PARIS GREEN
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
PARIS GREEN (ACETATO-O)(TRIMETAARSENITO)DICOPPER ACETOARSENITE DE CUIVRE (French) (ACETO)TRIMETAARSENITODICOPPER BASE GREEN BASLE GREEN C.I. 77410 C.I. PIGMENT GREEN C.I. PIGMENT GREEN 21 C.I. PIGMENT GREEN 21 (9CI) COPPER ACETATE ARSENITE COPPER (II) ACETATE META-ARSENATE COPPER (II) ACETATE META-ARSENITE COPPER ACETO-ARSENITE COPPER ACETOARSENITE COPPER ACETOARSENITE, solid(DOT) COPPER, BIS(ACETATO)HEXAMETAARSENITOTETRA- CUPRIC ACETOARSENITE EMERALD GREEN ENT 884 FRENCH GREEN GENUINE PARIS GREEN IMPERIAL GREEN KING'S GREEN MEADOW GREEN MINERAL GREEN MITIS GREEN MOSS GREEN MOUNTAIN GREEN NEUWIED GREEN NEW GREEN ORTHO P-G BAIT PARIS GREEN, solid PARROT GREEN PATENT GREEN POWDER GREEN SCHWEINFURTERGRUN SCHWEINFURT GREEN SCHWEINFURTH GREEN SOWBUG & CUTWORM BAIT SOWBUG CUTWORM CONTROL SWEDISH GREEN VIENNA GREEN WUERZBERG GREEN ZWICKAU GREEN
IDENTIFIERS
SYNONYM REFERENCE
- (RTECS , 1991; EPA, 1985; Budavari, 1989; HSDB , 1991)
USES/FORMS/SOURCES
Paris Green was extensively used in the past as an insecticide, wood preservative, and pigment (particularly for marine anti-fouling paints) and has also been used as an anthelmintic and larvicide (EPA, 1985; Sax & Lewis, 1987; HSDB , 1993). It is not currently used in the USA (Morgan, 1989).
Paris Green is an inorganic trivalent arsenic compound which also contains copper (Morgan, 1989). It is an odorless, emerald green-colored, crystalline powder (Budavari, 1989; Sax & Lewis, 1987; EPA, 1985). It is soluble in ammonium hydroxide and insoluble in cold water and alcohol (HSDB , 1993). The ACGIH has established a Biological Exposure Index (BEI) for arsenic. Refer to the BIOMONITORING section for more information. This review is based on the effects of arsenic and its inorganic compounds in general. Effects attributed specifically to Paris Green are identified. The toxicology of arsenic and its compounds has been reviewed (Friberg et al, 1986).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Paris Green is an inorganic trivalent arsenic compound which also contains copper. It is an emerald green colored, crystalline powder. Although some absorption may occur from dermal contact or inhalation, most poisonings result from ingestion. Upper respiratory tract irritation may result from inhalation exposure.
- Systemic Paris Green poisoning is primarily due to the arsenic content, and is not different from any other arsenic poisoning. Chronic copper poisoning from Paris Green exposure is essentially unknown in humans. It is advisable to treat all arsenic compounds as highly toxic.
- Multiple keratoses, chronic lymphatic leukemia and macular degeneration have been tied to occupational exposure.
- Acute arsenic ingestion generally produces symptoms within 30 to 60 minutes, but onset may be delayed for several hours if ingested with food. A metallic or garlic taste, vomiting, abdominal pain, dysphagia, and profuse watery (rice-water-like) and sometimes bloody diarrhea may occur. Dehydration, intense thirst, and fluid-electrolyte disturbances are common. Hypovolemia from capillary leaking ("third spacing" of fluids) is a common early sign.
- Systemic arsenic poisoning from occupational exposure is uncommon. Arsenic workers have developed a hoarse voice; nasal irritation and possible perforation of the nasal septum; irritation of eyes, skin, and mucous membranes; and, rarely, cirrhosis of the liver. Nausea and vomiting are infrequent. Painful ulceration of the wrist and scrotal skin, lips, and nostrils may develop with dust exposure.
- The primary target organs initially are the gastrointestinal tract, heart, brain, and kidneys. Seizures and pulkonary edema can result from exposure. Eventually, the skin, bone marrow, and peripheral nervous system may be significantly damaged. The peripheral neuropathy appears similar regardless of the route of exposure.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. 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.
ACUTE CLINICAL EFFECTS
- From its acute oral LD50 of 22 mg/kg in rats (RTECS , 1993), Paris Green is a HIGHLY TOXIC SUBSTANCE. Although some absorption may occur from dermal contact or inhalation, most Paris Green poisonings result from ingestion (EPA, 1985). It is an eye, skin, and respiratory tract irritant (EPA, 1985; Grant, 1986; OHM/TADS , 1993). Systemic Paris Green poisoning is primarily due to the arsenic content, and signs and symptoms are not different from those caused by any other arsenic poisoning (Budavari, 1989; HSDB , 1993; OHM/TADS , 1993).
- Acute arsenic ingestion generally produces signs and symptoms within 30 to 60 minutes, but onset may be delayed for several hours if ingested with food (Morgan, 1989; Sittig, 1985). A metallic or garlic taste and garlic-like odor of the breath, vomiting, abdominal pain, dysphagia, and profuse watery (ricewater-like) and sometimes bloody diarrhea may occur (Sittig, 1985; Finkel, 1983; EPA, 1988).
- Dehydration, intense thirst, and fluid-electrolyte disturbances are common (Morgan, 1989). Hypovolemia from capillary leaking ("third spacing" of fluids) is a common early sign (Morgan, 1989; EPA, 1988; HSDB , 1993). Cardiac arrhythmias may occur, but may be secondary to electrolyte imbalance (Peterson & Rumack, 1977; Goldsmith, 1980; St Peter et al, 1970; Sittig, 1985).
- The primary initial target organs are the gastrointestinal tract, heart, brain, and kidneys (Sittig, 1985; Morgan, 1989; Finkel, 1983; HSDB , 1993). Eventually, the skin, bone marrow, and peripheral nervous system may be significantly damaged (Finkel, 1983; Morgan, 1989; Sittig, 1985; HSDB , 1993). Hemolysis, pancytopenia, and anemia may occur after acute arsenic poisoning (Kyle & Pease, 1965; Kjeldsberg & Ward, 1972).
- MEE'S LINES may be seen after acute exposure. Mee's lines commonly take 5 weeks to appear above the cuticle and advance 1 mm per week afterwards, allowing an approximation of the time of acute exposure (Heyman et al, 1956).
- Permanent encephalopathy may ensue from acute exposure to arsenic compounds. This encephalopathy can result in atrophy of the cortex one to six months after exposure (Fincher & Koerker, 1987), causing loss of many higher brain functions.
- Peripheral neuropathy (both sensory and motor) can appear in a similar pattern regardless of the route arsenic exposure (Finkel, 1983). It commonly begins 1 to 3 weeks following exposure (Le Quesne & McLeod, 1977; Heyman et al, 1956), usually as paresthesias of the soles of the feet and hands, progressing proximally over the next few days (Heyman et al, 1956).
- Severe muscle weakness and wasting then develop, causing severe disability (Le Quesne & McLeod, 1977). It may initially be confused with Guillain-Barre' syndrome (Donofrio et al, 1987). Paresthesias may be painful and are frequently described as severe burning pain in a "stocking and glove" distribution.
- Physical findings of arsenic peripheral neuropathy include prominently decreased sensation to touch, pinprick, and temperature, frequently in a stocking and glove distribution (Heyman et al, 1956). Loss of vibration sense is also common. Profound muscle weakness and wasting, distal more than proximal, is also seen (Donofrio et al, 1987; Heyman et al, 1956). Wrist drop, foot drop, and muscle fasciculations may also occur in patients with arsenic poisoning (Heyman et al, 1956).
- Arsenic is a general cellular poison. It inhibits enzymes required for cellular respiration and depletes cellular energy stores, leading to cell death (Schoolmeester & White, 1980).
CHRONIC CLINICAL EFFECTS
- Systemic absorption of as little as 3 to 4 mg of arsenic per day can cause chronic poisoning (HSDB , 1993). Trivalent arsenicals, such as those found in Paris Green, are eliminated less rapidly than pentavalent compounds and can thus cause CUMULATIVE TOXICITY (HSDB , 1993). Chronic COPPER poisoning from Paris Green exposure is essentially unknown in humans (OHM/TADS , 1993).
- Effects of chronic arsenic poisoning include hyperpigmentation of the skin (especially on the palms of the hands and soles of the feet), BLACKFOOT DISEASE, anemia, peripheral neuropathies, cirrhosis of the liver, hair loss, and nail changes (ILO, 1983) Finkel, 1983).
- Workers chronically exposed to arsenic by inhalation and dermal contact have mainly developed a hoarse voice, nasal irritation, perforation of the nasal septum, irritation of eyes, skin, and mucous membranes, and rarely, cirrhosis of the liver (ACGIH, 1986; (Finkel, 1983; Sittig, 1985; Proctor et al, 1988; Clayton & Clayton, 1981). Nausea and vomiting are infrequent complaints among chronically-exposed arsenic workers (Clayton & Clayton, 1981). Painful ulceration of the wrist and scrotal skin, lips, and nostrils may develop with chronic arsenic dust exposure (Finkel, 1983; Sittig, 1985).
- Dermatitis due to Paris Green exposure has a dry, scaly appearance and can result in a brownish skin pigmentation (Grant, 1986), commonly found on the scrotum, inguinal area, and nasolabial folds (HSDB , 1993). Lesions may begin with erythema and progress to eczema with weeping, followed by healing with a dark pigmentation (HSDB , 1993). These skin lesions may vary from local inflammation, with or without the presence of ulcers, to thickened, hyperkeratotic and pigmented lesions (Finkel, 1983). Malignant transformation may occur in some of these skin lesions (Finkel, 1983).
- Chronic arsenic poisoning can result in alopecia and liver enlargement in addition to the signs and symptoms mentioned in the ACUTE EXPOSURE section (Finkel, 1983). Aplastic anemia has been described after chronic arsenic exposure (Kjeldsberg & Ward, 1972).
- Arsenic compounds can cause cancer in humans. (Refer to the CARCINOGENIC EFFECTS section below for more information.)
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
One milligram/kilogram of ingested arsenic may be lethal in a child (Woody & Kometani, 1948; HSDB , 2000). As little as 20 milligrams of arsenic may produce life-threatening toxicity (Zaloga et al, 1970; Schoolmeester & White, 1980; Hutton & Christians, 1983). An oral dose of 120 mg of arsenic trioxide may be fatal (Finkel, 1983).
Between 1966 and 1979, 61 cases of accidental sodium arsenite poisoning, including 11 patients who were hospitalized and 24 fatal cases in adults and children, were reported to the EPA's Pesticide Incident Monitoring System (PIMS) (EPA, 1988).
MAXIMUM TOLERATED EXPOSURE
Estimates of acute oral toxic doses of various arsenic compounds range from 1 milligram to 10 grams. Arsenic trioxide in a solubilized form becomes sodium arsenite, which is more toxic than in an unsolubilized form. 200 milligrams of arsenic trioxide ingested acutely by an adult may be lethal (Baselt & Cravey, 1989; Baselt, 1988). Trivalent arsenic (arsenite) is more toxic in animals than the pentavalent form (arsenate) (Morgan, 1989). However, significant toxicity may occur with large amounts of pentavalent salts in humans. Pentavalent arsenic may be converted in vivo to trivalent arsenic.
INFANT ADULT A 30-year-old man survived an ingestion of 6 ounces of "Blue Ball Rat Killer" containing 1.5% arsenous oxide (2,150 milligrams metallic arsenic per 6 ounces) with aggressive therapy (fluid resuscitation, chelation, and hemodialysis) (Fesmire et al, 1988).
OCCUPATIONAL
- Carcinogenicity Ratings for CAS12002-03-8 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed 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): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS12002-03-8 (U.S. Environmental Protection Agency, 2011):
References: RTECS, 2000 Lewis, 1996; Budavari, 1996 OHM/TADS, 2000 LD50- (ORAL)RABBIT: 13 mg/kg - convulsions or effect on seizure threshold, altered food intake (animal), hypermotility, diarrhea
LD50- (ORAL)RAT: 22 mg/kg Female, 100 mg/kg
LD50- (SKIN)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS12002-03-8 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS12002-03-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS12002-03-8 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS12002-03-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS12002-03-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS12002-03-8 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS12002-03-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS12002-03-8 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS12002-03-8 (U.S. Environmental Protection Agency, 2010):
Listed as: Paris Green Reportable Quantity, in pounds: 1 Threshold Planning Quantity, in pounds: Note(s): Not Listed
- EPA SARA Title III, Community Right-to-Know for CAS12002-03-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS12002-03-8 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS12002-03-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1585 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1585 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS12002-03-8 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 12002-03-8.
-PHYSICAL HAZARDS
FIRE HAZARD
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS12002-03-8 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS12002-03-8 (NFPA, 2002):
REACTIVITY HAZARD
- Contact with strong oxidizers may cause fire and explosion (Pohanish & Greene, 1997).
EVACUATION PROCEDURES
- 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 151 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 25 to 50 meters (80 to 160 feet) in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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 151 (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: UNITED STATES:
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.
- AIHA ERPG Values for CAS12002-03-8 (AIHA, 2006):
- DOE TEEL Values for CAS12002-03-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Paris Green (Cupric acetoarsenite) TEEL-0 (units = mg/m3): 1.13 TEEL-1 (units = mg/m3): 3.38 TEEL-2 (units = mg/m3): 22 TEEL-3 (units = mg/m3): 22 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 CAS12002-03-8 (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; 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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):
- NIOSH IDLH Values for CAS12002-03-8 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) 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. Cover with plastic sheet to prevent spreading. 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 151 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Paris Green is an emerald green, crystalline, ordorless powder (Budavari, 1996) HSBD, 2000).
-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.
- 49 CFR 172.101: Department of Transportation - Table of Hazardous Materials. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 11, 2005.
- 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.
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