxicity H codes: H300, H330, H310

Sensitization H code: H334

Germ cell mutagenicity: H340

Carcinogenicity: H350

Toxic to reproduction: H360f, H360d, or H360fd

STOT(RE): H372

 Using the GHS hazard category and/or a Tier II process will be required to separate D from E

1-bromopropane

TIER 1a

 Signal word: danger

 H360FD: May damage fertility or the unborn child (D or E)

▪ OSHA-GHS: Presumed human reproductive toxicant

 H373: May cause damage to organs through prolonged or repeated exposure

(STOT-RE-2)

H319: Causes serious eye irritation

H335: May cause respiratory irritation

H315: Causes skin irritation

H336: May cause drowsiness or dizziness

TIER 1a outcome: Band D-E

TIER 1b

 Hazard Category Repro 1B

Tier 1b outcome: Band D: (1-10 ppm)

 TLV: 10 ppm

• OEB based on point of departure (POD) at which adverse effects are observed o LD50 (oral and dermal) or LC50 (inhalation) for acute toxicity data; o RD50 (in mice) for sensory irritation; o Irritation threshold (mice, rats or human volunteers) for irritation; o NOAEL, BMDL or LOAEL for target organ systemic toxicity, developmental/reproductive toxicity; and o CSFs, IUR, TD

05

/TC

05

, NSRLs (CalEPA Prop 65) of tumorigenic doses for carcinogenicity (still being investigated)

Tier 1 Process results in Band C

Endpoint PODs from authoritative reviews

Score data quality and relevance

Establish Total

Determinant

Score (TDS)

Tier 2

Can Band A or B be considered?

Does TDS exceed threshold for minimum, quality dataset?

yes

Establish OEB no Data insufficient for OEB, “C” default band

TDS reflects the availability of qualitative info and/or quantitative data for each endpoint under consideration. Endpoint scores include data relevance and quality factors. TDS is the sum of the endpoint scores.

Total Determinant Score

Endpoint

LD50 (Oral)

LD50 (Dermal)

Acute Toxicity

LC50 (Gases)

LC50 (Vapors)

LC50

(Dusts/mists)

Skin Corrosion / Irritation

Serious Eye Damage

Eye Damage / Irritation

Respiratory Sensitization

Skin Sensitization

Germ Cell Mutagenicity

Carcinogenicity

Reproduction

Specific Target Organ (Single

Exposure)

Specific Target Organ (Repeated

Exposure)

A B

Bands

C D E Quality

Data

Relevance

Total Overall

Criteria endpoints and band cut points

Process

Decision logic

Modify based on validation results

Finalize criteria for each band, including weight of evidence and dose-response considerations

Develop process, decision logic, and algorithms

Validate process and tools

Develop stakeholder education materials and guidance document

Identify data sources

 NIOSH guidance

 Overall process, including the decision logic

 Tools to facilitate finding and evaluating hazard data and assign chemicals to hazard bands

 Education materials for H&S professionals, managers, and workers

MIHS

Hazard group

A -Skin and eye irritants

B - Harmful on single exposure

C -Severely irritating & corrosive, skin sensitizers

D -Very toxic on single exposure, reproductive hazard

E - Carcinogen, occupational asthma

S: Skin and eye contact

Target airborne concentration range for

Control Banding

>1-10 mg/m ppm vapor

3 dust or >50-500

>01-1 mg/m 3 dust or >5-50 ppm vapor

>0.01-0.1 mg/m 3 dust or >0.5-5 ppm vapor

< 0.01 mg/m 3 dust or < 0 5 ppm vapor

Seek Specialist Advice

Prevention or reduction of skin and/or eye exposure

B - E

39/23/24/25;

R phrases*

36; 38; 36/38; 65;66; All substances that do not have R phrases in groups

20; 20/21; 20/21/22; 20/22; 21; 21/22;

22; 40/20/21/22;33;67

23; 23/24; 23/24/25; 23/25; 24; 24/25;

25; 34; 35; 36/37; 36/37/38; 37; 37/38;

41; 43; 48/20; 48/20/21; 48/20/21/22;

48/20/22; 48/21; 48/21/22; 48/22;

26; 26/27; 26/27/28; 26/28; 27; 27/28;

28; Carc Cat 3 R40; 48/23; 48/23/24;

48/23/24/25; 48/23/25; 48/24;

48/24/25; 48/25; 60; 61; 62; 63;

39/26/27/28

Muta Cat 3 R40; 42; 42/43; 45; 46;

49; 68

21; 24; 27; 34; 35; 36; 38; 41; 43;

48/21; 48/24;

39/24;39/27;40/21;66;plus R -phrase combinations containing these. Sk

GHS Hazard Classification (class/level)

Acute toxicity (lethality), any route, class 5;

Skin irritancy class 2 or 3;

Eye irritancy class 2;

All dusts and vapors not allocated to another band

Acute toxicity (lethality), any route, class 4;

Acute toxicity (systemic), any route, class 2

Acute toxicity (lethality), any route, class 3;

Acute toxicity (systemic), any route, class 1;

Corrosivity, subclass 1A, 1B or 1C; Eye irritancy class 1;

Respiratory system irritancy (GHS criteria to be agreed);

Skin sensitization;

Repeated exposure toxicity, any route, class 2

Acute toxicity (lethality), any route, class 1 or 2;

Carcinogenicity class 2;

Repeated exposure toxicity, any route, class 1;

Reproductive toxicity class 1 or 2

Mutagenicity class 1 or 2; Carcinogenicity class 1;

Respiratory sensitization

Acute toxicity (lethality), dermal only, class 1, 2, 3 or 4;

Acute toxicity (systemic), dermal only, class 1 or 2;

Corrosivity, subclass 1A, 1B or 1C; Skin irritation class 2;

Eye irritation class 1 or 2;

Skin sensitization;

Repeated exposure toxicity, dermal only, class 1 or 2

MIHS

MIHS

 Hazard Bands are screening level hazard groups, often based on limited data.

 One of the critical limitations to the use of

Hazard Banding has been the lack of standardization of hazard phrases in MSDSs and the lack of expertise to translate those phrases into hazard groups by nontoxicologists.

MIHS

 Since Hazard Banding is a preliminary attempt to categorize the relative hazards of the substance to assist OEHS personnel to assign the right controls such as ventilation and PPE, lack of the ability to categorize the hazards can seem insurmountable.

MIHS

 But, where this data exists, it is helpful to compare the relative hazard risk to other more well characterized substances.

 Another concern is when a substance is a solid particle or aerosol, the same dilemma exists as often exists for setting an OEL since there is rarely sufficient inhalation toxicology data for these substances.

MIHS

Most Extensive Data Requirements

( human epidemiology studies)

> quality

> certainty

Moderate Data

Requirements

(human data & insight )

> quality

> certainty

Traditional OELs

• Regulatory, Authoritative

• Health-based

(TLVs, MAKs, WEELs, PELs, MACs,

RELs)

Working Provisional OELs

(internal company, trade association, vendor limits)

Hierarchy of OELs

As more toxicological and epidemiological data becomes available, we move up the hierarchy of OELs.

multiple animal studies

Prescriptive Process Based OELs

(REACH DNELs/DMELs)

Hazard Banding Strategies = Occupational Exposure Bands (OEBs)

• Biosafety Levels (1,2,3,4)

Least Data

Requirements

• Pharmaceutical Banding

• WEEL-Banding Matrix

( in vitro , SAR ( in silico ) & few EPA SNUR New Chemical Exposure Limits Potential animal studies)

Health Hazard

(NCEL)

----------------------------------------------------------

Hierarchy of

OELs / Banding

Strategies

Traditional OEL

Working OEL

DNEL / DMEL

(Prescriptive)

Hazard Banding

“Most Effective”

Hierarchy of

Exposure

Controls

Elimination of

Hazards

Engineering

Controls

Administrative

Controls

PPE

Least Effective

Hierarchy of

Exposure

Assessment

Validated Monitoring

Monitoring

Modeling

Qualitative

Susan Ripple, MS, CIH

Manager

Industrial Hygiene Expertise Center

The Dow Chemical Co.

Midland, MI sdripple@dow.com

MIHS

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