DIETHANOLAMINE

This compound may be used in manufacturing surface active agents used in textile specialties, herbicides, and petroleum demulsifiers (Budavari, 1996). Diethanolamine may also be used in liquid detergents for emulsion paints, cutting oils, shampoos, cosmetics, cleaners, and polishes; in textile and dye specialties; in organic syntheses; as an absorbent for acid gases; as a chemical intermediate for resins, plasticizers, and fatty alkanolamides for liquid detergents; for solubilizing 2,4-dichlorophenoxyacetic acid (2,4-D); as a humectant and softening agent; as an emulsifier intermediate for detergents; as an intermediate for rubber chemicals; as a corrosion inhibitor; and as a dispersing agent (Budavari, 1996) Hathaway, et al, 1996; (HSDB , 1998; Lewis, 1993; Sittig, 1991). This compound can also be used with cracking gases and coal or oil gases containing carbonyl sulfide that could react with monoethanolamine (Budavari, 1996).

SOURCES

Diethanolamine is derived through ammonolysis of ethylene oxide (Budavari, 1996; Lewis, 1993).
Diethanolamine forms ethanolamine soaps through a reaction with long-chain fatty acids (Hathaway et al, 1996).
When diethanolamine is dehydrated, it produces morpholine (HSDB , 1998).

-CLINICAL EFFECTS

GENERAL CLINICAL EFFECTS

Diethanolamine is irritating to the eyes, skin, and mucous membranes. In experimental animals, exposure has resulted in CNS depression, demyelination of the brain and spinal cord, a poorly regenerative anemia, renal tubular degeneration, hepatocellular cytological alterations and necrosis, fatty degeneration of the liver, cardiac myocyte degeneration, and alopecia. Inflammation, ulceration, hyperkeratosis, and acanthosis have occurred following topical application of diethanolamine.

A case of diethanolamine-induced asthma has been reported in a worker handling cutting fluid containing diethanolamine. Rare cases of allergic contact dermatitis may occur.

POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death.
Contact with molten substance may cause severe burns to skin and eyes.
Avoid any skin contact.
Effects of contact or inhalation may be delayed.
Fire may produce irritating, corrosive and/or toxic gases.
Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.

-MEDICAL TREATMENT

LIFE SUPPORT

Support respiratory and cardiovascular function.

SUMMARY

FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Move victim to fresh air.
Call 911 or emergency medical service.
Give artificial respiration if victim is not breathing.
Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device.
Administer oxygen if breathing is difficult.
Remove and isolate contaminated clothing and shoes.
In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes.
For minor skin contact, avoid spreading material on unaffected skin.
Keep victim warm and quiet.
Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed.
Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.

FIRST AID

FIRST AID

EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical.
DERMAL EXPOSURE - Immediately flush the contaminated skin with water. If this chemical penetrates the clothing, immediately remove the clothing and flush the skin with water. Get medical attention promptly.
INHALATION EXPOSURE - Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible.
ORAL EXPOSURE - If this chemical has been swallowed, get medical attention immediately.
TARGET ORGANS - Eyes, skin, and respiratory system (National Institute for Occupational Safety and Health, 2007).

GENERAL -

Move victims of inhalation exposure from the toxic environment and administer 100% humidified supplemental oxygen with assisted ventilation as required. Exposed skin and eyes should be copiously flushed with water. Because of the potential for rapid onset of CNS depression or seizures with possible aspiration of gastric contents, EMESIS SHOULD NOT BE INDUCED. Cautious gastric lavage followed by administration of activated charcoal may be of benefit if the patient is seen soon after the exposure.

INHALATION EXPOSURE -

INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm.
If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents.

DERMAL EXPOSURE -

DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999).
Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.

EYE EXPOSURE -

DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.

ORAL EXPOSURE -

Because of the potential for gastrointestinal tract irritation or CNS depression, DO NOT induce emesis.
Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation.
PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION

Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002).

In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis.
The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).

ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old.
Observe patients with ingestion carefully for the possible development of esophageal or gastrointestinal tract irritation or burns. If signs or symptoms of esophageal irritation or burns are present, consider endoscopy to determine the extent of injury.

-RANGE OF TOXICITY

MINIMUM LETHAL EXPOSURE

GENERAL

In humans, diethanolamine has an estimated fatal dose of 20 grams (HSDB , 1998).

MAXIMUM TOLERATED EXPOSURE

GENERAL

The maximum tolerated human exposure to this agent has not been delineated.

Carcinogenicity Ratings for CAS111-42-2 :

ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Diethanolamine

A3 :Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.

EPA (U.S. Environmental Protection Agency, 2011): Not Listed
IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): 3 ; Listed as: Diethanolamine

3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.

NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Diethanolamine
MAK (DFG, 2002): Category 3A ; Listed as: Diethanolamine

Category 3A : Substances for which the criteria for classification in Category 4 or 5 are fulfilled but for which the database is insufficient for the establishment of a MAK value.

NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

TOXICITY AND RISK ASSESSMENT VALUES

EPA IRIS

EPA Risk Assessment Values for CAS111-42-2 (U.S. Environmental Protection Agency, 2011):

Not Listed

TOXICITY VALUES

References: ACGIH, 1996(a); Budavari, 1996; CHRIS, 1998; Clayton & Clayton, 1994; Hathaway, et al, 1996; Lewis, 1996; HSDB, 1998; OHM/TADS, 1998; RTECS, 1998
- LD50- (ORAL)GUINEA_PIG:
- LD50- (SKIN)GUINEA_PIG:
- LD50- (INTRAPERITONEAL)MOUSE:
- LD50- (ORAL)MOUSE:
- LD50- (SUBCUTANEOUS)MOUSE:
- LD50- (ORAL)RABBIT:
- LD50- (SKIN)RABBIT:
- LD50- (INTRAMUSCULAR)RAT:
- LD50- (INTRAPERITONEAL)RAT:
- LD50- (INTRAVENOUS)RAT:
- LD50- (ORAL)RAT:
- LD50- (SUBCUTANEOUS)RAT:

CALCULATIONS

AMBIENT CONVERSIONS

1 ppm = 4.30 mg/m(3) (at 68 degrees F and 760 mmHg) (NIOSH , 1998)
1 ppm = 4.29 mg/m(3) (at 25 degrees C) (ACGIH, 1996(a))
1 mg/m(3) = 0.23 ppm (at 25 degrees C) (ACGIH, 1996(a))

-STANDARDS AND LABELS

WORKPLACE STANDARDS

ACGIH TLV Values for CAS111-42-2 (American Conference of Governmental Industrial Hygienists, 2010):

Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.

Adopted Value

Diethanolamine

TLV:

TLV-TWA: 1 mg/m(3)
TLV-STEL:
TLV-Ceiling:

Notations and Endnotes:

Carcinogenicity Category: A3
Codes: IFV, Skin
Definitions:

A3: Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.
IFV: Inhalable fraction and vapor.
Skin: This refers to the potential significant contribution to the overall exposure by the cutaneous route, including mucous membranes and the eyes, either by contact with vapors or, of likely greater significance, by direct skin contact with the substance. It should be noted that although some materials are capable of causing irritation, dermatitis, and sensitization in workers, these properties are not considered relevant when assigning a skin notation. Rather, data from acute dermal studies and repeated dose dermal studies in animals or humans, along with the ability of the chemical to be absorbed, are integrated in the decision-making toward assignment of the skin designation. Use of the skin designation provides an alert that air sampling would not be sufficient by itself in quantifying exposure from the substance and that measures to prevent significant cutaneous absorption may be warranted. Please see "Definitions and Notations" (in TLV booklet) for full definition.

TLV Basis - Critical Effect(s): Liver and kidney dam
Molecular Weight: 105.14

For gases and vapors, to convert the TLV from ppm to mg/m(3):

[(TLV in ppm)(gram molecular weight of substance)]/24.45

For gases and vapors, to convert the TLV from mg/m(3) to ppm:

[(TLV in mg/m(3))(24.45)]/gram molecular weight of substance

AIHA WEEL Values for CAS111-42-2 (AIHA, 2006):

Not Listed

NIOSH REL and IDLH Values for CAS111-42-2 (National Institute for Occupational Safety and Health, 2007):

Listed as: Diethanolamine
REL:

TWA: 3 ppm (15 mg/m(3))
STEL:
Ceiling:
Carcinogen Listing: (Not Listed) Not Listed
Skin Designation: Not Listed
Note(s):

IDLH: Not Listed

OSHA PEL Values for CAS111-42-2 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):

Not Listed

OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS111-42-2 (U.S. Occupational Safety and Health Administration, 2010):

Not Listed

ENVIRONMENTAL STANDARDS

EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS111-42-2 (U.S. Environmental Protection Agency, 2010):

Listed as: Diethanolamine
Final Reportable Quantity, in pounds (kilograms):

100 (45.4)

Additional Information:

EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS111-42-2 (U.S. Environmental Protection Agency, 2010):

Not Listed

EPA RCRA Hazardous Waste Number for CAS111-42-2 (U.S. Environmental Protection Agency, 2010b):

Not Listed
Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.

EPA SARA Title III, Extremely Hazardous Substance List for CAS111-42-2 (U.S. Environmental Protection Agency, 2010):

Not Listed

EPA SARA Title III, Community Right-to-Know for CAS111-42-2 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):

Listed as: Diethanolamine
Effective Date for Reporting Under 40 CFR 372.30: 1/1/87
Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:

DOT List of Marine Pollutants for CAS111-42-2 (49 CFR 172.101 - App. B, 2005):

Not Listed

EPA TSCA Inventory for CAS111-42-2 (EPA, 2005):

Listed as: Ethanol, 2,2'-iminobis-

SHIPPING REGULATIONS

SURFACE

DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2491 (49 CFR 172.101, 2005):

Hazardous materials descriptions and proper shipping name: Ethanolamine or Ethanolamine solutions

Symbol(s): Not Listed
Hazard class or Division: 8

8: Corrosive material. See 49 CFR section 173.136 for definitions.

Identification Number: UN2491
Packing Group: III

III: Packing Group III - indicates the degree of danger presented by the material is minor.

Label(s) required (if not excepted): 8

8: Corrosive.

Special Provisions: IB3, T4, TP1

IB3: Authorized IBCs: Metal (31A, 31B and 31N); Rigid plastics (31H1 and 31H2); Composite (31HZ1 and 31HA2, 31HB2, 31HN2, 31HD2 and 31HH2). Additional Requirement: Only liquids with a vapor pressure less than or equal to 110 kPa at 50 °C (1.1 bar at 122 °F), or 130 kPa at 55 °C (1.3 bar at 131 °F) are authorized, except for UN2672 (also see Special Provision IP8 in Table 3 for UN2672).
T4: Minimum test pressure (bar): 2.65; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): sxn.178.274(d)(2); Pressure-relief requirements (See sxn.178.275(g)): Normal; Bottom opening requirements (See sxn.178.275(d)): sxn.178.275(d)(3).
TP1: The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 97/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, and tf is the temperature in degrees celsius of the liquid during filling.

Packaging Authorizations (refer to 49 CFR 173.***):

Exceptions: 154
Non-bulk packaging: 203
Bulk packaging: 241

Quantity Limitations:

Passenger aircraft or railcar: 5 L
Cargo aircraft only: 60 L

Vessel Stowage Requirements:

Vessel stowage location: A

A: The material may be stowed "on deck" or "under deck" on a cargo vessel and on a passenger vessel.

Vessel stowage other: Not Listed

ICAO International Shipping Name for UN2491 (ICAO, 2002):

Proper Shipping Name: Ethanolamine
UN Number: 2491
Proper Shipping Name: Ethanolamine solution
UN Number: 2491

LABELS

NFPA

NFPA Hazard Ratings for CAS111-42-2 (NFPA, 2002):

Listed as: Diethanolamine
Hazard Ratings:

Health Rating (Blue): 3

(3) Seriously toxic material. Short term exposure could cause serious temporary or residual injury even though prompt medical treatment is given. Includes known or suspect small animal carcinogens, mutagens, or teratogens.

Flammability Rating (Red): 1

(1) Slightly combustible. Materials that require considerable preheating before ignition can occur. This rating includes most ordinary combustible materials.

Instability Rating (Yellow): 0

(0) Materials which are normally stable, even under fire conditions, and which are not reactive with water.

Oxidizer/Water-Reactive Designation: Not Listed

-HANDLING AND STORAGE

STORAGE

CONTAINER

Diethanolamine is solid at ambient temperature, but can be kept in liquid form at elevated temperatures or as an aqueous solution (OHM/TADS , 1998). Ethanolamines should be stored separate from strong oxidizers (such as chlorine and bromine) and strong acids, (such as hydrochloric, sulfuric, and nitric acids), because violent reactions may occur. These compounds should be stored in tightly closed containers in a cool, well-ventilated area away from heat. Keep sources of ignition such as smoking and open flames away from these compounds (Sittig, 1991).
Typical shipping containers include tank cars, trucks, compartment cars, drums, cans, and bottles (OHM/TADS , 1998).

-PERSONAL PROTECTION

SUMMARY

RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Wear positive pressure self-contained breathing apparatus (SCBA).
Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection.
Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.

Persons should avoid breathing vapors and wear appropriate chemical protective clothing to prevent contact with diethanolamine. Contaminated clothing and shoes should be removed and isolated before leaving the site (AAR, 1996). Workers should immediately wash any affected areas as soon as contamination occurs. Eyewash fountains and facilities for quickly drenching the body should be provided in areas where there is any possibility of exposure to this compound (NIOSH , 1998).

RESPIRATORY PROTECTION

Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.

PROTECTIVE CLOTHING

CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 111-42-2.

All data are compiled from published sources and are NOT recommended specifically by Truven Health Analytics. The appearance of specific manufacturers or products in this section does not represent an endorsement by Truven Health Analytics. No attempt has been made to verify the data presented. All product recommendations should be confirmed with the specific manufacturer for verification of product performance.
CLOTHING

Neoprene

LaCrosse-Rainfair Safety Products

Chem Tech II splash suits

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

National Safety Wear

Nation splash suit

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natprene splash suit

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Nattuf splash suit

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Neosafe II splash suit

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Neosafe I splash suit

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Neosafe V

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Neosafe VI

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

River City

Neoprene splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (River City, 1995)

Tingley Rubber Corporation

Premier, Magnaprene

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Neoprene+PVC

National Safety Wear

Natchem Splash Suits

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Nitrile

LaCrosse-Rainfair Safety Products

Super nitrile splash suits

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Paracril+PVC

National Safety Wear

Natweb splash suits

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natwork splash suits

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Plastic Laminate

DuPont Personal Protection

CPF 3

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): <0.1
Notes: Not Listed
Citation: (DuPont, 2002)

Responder

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (DuPont, 2002)

Responder Plus

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (DuPont, 2002)

Polyurethane

LaCrosse-Rainfair Safety Products

Cool air splash suits

Degradation Rating: Fair
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

National Safety Wear

Natflex splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natsoft splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Tingley Rubber Corporation

Iron Eagle, Eagle

Degradation Rating: Not Recommended
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Polyvinyl Chloride

LaCrosse-Rainfair Safety Products

8000 Series splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Acid Suit splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Chem King splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Chem Tech I splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Flame Tech splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Job King splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Warm Ã"N Dry splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

National Safety Wear

Natcide splash suit

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natcon splash suit

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natlite II splash suit

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natlite I splash suit

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

Natpro splash suit

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Nat-Wear, 2001)

River City

PVC splash suits

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (River City, 1995)

Tingley Rubber Corporation

American, Scrim, DuraScrim, PVC Polyester, Double-Ply PVC, PVC Film

Degradation Rating: Not Recommended
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Webdri, Safetyflex, Electra, ElectraBrite

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Styrene-butadiene Rubber (SBR)

LaCrosse-Rainfair Safety Products

Vultex splash suits

Degradation Rating: Fair
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

FOOTWEAR

Natural Rubber

Tingley Rubber Corporation

Molded Overshoes, Hand-Made Footwear

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Neoprene

LaCrosse-Rainfair Safety Products

Not specified

Degradation Rating: Not Recommended
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

North -- Safety 4H

Neoprene series - specific style not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (North, 2002)

Servus (Norcross Safety Products)

Neoprene III

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Servus, 1995)

Tingley Rubber Corporation

Molded Overshoes, Hand-Made Footwear

Degradation Rating: Good
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Nitrile+PVC

Onguard Industries

Heartland

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Polyurethane

LaCrosse-Rainfair Safety Products

Purolite

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Polyurethane+PVC

LaCrosse-Rainfair Safety Products

Not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Onguard Industries

Polyblend

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Superpoly

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Polyurethane Blend

LaCrosse-Rainfair Safety Products

Not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Polyvinyl Chloride

LaCrosse-Rainfair Safety Products

Not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

North -- Safety 4H

PVC Series - specific style not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (North, 2002)

Servus (Norcross Safety Products)

Supreme

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Servus, 1995)

Tingley Rubber Corporation

Two Stage Injection Molded, Better Grade, General Purpose, Workbrutes

Degradation Rating: Poor
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Two Stage Injection Molded, Premier

Degradation Rating: Fair
Breakthrough Time (minutes): Not reported
Permeation Rate (mcg/cm2/min): Not reported
Notes: Not Listed
Citation: (Tingley, 2002)

Rubber

North -- Safety 4H

Rubber Series - specific style not specified

Degradation Rating: Fair
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (North, 2002)

Rubber blend

LaCrosse-Rainfair Safety Products

Not specified

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (LaCrosse-Rainfair, 1997)

Onguard Industries

Bluemax

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Polymax

Degradation Rating: Good
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Standard

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Bata Shoe Company, 1995)

Servus (Norcross Safety Products)

Not specified

Degradation Rating: Fair
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Servus, 1995)

GLOVES

Butyl

Best Manufacturing

Butyl 878

Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None Detected
Notes: Tested with Limited Exposure Method (ASTM F 1383)
Citation: (Best Manufacturing, 2004)
Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (Best Manufacturing, 2004)

North Safety Products

Butyl Series

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (North, 2002)

Latex

Memphis Glove Company

5290 Series Flock-Lined Latex

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): Not tested
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

Natural Rubber

Best Manufacturing

Original Nitty Gritty

Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (Best Manufacturing, 2004)
Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None Detected
Notes: Tested under limited exposure method (ASTM F 1383)
Citation: (Best Manufacturing, 2004)

Neoprene

Best Manufacturing

Chloroflex 723

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)

Neoprene 6780 Series

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)

Ultraflex Neoprene 32

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)

MAPA Spontex, Inc.

Chem-ply/N-440

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: 99%
Citation: (MAPA Professional, 2004)

Memphis Glove Company

5410S Series Flock-Lined Neoprene

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): Not tested
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

6912 Neomax Neoprene

Degradation Rating: 6 (on a scale of 0 to 6, with 0 offering the least chemical resistance)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

Wells Lamont Industrial

Not specified

Degradation Rating: Excellent
Breakthrough Time (minutes): No Breakthrough Time provided
Permeation Rate (mcg/cm2/min): No Permeation Rate provided
Notes: Not Listed
Citation: (Wells Lamont Industrial, 2002)

Neoprene+NatR

Best Manufacturing

Chem Master CHM

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)

Playtex

123 Argus

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): <0.1
Notes: Not Listed
Citation: (Playtex, 1995)

Industrial CR Glove #827

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Playtex, 1995)

Industrial Glove #834

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Playtex, 1995)

Industrial HD Glove #103

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Playtex, 1995)

Utility Glove #835

Degradation Rating: Excellent
Breakthrough Time (minutes): Not Listed
Permeation Rate (mcg/cm2/min): Not Listed
Notes: Not Listed
Citation: (Playtex, 1995)

Nitrile

Best Manufacturing

N-DEX 7005

Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): None Detected
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (Best Manufacturing, 2004)

N-DEX 8005

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)

Nitri-Solve 727

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)

Ultimate N-Dex 9905

Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (Best Manufacturing, 2004)
Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None Detected
Notes: Tested with Limited Exposure Method (ASTM F 1383)
Citation: (Best Manufacturing, 2004)

Ultraflex Nitrile 22R

Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (Best Manufacturing, 2004)
Degradation Rating: Excellent (after 60 minutes of testing)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None Detected
Notes: Tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2004)

MAPA Spontex, Inc.

Stansolv/A-14

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: 97%; non-normalized breakthrough
Citation: (MAPA Professional, 2004)

Memphis Glove Company

5320 Series Flock-Lined Nitrile

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): Not tested
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

9750 Series Predator Nitrile

Degradation Rating: 6 (on a scale of 0 to 6, with 0 offering the least chemical resistance)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

Wells Lamont Industrial

Not specified

Degradation Rating: Excellent
Breakthrough Time (minutes): No Breakthrough Time provided
Permeation Rate (mcg/cm2/min): No Permeation Rate provided
Notes: Not Listed
Citation: (Wells Lamont Industrial, 2002)

Nitrile+PVC

Best Manufacturing

Hustler 725R

Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None detected
Notes: tested through limited exposure method (ATSM F 1383)
Citation: (Best Manufacturing, 2002)
Degradation Rating: Excellent (after 60 minutes)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None detected
Notes: Not Listed
Citation: (Best Manufacturing, 2002)

Plastic Laminate

North -- Safety 4H

Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): Not reported
Notes: tested at 21 degrees C; 70 degrees F
Citation: (Safety 4, 2002)
Degradation Rating: No Degradation Rating provided
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): Not reported
Notes: tested at 35 degrees C; 95 degrees F
Citation: (Safety 4, 2002)

Polyvinyl Chloride

Memphis Glove Company

6400 Actifresh Green PVC

Degradation Rating: 6 (on a scale of 0 to 6, with 0 offering the least chemical resistance)
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): Not Reported
Notes: Not Listed
Citation: (Memphis Glove Company, 2001)

Wells Lamont Industrial

Not specified

Degradation Rating: Excellent
Breakthrough Time (minutes): No Breakthrough Time provided
Permeation Rate (mcg/cm2/min): No Permeation Rate provided
Notes: Not Listed
Citation: (Wells Lamont Industrial, 2002)

Vinyl

MAPA Spontex, Inc.

Pylox/V-20

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: 97%; non-normalized breakthrough
Citation: (MAPA Professional, 2004)

Viton

North Safety Products

Viton Series

Degradation Rating: Excellent
Breakthrough Time (minutes): >480
Permeation Rate (mcg/cm2/min): None Detected
Notes: Not Listed
Citation: (North, 2002)

Viton over Butyl

Best Manufacturing

Viton #890

Degradation Rating: Not Tested
Breakthrough Time (minutes): 142
Permeation Rate (mcg/cm2/min): 49
Notes: Not Listed
Citation: (Best Manufacturing, 2004)
Degradation Rating: Not Tested
Breakthrough Time (minutes): >240
Permeation Rate (mcg/cm2/min): None Detected
Notes: Tested with limited exposure method (ASTM F 1383)
Citation: (Best Manufacturing, 2004)

GENERAL INFORMATION

This section provides a compilation of chemical resistance information and test data for specific protective clothing products. Chemical resistance information includes both degradation resistance ratings and permeation resistance data. This information is designed to assist in the selection of appropriate protective clothing. Only data on specific products and manufacturers are included. Generic information or recommendations are not provided since significant differences can exist in the chemical resistance for apparent similar product types.
Specific product information is organized by general product type (gloves, garments, and footwear), material type, and manufacturer. The category 'garments' may include totally encapsulating suits, splash suits, as well as other items (e.g., coveralls, jackets, and aprons). Specific manufacturers should be contacted to determine the features of available styles/models.
In addition to chemical resistance information, there are many critical variables in the selection of protective clothing which cannot be represented in this summary of the literature. Some factors to be considered in choosing protective clothing include, but are not limited to: overall clothing integrity, physical hazard resistance, durability, human factors, ease of decontamination, and cost. Overall clothing integrity refers to a specific design's ability to offer consistent protection for all clothing-covered areas of the body. Physical hazards include resisting the effects of abrasion, cuts, tears, and punctures. Human factors entail effects on wearer mobility, visibility, and hearing for garments; dexterity, tactility, and grip for gloves; ankle support and weight for footwear; and, any effect of the clothing on the function of the wearer. There are several variations in the design for gloves, garments, and footwear that affect these factors. Protective clothing must properly be sized and correctly fit the wearer to ensure its proper use and function.
As required in the U.S.A., protective clothing should be selected based on a risk assessment of the workplace. This risk assessment must account for the identification of existing as well as potential hazards and involve the recommendation of protective clothing appropriate for the identified hazards. Therefore, the recommendations in this section should not be used as the sole basis for decisions on choice of protective clothing, but rather should be used as a tool by qualified occupational health and safety professionals or other technically qualified persons in conjunction with a review of all mitigating factors. Consult the OSHA PPE Standard (29 CFR 1910.132 - 1910.138) for regulations and additional guidance regarding the selection and use of protective clothing and equipment. For general information on protective clothing selection, refer to the "PERSONAL PROTECTIVE EQUIPMENT - OSHA PUB 3077" document.
PROTECTIVE CLOTHING SELECTION

Determine the type of protective clothing item needed based on a risk assessment (e.g., gloves, garments, footwear).
For high risk situations, choose clothing that covers all parts of the body that may be exposed. In many cases, multiple clothing items will be required. Low risk situations may permit partial body protective clothing. Select protective clothing products that have reported chemical resistance data. High risk situations involving full body clothing or extended chemical contact often require permeation resistance data to determine the barrier effectiveness of materials used in the construction of clothing. Relatively low risk situations, where only splash or incidental exposure occur, may allow use of protective clothing based on degradation or penetration resistance data. Specifics on the interpretation of chemical resistance data are presented below.
Other factors must be considered in addition to chemical resistance. The selected chemical protective clothing item should offer the optimal combination of protection against identified hazards while allowing maximum function and comfort.

INTERPRETATION OF DEGRADATION RATINGS

Degradation refers to physical changes in a material as the result of chemical exposure. Degradation may become evident in visible changes, such as discoloration, swelling, delamination, deterioration, or disintegration. Degradation effects may also be measured by weight change or other changes in a material's physical properties (e.g., strength, elasticity, hardness).
Degradation resistance ratings are provided by manufacturers to rate the amount of degradation that occurs for a particular protective clothing material when contacted by a chemical. All degradation ratings are qualitative and include ratings, such as "EXCELLENT," "GOOD," "FAIR," "POOR," and "NOT RECOMMENDED." There is no standard test method for the measurement of chemical degradation resistance; therefore, manufacturer ratings may be based on different testing approaches. This makes comparison of degradation ratings between manufacturers unreliable.
The use of degradation resistance ratings alone to recommend protective clothing, particularly for high hazard situations, should be avoided. Degradation resistance testing does not directly assess the barrier quality of protective clothing, since materials can show relatively little degradation but still allow either permeation or penetration by a chemical. Degradation resistance ratings can be used to exclude protective clothing materials from consideration. Protective clothing materials with a "NOT RECOMMENDED" degradation resistance rating should never be used.
For some products, the rating "NO PENETRATION" is provided. This refers to penetration resistance test results that are based on a different procedure (American Society for Testing and Materials (ASTM) Standard Test Method F 903). Penetration resistance testing involves placing a material sample in a test cell, exposing the exterior side of the material to a chemical, and then observing the interior side of the material for visible signs of liquid penetration. Part of the test is conducted at an elevated pressure. Test results are reported as pass (no penetration) or fail (penetration detected). Unlike degradation testing, penetration testing provides an assessment of protective clothing material barrier performance. Since penetration resistance testing examines only observable amounts of liquid penetration, permeation may still occur. The use of penetration resistance data must be restricted to liquid chemicals, and should be limited to scenarios where there is no reasonable vapor exposure hazard under the conditions of exposure.

INTERPRETATION OF PERMEATION DATA

Permeation is the process of chemical movement through a material on a molecular level. Permeation resistance refers to the ability of a material to retard or prevent chemical movement through it. Permeation may occur without any visible signs of degradation.
Permeation resistance is measured using a test cell which is divided into two halves by a protective clothing specimen. Chemical is placed on the challenge side, while the collection side is periodically monitored for permeating chemical. Permeation data were obtained in accordance with the American Society for Testing and Materials (ASTM) Standard Test Method F 739 (Resistance of Materials Used in Protective Clothing to Permeation by Liquids and Gases), unless stated otherwise. In the case of chemicals that are classified as warfare agents, the data were obtained in accordance with the Military Standard 282 (MIL-STD-282) (Military Standard, Filter Units, Protective Clothing, Gas-Mask Components, and Related Products: Performance Test Methods).
Permeation rate is the amount of chemical that passes through a material for a measured surface area per unit time. In this section, permeation rate is expressed in micrograms per square centimeter per minute (mcg/cm(2)/min). The reported permeation rate is either the steady-state rate or the maximum rate observed during testing. In some cases, very large permeation rates exceed measurement techniques and are reported as ">" (greater than) or "HIGH."
Breakthrough time is the elapsed time, in minutes, from the time the chemical comes in contact with the material exterior surface, to the time that chemical is detected on the interior surface. When no breakthrough is detected, the breakthrough time is report as ">" the testing period. If permeation breakthrough is rapid, results are reported as "<" (less than) the earlier sampling time or as "IMMEDIATELY" (which usually means breakthrough in less than 4 minutes).
The breakthrough time should exceed the expected use period of the selected protective clothing. Additionally, there are several other factors that must be taken into account to provide appropriate protection.
Permeation testing is usually conducted with full strength, undiluted chemical for the duration of the test period. Actual exposures may involve diluted chemical for short or intermittent exposure periods.
Permeation testing is usually conducted at room temperature. Permeation occurs faster at elevated temperatures (short breakthrough times and higher permeation rates) and slower at reduced temperatures (long breakthrough times and lower permeation rates).
Permeation resistance of mixtures cannot usually be determined on the basis of the individual chemicals making up the mixture. Synergistic effects may occur and result in more rapid permeation than accounted for by the individual mixture chemicals.
Permeation rates may be used to calculate potential wearer exposure; however, several assumptions must be made about the extent of exposure and condition of clothing wear. Furthermore, there are few chemicals with dermal exposure limits, making it difficult to determine an acceptable skin exposure level.

COMPANY INFORMATION

Best Manufacturing 579 Edison Street Menlo, GA 30731 USA Phone: (706) 862-2302 Fax: (706) 862-6000 Toll-Free: (800) 241-0323 Website: http://www.bestglove.com Email: USA@bestglove.com
DuPont Personal Protection P. O. Box 80705 Wilmington, DE 19880-0705 USA Phone: (302) 774-1000 Toll-Free: (800) 931-3456 Website: http://personalprotection.dupont.com Email: personalprotection@usa.dupont.com
LaCrosse-Rainfair Safety Products 18550 NE Riverside Parkway Portland, OR 97230 USA Phone: (800) 557-7246 Fax: (800) 558-0188 Toll-Free: (800) 557-7246 Website: http://www.lacrosserainfair.com Email: info@lacrossesafety.com
MAPA Spontex, Inc. 100 Spontex Dr. Columbia, TN 38401 USA Phone: (800) 537--2897 Fax: (800) 537--3299 Website: http://www.mapaglove.com Email: sales@mapaglove.com
Memphis Glove Company 5321 East Shelby Dr. Memphis, TN 38188 USA Phone: (901) 795-0672 Fax: (901) 794-7622 Toll-Free: (800) 955-6887 Website: http://www.memphisglove.com
National Safety Wear 9 High Street Miora, NY 12957 USA Phone: (800) 833-7270 Fax: (518) 529-7401 Toll-Free: (800) 833-7270 Website: http://www.natwear.com Email: sales@natwear.com
North -- Safety 4H 2000 Plainfield Pike Cranston, RI 02921 USA Phone: (800) 430-4110 Fax: (800) 572-6346 Toll-Free: (800) 430-4110 Website: http://www.safety4.com
North Safety Products 2000 Plainfield Pike Cranston, RI 02921 USA Phone: (800) 430-4110 Fax: (800) 572-6346 Toll-Free: (800) 430-4110 Website: http://www.northsafety.com Email: marketing@northsafety.com
Onguard Industries 1850 Clark Road Havre de Grace, MD 21078 USA Phone: (410) 272-2000 Fax: (800) 304-2282 Toll-Free: (800) 365-2282 Website: http://www.onguardindustries.com Email: support@onguardindustries.com
Playtex 300 Nyala Farms Road Westport, CT 06880 USA
River City 5321 East Shelby Dr. Memphis, TN 38188 USA Phone: (800) 888-0347 Fax: (901) 795-3815 Toll-Free: (800) 888-0347 Website: http://www.protectivewear.com Email: support@protectivewear.com
Servus (Norcross Safety Products) 1136 Second St Rock Island, IL 61202 USA Phone: (800) 777-9021 Fax: (800) 267-6809 Toll-Free: (800) 777-9021 Website: http://www.servusproducts.com Email: info@nspusa.com
Tingley Rubber Corporation One Cragwood Road PO Box 100 South Plainfield, NJ 07080 USA Phone: (800) 631-5498 Fax: (866) 757-9239 Toll-Free: (800) 631-5498 Website: http://www.tingleyrubber.com
Wells Lamont Industrial 6640 W. Touhy Ave. Niles, IL 60714 USA Fax: (847) 647-6943 Toll-Free: (800) 247-3295 Website: http://www.wellslamontindustry.com Email: kmeger@wellslamont.com

REFERENCES

CHEMICAL PROTECTIVE CLOTHING CITATIONS

The following sources were consulted for chemical protective clothing data:

(Ansell-Edmont, 2001)
(Bata Shoe Company, 1995)
(Best Manufacturing, 2002)
(Best Manufacturing, 2004)
(Boss Manufacturing Company, 1998)
(ChemFab Corporation, 1993)
(Comasec Safety, Inc., 2003)
(Comasec Safety, Inc., 2003a)
(DuPont, 2002)
(DuPont, 2002)
(DuPont, 2003)
(Guardian Manufacturing Group, 2001)
(ILC Dover, Inc., 1998)
(Kappler Inc., 2001)
(Kimberly-Clark, 2002)
(LaCrosse-Rainfair, 1997)
(MAPA Professional, 2003)
(MAPA Professional, 2004)
(Mar-Mac Manufacturing, Inc, 1995)
(Marigold Industrial, 2003)
(Memphis Glove Company, 2001)
(Montgomery Safety Products, 1995)
(Nat-Wear, 2001)
(Neese Industries, Inc., 2003)
(North, 2002)
(North, 2002)
(Playtex, 1995)
(River City, 1995)
(Safety 4, 2002)
(Servus, 1995)
(Standard Safety Equipment, 1995)
(Tingley, 2002)
(Trelleborg-Viking, Inc., 2001)
(Trelleborg-Viking, Inc., 2002)
(Wells Lamont Industrial, 2002)
(Workrite, 1997)

-PHYSICAL HAZARDS

FIRE HAZARD

SUMMARY

POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- Combustible material: may burn but does not ignite readily.
- When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards.
- Those substances designated with a "P" may polymerize explosively when heated or involved in a fire.
- Contact with metals may evolve flammable hydrogen gas.
- Containers may explode when heated.
- Runoff may pollute waterways.
- Substance may be transported in a molten form.
Diethanolamine is combustible when exposed to heat or flame and can react with oxidizing materials (Lewis, 1996). It does not burn, or burns with difficulty (AAR, 1996). Fires involving this compound may be fought using alcohol foam, water, or carbon dioxide dry chemical (Lewis, 1996).

FLAMMABILITY CLASSIFICATION

NFPA Flammability Rating for CAS111-42-2 (NFPA, 2002):

Listed as: Diethanolamine
Flammability Rating: 1

(1) Slightly combustible. Materials that require considerable preheating before ignition can occur. This rating includes most ordinary combustible materials.

FIRE CONTROL/EXTINGUISHING AGENTS

SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Dry chemical, CO2 or water spray.

LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Dry chemical, CO2, alcohol-resistant foam or water spray.
Move containers from fire area if you can do it without risk.
Dike fire control water for later disposal; do not scatter the material.

TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Fight fire from maximum distance or use unmanned hose holders or monitor nozzles.
Do not get water inside containers.
Cool containers with flooding quantities of water until well after fire is out.
Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank.
ALWAYS stay away from tanks engulfed in fire.

NFPA Extinguishing Methods for CAS111-42-2 (NFPA, 2002):

Listed as: Diethanolamine
Extinguishing Method(s): 5, 2

5: Flammable liquid fires can be extinguished using carbon dioxide, dry chemical, foam, and vaporizing liquid extinguishers, as long as the fires are small to moderate in size and the flammable liquid reservoir is shallow. Use of foam to form a blanket over a flammable liquid is not effective when the liquid is water-soluble. Certain alcohol resistant foams are effective extinguishing agents for polar, non-polar, and water-soluble liquid fires. These foams are preferred for fighting flammable liquid fires except those that involve water reactive flammable liquids.
2: "Water or foam may cause frothing" refers to a situation where materials with a flash point above 212 degrees F (100 degrees C) are burning. Potentially violent frothing can be dangerous to fire fighters near the burning liquid. However, when highly viscous liquids are burning, fire fighters can intentionally cause frothing on the liquid surface to prevent further introduction of oxygen.

This compound does not burn, or burns with difficulty (AAR, 1996). When fighting fires involving diethanolamine, alcohol foam, water, or carbon dioxide dry chemical may be used (Lewis, 1996). Run-off water should be kept out of sewers and water sources (AAR, 1996). Water may be used to cool affected containers, disperse the vapors, and prevent the spread of fires (CHRIS , 1998; ITI, 1995).

OHM/TADS (1998) indicates that alcohol foam should be used because water or foam may cause frothing.

COMBUSTION TOXICITY

When heated to decomposition, diethanolamine emits toxic fumes of oxides of nitrogen (Lewis, 1996).

DUST/VAPOR HAZARD

Diethanolamine, when heated to decomposition, emits toxic fumes of oxides of nitrogen (Lewis, 1996).

REACTIVITY HAZARD

Diethanolamine reacts with oxidizing materials, strong acids, acid anhydrides, and halides (Lewis, 1996; NIOSH , 1998). This compound may also react with nitrite or oxides of nitrogen to form n-nitrosodiethanolamine (ACGIH, 1996(a)).

Diethanolamine reacts with carbon monoxide in the air. It is corrosive to copper, zinc, and galvanized iron (HSDB , 1998).

EVACUATION PROCEDURES

SUMMARY

Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.

SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.

FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.

PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)

CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number:

MEXICO:

SETIQ:

01-800-00-214-00 in the Mexican Republic;
For calls originating in Mexico City and the Metropolitan Area: 5559-1588;
For calls originating elsewhere, call: 011-52-555-559-1588.

CENACOM:

01-800-00-413-00 in the Mexican Republic;
For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885;
For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.

ARGENTINA:

CIQUIME:

0-800-222-2933 in the Republic of Argentina;
For calls originating elsewhere, call: +54-11-4613-1100.

BRAZIL:

PRÓ-QUÍMICA:

0-800-118270 (Toll-free in Brazil);
For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).

COLUMBIA:

CISPROQUIM:

01-800-091-6012 in Colombia;
For calls originating in Bogotá, Colombia, call: 288-6012;
For calls originating elsewhere, call: 011-57-1-288-6012.

CANADA:

CANUTEC:

613-996-6666 (Collect calls are accepted);
*666 cellular (in Canada only).

UNITED STATES:

CHEMTREC®:

1-800-424-9300 (Toll-free in the U.S., Canada, and the U.S. Virgin Islands);
703-527-3887 for calls originating elsewhere (Collect calls are accepted).

CHEM-TEL, INC.:

1-800-255-3924 (Toll-free in the U.S., Canada, and the U.S. Virgin Islands);
813-248-0585 for calls originating elsewhere (Collect calls are accepted).

INFOTRAC:

1-800-535-5053 (Toll-free in the U.S., Canada, and the U.S. Virgin Islands);
352-323-3500 for calls originating elsewhere (Collect calls are accepted).

3E COMPANY:

1-800-451-8346 (Toll-free in the U.S., Canada, and the U.S. Virgin Islands);
760-602-8703 for calls originating elsewhere (Collect calls are accepted).

NATIONAL RESPONSE CENTER (NRC):

1-800-424-8802 - (24 hours) (Toll-free in the U.S., Canada, and the U.S. Virgin Islands);
202-267-2675 for calls in the District of Columbia.

MILITARY SHIPMENTS:

703-697-0218 - Explosives/ammunition incidents (Collect calls are accepted);
1-800-851-8061 - All other dangerous goods incidents.

NATIONWIDE POISON CONTROL CENTER (United States only):

1-800-222-1222 (Toll-free in the U.S.).

For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions.
As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids.
Keep unauthorized personnel away.
Stay upwind.
Keep out of low areas.
Ventilate enclosed areas.

AIHA ERPG Values for CAS111-42-2 (AIHA, 2006):

Not Listed

DOE TEEL Values for CAS111-42-2 (U.S. Department of Energy, Office of Emergency Management, 2010):

Listed as Diethanolamine
TEEL-0 (units = mg/m3): 1
TEEL-1 (units = mg/m3): 25
TEEL-2 (units = mg/m3): 150
TEEL-3 (units = mg/m3): 300
Definitions:

TEEL-0: The threshold concentration below which most people will experience no adverse health effects.
TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure.
TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape.
TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.

AEGL Values for CAS111-42-2 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):

Not Listed

NIOSH IDLH Values for CAS111-42-2 (National Institute for Occupational Safety and Health, 2007):

Not Listed

CONTAINMENT/WASTE TREATMENT OPTIONS

SUMMARY

SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area).
- Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
- Stop leak if you can do it without risk.
- Prevent entry into waterways, sewers, basements or confined areas.
- Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers.
- DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- Wear positive pressure self-contained breathing apparatus (SCBA).
- Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection.
- Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
This compound is a threat to the environment and immediate steps should be taken to limit its spread to the environment. Diethanolamine can penetrate soil and contaminate groundwater and nearby streams. Material should be kept out of water sources and sewers. Dikes may be used to contain flow. Stop leaks, if it can be done without undue personnel hazard (AAR, 1996; (CHRIS , 1998).
If diethanolamine is spilled on land, surface flow may be diked using soil, sand bags, foamed polyurethane, or foamed concrete. Bulk liquid may be absorbed with fly ash, cement powder, or commercial sorbents (AAR, 1996).
If diethanolamine is spilled in water, trapped material may be removed with suction hoses (AAR, 1996).
OHM/TADS (1998) reports that, for alkaline solutions, carbon or peat may be effective in clean-up. Water may be neutralized with dilute acetic acid and treated with cation exchangers.

WASTE TREATMENT OPTIONS

CHEMICAL TREATMENT

One disposal method includes adding the contaminated amine to a layer of sodium bisulfate in a large evaporating dish, spraying with water to neutralize, and routing to a sewage plant (OHM/TADS , 1998).
Waste management activities associated with material disposition are unique to individual situations. Proper waste characterization and decisions regarding waste management should be coordinated with the appropriate local, state, or federal authorities to ensure compliance with all applicable rules and regulations.

PHYSICAL TREATMENT

Diethanolamine may be dissolved in a combustible solvent and burned in an open furnace or may be sprinkled into the fire chamber of a furnace with an afterburner and scrubber (ITI, 1995; OHM/TADS , 1998).

-ENVIRONMENTAL HAZARD MANAGEMENT

POLLUTION HAZARD

Diethanolamine is released to the environment through emissions or effluents from its manufacture and use, from consumer product disposal, and from the application of agricultural chemicals (Howard, 1990). This compound is dangerous to aquatic life in high concentrations and may be dangerous if it enters water intakes (CHRIS , 1998).

ENVIRONMENTAL FATE AND KINETICS

Diethanolamine's vapor pressure indicates that it will primarily exist in the vapor phase in the atmosphere. The primary removal mechanism is reaction with photochemically generated hydroxyl radicals (half-life of 0.72-7.2 hours). Precipitation may also be a significant removal process, due to diethanolamine's complete solubility in water (Howard, 1991; (Howard, 1990).

WATER

SURFACE WATER
- Diethanolamine is expected to biodegrade in water, with half-lives of 14.4-168 hours (surface water) and 28.8-336 hours (groundwater) (Howard, 1991; (Howard, 1990). OHM/TADS (1998) reports that this compound will form a strong alkaline solution in water, due to the dissociation of amine groups and the subsequent formation of ammonium ions. This compound is not expected to bioconcentrate in aquatic organisms, adsorb to suspended solids and sediments, or volatilize (Howard, 1991; (Howard, 1990). The biological oxygen demand of diethanolamine is 10% (theoretical), 5 days (CHRIS , 1998).

SOIL

TERRESTRIAL
- In soil, biodegradation is expected to be rapid, following acclimation (half-life 14.4-168 hours). Some residual amounts of this compound may leach into groundwater. Volatilization is not an important fate process (Howard, 1991; (Howard, 1990). The Koc value of 4 and the complete solubility in water indicate that this compound should be extremely mobile in soil and should not adsorb appreciably to suspended solids or sediments in water (Howard, 1990). However, the protonated form of this compound may adsorb to humic material in unsuspended sediments and solids (HSDB , 1998).

BIOACCUMULATION

BIOCONCENTRATION FACTOR

With a bioconcentration factor of <1, diethanolamine is not expected to bioconcentrate in aquatic organisms (Howard, 1990).

ENVIRONMENTAL TOXICITY

References: (OHM/TADS , 1998)

TLM - FISH: 100 ppm for 24H -- 15-21 degrees C; Aerated
TLM - BLUEGILL: 1850 ppm for 48H -- 15-21 degrees C; Aerated
TLM - SUNFISH: 2100 ppm for 24H -- 20 degrees C; Aerated
TLM - BLUEGILL: 2100 ppm for 24H -- 20 degrees C; Aerated
TLM - MOSQUITO FISH: 1800 for 24H -- Turbid
TLM - MOSQUITO FISH: 1550 for 48H -- Turbid
TLM - MOSQUITO FISH: 1400 ppm for 96H -- Turbid
TLM - BRINE SHRIMP: 2800 ppm for 24H -- Static
CRITICAL - CREEK CHUB: 80-120 ppm for 24H -- 15-21 degrees C; Aerated
LC50 - FATHEAD MINNOW: > 100 ppm for 96H -- Static
LC50 - DAPHNIA MAGNA: 1.4 ppm for 96H -- Static
INHIBITORY - SELENASTRUM CAPRICORNATUM: 100 ppm

-PHYSICAL/CHEMICAL PROPERTIES

MOLECULAR WEIGHT

105.14

DESCRIPTION/PHYSICAL STATE

Diethanolamine exists as a faintly colored to colorless, viscous, hygroscopic liquid (above 82 degrees F) or deliquescent prisms with a mild ammoniacal odor (Ashford, 1994; Budavari, 1996; Lewis, 1996; NIOSH , 1998). CHIRS (1998) reports that this compound has a slight dead fish odor.

11.0 (0.1 normal) (Budavari, 1996)

VAPOR PRESSURE

5 mmHg (at 138 degrees C) (Lewis, 1996)

< 0.01 mmHg (at 20 degrees C) (ACGIH, 1996(a); (NIOSH , 1998)

0.00028 mmHg (at 25 degrees C) (Howard, 1990)

1.4x10(-4) mmHg (at 25 degrees C) (HSDB , 1998)

SPECIFIC GRAVITY

OTHER TEMPERATURE AND/OR PRESSURE

1.0919 (at 30/20 degrees C) (Lewis, 1996)
1.092 (at 30/20 degrees C) (Lewis, 1993)
1.0881 (at 30/4 degrees C) (Budavari, 1996)
1.0693 (at 60/4 degrees C) (Budavari, 1996)
1.09664 (at 20/4 degrees C) (Clayton & Clayton, 1994)

DENSITY

OTHER TEMPERATURE AND/OR PRESSURE

1.09 kg/L (at 30 degrees C) (Ashford, 1994)
1.095 kg/L (at 15.6 degrees C) (ITI, 1995)

TEMPERATURE AND/OR PRESSURE NOT LISTED

1.091 kg/L (OHM/TADS , 1998)

FREEZING/MELTING POINT

FREEZING POINT

28 degrees C; 82 degrees F; 301 degrees K (CHRIS , 1998; NIOSH , 1998)

MELTING POINT

28.0 degrees C; 82 degrees F (Lewis, 1996; NFPA, 1994)
27.8 degrees C (ITI, 1995)

BOILING POINT

270 degrees C (decomposes) (Lewis, 1996)

269 degrees C (Lewis, 1993)

268 degrees C; 514 degrees F (NFPA, 1994)

268.8 degrees C (at 760 mmHg) (Budavari, 1996)

217 degrees C (at 150 mmHg) (Budavari, 1996)

20 degrees C (at 0.01 mmHg) (Budavari, 1996)

> 270 degrees C (Ashford, 1994)

516 degrees F (decomposes) (NIOSH , 1998)

268.4 degrees C; 515.1 degrees F; 541.6 degrees K (CHRIS , 1998)

FLASH POINT

305 degrees F (open cup) (Lewis, 1996)

300 degrees F (Budavari, 1996)

152 degrees C; 306 degrees F (open cup) (Lewis, 1993)

172 degrees C; 342 degrees F (open cup) (NFPA, 1994)

280 degrees F (open cup) (Clayton & Clayton, 1994)

134 degrees C (open cup) (ITI, 1995)

279 degrees F (NIOSH , 1998)

152 degrees (closed cup) (ACGIH, 1996(a))

150 degrees C (OHM/TADS , 1998)

AUTOIGNITION TEMPERATURE

662 degrees C; 1224 degrees F (Lewis, 1996; NFPA, 1994)

EXPLOSIVE LIMITS

LOWER

1.6 % (NIOSH , 1998)

UPPER

9.8 % (NIOSH , 1998)

SOLUBILITY

IN WATER

Diethanolamine is very soluble in water (96.4% w/w) (Clayton & Clayton, 1994; Lewis, 1996).
Miscible with water (Budavari, 1996).

IN ORGANIC SOLVENTS

Diethanolamine is very soluble in alcohol is soluble in methanol and acetone (Budavari, 1996; Lewis, 1993). It is insoluble in ether and benzene and hydrocarbon solvents (Ashford, 1994; Lewis, 1993).
This compound is slightly soluble in ether (0.8% at 25 degrees C) and benzene (4.2% at 25 degrees C) and is hardly soluble in carbon tetrachloride (< 0.1% at 25 degrees C) and heptane (< 0.1% at 25 degrees C) (Budavari, 1996; ITI, 1995; HSDB , 1998).

OCTANOL/WATER PARTITION COEFFICIENT

-1.43 (Howard, 1990)

HENRY'S CONSTANT

5.35x10(-14) atm-m(3)/mol (at 25 degrees C) (Howard, 1990)

3.9x10(-11) atm-m(3)/mol (at 25 degrees C) (estimated) (HSDB , 1998)

SPECTRAL CONSTANTS

5638 (Coblentz Society spectral Collection) (HSDB , 1998)

MASS

313 (Atlas of Mass Spectral Data) (HSDB , 1998)

OTHER/PHYSICAL

ODOR THRESHOLD

0.27 ppm (ACGIH, 1996(a))

CRITICAL PRESSURE

470 psia; 32 atm; 3.2 MN/m(2) (CHRIS , 1998)

CRITICAL TEMPERATURE

442 degrees C; 828 degrees F; 715 degrees K (CHRIS , 1998)

DIPOLE MOMENT

2.81 (Budavari, 1996)

DISSOCIATION CONSTANT

pKa = 8.97 (Howard, 1990)
pKa = 8.88 (HSDB , 1998)

HEAT OF COMBUSTION

-10,790 Btu/lb; -6000 cal/g; 0.251x10(5) J/kg (CHRIS , 1998)

INDEX OF REFRACTION

1.4753 (at 30 degrees C) (Budavari, 1996)

NUCLEAR MAGNETIC RESONANCE

6575 (Sadtler Research Laboratories Spectral Collection) (HSDB , 1998)

VISCOSITY

351.9 cp (at 30 degrees C) (Budavari, 1996)
53.85 cp (at 60 degrees C) (Budavari, 1996)

-REFERENCES

GENERAL BIBLIOGRAPHY

40 CFR 372.28: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Lower thresholds for chemicals of special concern. National Archives and Records Administration (NARA) and the Government Printing Office (GPO). Washington, DC. Final rules current as of Apr 3, 2006.

40 CFR 372.65: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Chemicals and Chemical Categories to which this part applies. National Archives and Records Association (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Apr 3, 2006.

49 CFR 172.101 - App. B: Department of Transportation - Table of Hazardous Materials, Appendix B: List of Marine Pollutants. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 29, 2005.

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62 FR 58840: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 1997.

65 FR 14186: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.

65 FR 39264: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.

65 FR 77866: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.

66 FR 21940: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2001.

67 FR 7164: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2002.

68 FR 42710: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2003.

69 FR 54144: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2004.

AIHA: 2006 Emergency Response Planning Guidelines and Workplace Environmental Exposure Level Guides Handbook, American Industrial Hygiene Association, Fairfax, VA, 2006.

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DIETHANOLAMINE

Classification | Information to evaluate chemical incidents

Information to evaluate chemical incidents

Information to evaluate chemical incidents

Information to evaluate chemical incidents