MOBILE VIEW  | 

ASBESTOS

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) Asbestos is a group of six naturally occurring silicate fibrous minerals. Different forms of asbestos vary in content of iron, magnesium, calcium, aluminum, sodium oxides, and trace elements (i.e., Ni, Mn, Cr, K, Na and Ti) (ATSDR, 1990).
    B) The term "asbestos" can refer either to the minerals or to the industrial product obtained by mining and processing the minerals (ACGIH, 1991).

Specific Substances

    A) ASBESTOS
    1) Asbesto (French)
    2) Amiante (French)
    3) Asbestos (Greek)
    4) Amianto (Portugese)
    5) Asbesto (Portugese)
    6) Asbesto (Spanish)
    7) Amianto (Spanish)
    8) Asbesto (Italian)
    9) Amianto (Italian)
    10) Asbest (German)
    11) Acoect (Russian)
    SPECIFIC SUBSTANCES
    1) AMIANTHUS
    2) AMOSITE
    3) AMPHIBOLE
    4) ASBEST (GERMAN)
    5) ASBESTO (SPANISH)
    6) ASBESTOS
    7) ASBESTOS DUST
    8) ASBESTOS FIBER
    9) ASBESTOS FIBRE
    10) ASBESTOSE (GERMAN)
    11) ASCARITE
    12) FIBROUS GRUNERITE
    13) KROKYDOLITH (GERMAN)
    Serpentine asbestos -- Chrysotile (white asbestos)
    1) 5R04
    2) 7-45 ASBESTOS
    3) AVIBEST
    4) AVIBEST C
    5) CALIDRIA RG 100
    6) CALIDRIA RG 144
    7) CALIDRIA RG 600
    8) CASSIAR AK
    9) CHRYSOTILE
    10) HOOKER NO. 1 CHRYSOTILE ASBESTOS
    11) K 6-30
    12) K6-30
    13) METAXITE
    14) PLASTIBEST 20
    15) RG 600
    16) SERPENTINE
    17) SERPENTINE ASBESTOS
    18) SERPENTINE CHRYSOTILE
    19) SYLODEX
    20) WHITE ASBESTOS
    21) CAS 12001-29-5
    Amphibole asbestos -- Actinolite
    1) CAS 77536-66-4
    Amphibole asbestos -- Amosite
    1) AMOSITE
    2) BROWN ASBESTOS
    3) FIBROUS CUMMINGTONITE/GRUNERITE
    4) GRUNERITE ASBESTOS
    5) MYSORITE
    6) CAS 12172-73-5
    Amphibole asbestos -- Anthophyllite
    1) ANTHOPHYLLITE
    2) AZOBOLEN ASBESTOS
    3) FERROANTHOPHYLLITE
    4) CAS 77536-67-5
    Amphibole asbestos -- Crocidolite
    1) AMORPHOUS CROCIDOLITE ASBESTOS
    2) BLUE ASBESTOS
    3) CROCIDOLITE
    4) FIBROUS CROCIDOLITE ASBESTOS
    5) KROKYDOLITH (GERMAN)
    6) CAS 12001-28-4
    Amphibole asbestos -- Tremolite
    1) CALCIUM MAGNESIUM SALT (8:4)
    2) FIBROUS TREMOLITE
    3) SILICIC ACID
    4) CAS 77536-68-6
    GENERAL TERMS
    1) CHRYSOTILE ASBESTOS
    2) CASSIER AK
    3) CALCIUM MAGNESIUM SALT
    4) CROCIDOLITE ASBESTOS
    5) AMPHIBOLE ASBESTOS
    6) ACTINOLITE
    7) MYORSITE
    8) TREMOLITE

    1.2.1) MOLECULAR FORMULA
    1) ActinoliteCa2Fe5Si8O22(OH)2Actinolite(Ca2(Mg,Fe)5Si8O22(OH)2)nAmosite(Fe(2+))2(Fe(2+), Mg)5Si8O22(OH)2Amosite((Mg,Fe)7Si8O22(OH)2)nAnthophyllite((Mg,Fe)7Si8O22(OH)2)nAnthophylliteMg7Si8O22(OH)2ChrysotileMg3Si2O5(OH)4CrocidoliteNa2Fe(2+), Mg(3Fe(3+)Si8O22(OH)2)Crocidolite(NaFe3(2+)Fe2(3+)Si8O22(OH)2)nTremoliteCa2Mg5Si8O22(OH)2Tremolite(Ca2Mg5Si8O22(OH)2)n

Available Forms Sources

    A) FORMS
    1) The name asbestos is used as a general term for the class of natural fibrous silicates, a group of naturally occurring, hydrated silicate minerals of the serpentine or amphibole mineralogical series characterized by fibers or bundles of fine, single crystal fibrils. Asbestos includes chrysotile, of the serpentine family of minerals which is structurally different from the other amphibole forms. The amphibole family includes amosite, crocidolite, and the fibrous varieties of tremolite, actinolite, and anthophyllite. The four types of asbestos used commercially are chrysotile (white), crocidolite (blue), amosite (brown), and anthophyllite (ATSDR, 2001; Baxter, et al., 2000; Bingham, et al., 2001; (S Budavari , 2001; Lewis, 1998).
    2) Asbestos fibers form from mineral deposits that, under certain conditions and for enough time, lead to their chemical composition and their structural development from silicate chains into fibrous structures that are loosely bonded in a parallel array (fiber bundles) or matted masses. Individual fibrils, separated easily from the bundles, are needle-shaped, crystal rods. Typical length to width ratios of naturally occurring asbestos fibers are approximately 100 and higher. Asbestos fibers are insoluble, moldable, chemically inert, and have unique tensile strength. They are also poor conductors of heat (ATSDR, 2001: Bingham, et al., 2001; (Lewis, 1998).
    3) SERPENTINE ASBESTOS (CHRYSOTILE)
    a) The most common and most abundant form of asbestos is the mineral chrysotile, the fibrous form of the serpentine mineral group. Chrysotile is referred to as white asbestos and is a magnesium silicate mineral. Mining of chrysotile produces bundles of soft flexible fibers that can be up to several centimeters long. The fibers easily divide into smaller bundles and into individual fibrils. The individual fibril is made up of double sheets of brucite (Mg (OH)2) and silica (SiO2) rolled around a small core of amorphous magnesium silicate, resembling a curved tube from 25 to 50 nm in diameter. The thin crystalline fibers are strong and flexible and are capable of being woven. Due to their structure, the chrysotile fiber aggregates can withstand mechanical treatment better than the amphiboles (ATSDR, 2001; Baxter, et al., 2000; Bingham, et al., 2001; (S Budavari , 2001).
    b) A microcrystalline form of chrysotile, or serpentine asbestos, was developed and is known as TM "Avibest" (Lewis, 2001).
    4) AMPHIBOLE ASBESTOS
    a) Amphibole asbestos includes various silicates of magnesium, iron, calcium, and sodium. The fibers of this group are generally more brittle than serpentine asbestos and therefore fabrication is limited and they cannot be spun. In addition, amphibole fibers are more resistant to chemicals and heat than serpentine asbestos. Amphibole asbestos includes actinolite, amosite (brown asbestos), anthophyllite, crocidolite (blue asbestos), and tremolite. Anthophyllite, amosite, and crocidolite have been used commercially. The amphiboles can form a variety of polymeric structures by forming Si-O-Si bonds. The linear double chain structure crystallizes into long, thin, straight fibers that are characteristic of this type of asbestos. Many other amphiboles occur in commercially exploited minerals (Baxter, et al., 2000; (Lewis, 2001).
    5) ACTINOLITE
    a) Some of the asbestos minerals exist as a range of chemical forms, due to ion or ionic group substitution. In particular, actinolite and tremolite form a solid solution series, where magnesium and iron (II) freely substitute with each other. Iron replaces magnesium going from tremolite to actinolite (ATSDR, 2001).
    6) AMOSITE
    a) Amosite is a commercial name for fibrous grunerite, or iron magnesium silicate. Also known as brown asbestos, it is yellowish- gray to dark brown and it will appear vitreous to pearly in luster. The fibers are course. In use the fibers may be split to 100 nm diameter (Baxter, et al., 2000; Bingham, et al., 2001).
    7) ANTHOPHYLLITE
    a) Anthophyllite is the fibrous form of another iron magnesium silicate (not grunerite). It has similar properties as amosite, but no longer has commercial value (Baxter, et al., 2000).
    8) CROCIDOLITE
    a) Crocidolite is a cobalt blue to lavender blue mineral. It can appear from silky to dull in luster. It is the fibrous form of riebeckite, a sodium iron silicate. Fiber bundles are shorter and more stiff than chrysotile and readily split to straight fibrils of minimum diameter of 100 nm(Bingham, et al., 2001).
    9) TREMOLITE
    a) Tremolite is a calcium magnesium silicate. It may be gray-white, green, yellow, or blue and has a silky luster. It crystallizes as an amphibole fiber or as a plately talc. Fibrous tremolite does not have industrial applications. It is found as a contaminant with other fibers, such as chrysotile, and with talc. Tremolite and actinolite form a continuous mineral series with iron (II) and magnesium substitution ongoing while maintaining the same three-dimensional crystal structure. Tremolite contains little or no iron, and actinolite contains iron (ATSDR, 2001; Baxter, et al., 2000; Bingham, et al., 2001).
    B) SOURCES
    1) The various forms of asbestos result from water leaching siliceous minerals from the parent rock and then recrystallization in the interstices of the parent rock. The compound metallic silicates crystallize as very long, thin particles. The metal content will vary as limited by the structure of the crystal lattices. Deposits of fibrous minerals usually are found in veins where fibers are at right angles to the vein walls (ATSDR, 2001; Baxter, et al., 2000).
    2) Open pit mines were the main source of asbestos mined in the United States. Ore was blasted or drilled to extract it from the earth, and then crushed, dried, and stored until milling operations were undertaken. Milling involved crushing, fiberizing, screening, aspirating, and grading operations. More current methods utilized mechanical means for removal rather than blasting, as well as using watering during the milling process, to reduce air emissions (ATSDR, 2001).
    3) SERPENTINE ASBESTOS (CHRYSOTILE)
    a) The asbestiform chrysotile variety of serpentine asbestos occurs in only a small part of serpentine mineral deposits. The cross-vein deposit is the most common chrysotile deposit, and most industrial chrysotile fibers are extracted from such deposits. Ninety percent of asbestos in commercial use is from chrysotile. It is mined in large deposits in central Russia and Quebec, Canada and in smaller deposits in western Canada, the U.S., the Mediterranean basin, in southern Africa, and in Australia (Baxter, et al., 2000; Bingham, et al., 2001).
    4) AMPHIBOLE ASBESTOS
    a) The amphibole group of minerals are widespread, although only a few varieties are asbestiform and these occur in small quantities (Bingham, et al., 2001).
    1) AMOSITE
    a) Mining of amosite occurs in the Transvaal (Baxter, et al., 2000).
    2) ANTHOPHYLLITE
    a) Anthophyllite was mined until recently from a historically used deposit in Finland (Baxter, et al., 2000).
    3) CROCIDOLITE
    a) Crocidolite (blue asbestos) is mined in the North West Cape province of the Republic of South Africa and to a lesser extent in the Transvaal; smaller scale mining has also occurred in Western Australia. It is found in banded ironstone. In the South Africa deposit, amphibole fibers of crocidolite originated from a gel of iron hydroxide and colloidal silica, that were later consolidated by a secondary reaction yielding formations of banded ironstone (Baxter, et al., 2000; Bingham, et al., 2001).
    4) TREMOLITE
    a) Deposits of chrysotile are sometimes associated with fibrous tremolite, including those in the Mediterranean basin and a large deposit in China (Baxter, et al., 2000).
    5) The general population can be exposed to asbestos by the inhalation route of exposure. In the ambient air, asbestos arises from natural sources, from windblown soil from hazardous waste sites, deterioration of automobile clutches and brakes, or breakdown of asbestos-containing materials such as insulation. Exposure to general occupants of modern or recently renovated commercial buildings in the USA is not likely to be higher than background levels (ATSDR, 2001; Reynolds et al, 1994).
    6) Significant environmental exposure can occur from friable asbestos in older buildings that are deteriorated, remodeled, or destroyed. Public buildings, such as schools, previously used asbestos as a fireproof insulation in ceiling or walls (Mossman et al, 1990; Mossman & Gee, 1989; Murray, 1990; Spurny, 1989; Stein et al, 1989).
    7) Most European countries have banned asbestos-containing insulation material from their new buildings (Mendes, 2001).
    C) USES
    1) Asbestos has been mined for use in a variety of manufactured products due to its low cost and desirable properties such as heat and fire resistance; wear and friction characteristics; tensile strength; heat, electrical and sound insulation; adsorption capacity; and resistance to chemical and biological attack. It has been mostly used in building materials, friction products, and heat-resistant fabrics. Particular asbestos-containing products include fireproof fabrics, such as for gloves and clothing or furnace and hot pipe coverings; in heat-resistant insulators; brake linings; gaskets; roofing materials (i.e., asbestos cement); electrical and heat insulation; paint filler; chemical filters; and diaphragm cells. It is also used as a reinforcing agent in rubber, plastics, and cement, as an inert filler medium (laboratory and commercial uses), and as a component of paper dryer felts (ATSDR, 2001; (S Budavari , 2001; ILO , 1998; Lewis, 2001).
    2) Nearly 3,000 applications or types of products were listed for asbestos during its peak demand. Most applications involve bonding with other materials such as resins, plastics, and Portland cement (i.e., floor tiles, cements, and roofing felts and shingles), while other applications utilize asbestos as a loose fibrous mixture, powder, or woven as a textile (i.e., insulation material, cement powders, and acoustical products). U.S. consumption has declined from 790 million pounds in 1980 to 46 million pounds in 1997, and consumption was reduced to 34.8 million pounds per year by 1998 and 1999. The consumption pattern for 1999 was 61% roofing products, 19% gaskets, and 13% for friction products, such as clutch, brake and transmission components. Chrysotile is the only form used in U.S. manufacturing today (ATSDR, 2001; (Pohanish, 2002).
    3) Amosite, chrysotile, and crocidolite were used industrially in the U.S.; anthophyllite originates and is used commercially in Finland. Of the asbestos used in North America, 95% of the natural mineral fibers used has been chrysotile from Canada. The remaining 5% has been amosite and crocidolite, imported from South Africa (ACGIH, 2001).
    4) The following list of suspect asbestos-containing materials (ACM) was compiled by EPA as a guide ((EPA, 2002f)):
    1) Cement Pipes
    2) Cement Wallboard
    3) Cement Siding
    4) Asphalt Floor Tile
    5) Vinyl Floor Tile
    6) Vinyl Sheet Flooring
    7) Flooring Backing
    8) Construction Mastics (floor tile, carpet, ceiling tile, etc.)
    9) Acoustical Plaster
    10) Decorative Plaster
    11) Textured Paints/Coatings
    12) Ceiling Tiles and Lay-in Panels
    13) Spray-Applied Insulation
    14) Blown-in Insulation
    15) Fireproofing Materials
    16) Taping Compounds (thermal)
    17) Packing Materials (for wall/floor penetrations)
    18) High Temperature Gaskets
    19) Laboratory Hoods/Table Tops
    20) Laboratory Gloves
    21) Fire Blankets
    22) Fire Curtains
    23) Elevator Equipment Panels
    24) Elevator Brake Shoes
    25) HVAC Duct Insulation
    26) Boiler Insulation
    27) Breaching Insulation
    28) Ductwork Flexible Fabric Connections
    29) Cooling Towers
    30) Pipe Insulation (corrugated air-cell, block, etc.)
    31) Heating and Electrical Ducts
    32) Electrical Panel Partitions
    33) Electrical Cloth
    34) Electric Wiring Insulation
    35) Chalkboards
    36) Roofing Shingles
    37) Roofing Felt
    38) Base Flashing
    39) Thermal Paper Products
    40) Fire Doors
    41) Caulking/Putties
    42) Adhesives
    43) Wallboard
    44) Joint Compounds
    45) Vinyl Wall Coverings
    46) Spackling Compounds
    5) EPA prohibited spraying of asbesto containing material (ACM) on buildings and structures for fireproofing and insulation purposes in 1973; decorative applications were later included in the ban. Other uses were banned by the Consumer Product Safety Commission, including asbestos in patching compounds and in hair dryer heat shields. A 1989 EPA regulation known as the Asbestos Ban and Phase-out Rule would have prohibited the manufacture, importation, processing, and distribution in commerce of asbestos and most ACM by 1997 under the Toxic Substances and Control Act (TSCA), but the rule was overturned in 1991 as the result of a lawsuit. Currently banned products and uses include all new uses of asbestos, roofing felt, commercial, corrugated, and specialty paper, millboard, rollboard (ATSDR, 2001; ((EPA, 2002f); (EPA, 2002g)).
    6) Asbestos was used as a filter agent during winemaking. Some countries, including the U.S., have replaced its use with diatomaceous earth (ILO , 1998).
    7) Asbestos is used as the diaphragm during the production of chlorine from the diaphragm cell method (ILO , 1998).

Life Support

    A) This overview assumes that basic life support measures have been instituted.

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) USES: Asbestos has been mined for use in a variety of manufactured products due to its low cost and desirable properties, such as heat and fire resistance, wear and friction characteristics, tensile strength, heat, electrical, and sound insulation, adsorption capacity, and resistance to chemical and biological attack. It has been mostly used in building materials, friction products, and heat-resistant fabrics.
    B) TOXICOLOGY: Asbestos exposure occurs from inhalation of airborne fibers or from ingestion of fibers. All asbestos fiber types are fibrogenic and known to cause asbestosis, pleural changes, lung cancer, and mesothelioma. Most human studies have examined exposure to chrysotile, the most widely used type of asbestos. Asbestosis has been reported in populations exposed to amosite, crocidolite, tremolite, and anthophyllite asbestos. Crocidolite has the greatest potential to produce disease, followed by amosite and chrysotile.
    C) EPIDEMIOLOGY: It has been estimated that of the 4 million workers heavily exposed to asbestos, at least 1.6 million (35% to 44%) are expected to die of asbestos-related cancers. It is estimated that between 58,000 and 75,000 asbestos-associated deaths will occur each year, which will account for between 13% and 18% of the total cancer deaths in the United States.
    D) WITH POISONING/EXPOSURE
    1) CHRONIC TOXICITY: Asbestos exposure increases the risk for non-malignant asbestos-related lung and pleural disorders (asbestosis, pleural plaques, pleural thickening, and pleural effusions), lung cancer, and mesothelioma. Chronic inhalation of asbestos fibers may lead to a characteristic pneumoconiosis termed asbestosis, a diffuse interstitial lung fibrosis. Individuals with fully developed asbestosis will experience dyspnea, which is often accompanied by rales or cough. Deficits in pulmonary function variables, (ie, forced expiratory volume in one second (FEV1) and forced vital capacity (FVC)), also occur. Asbestosis can cause cardiovascular effects, such as pulmonary hypertension and compensatory hypertrophy of the right heart (cor pulmonale). Besides asbestosis, chronic asbestos exposure causes lung cancer, mesothelioma (primarily of the pleura but also of the peritoneum), pleural disease, and pleural plaques. Tobacco smokers, exposed to asbestos, are at greater risk for lung cancer than nonsmokers. Cancers at sites other than the respiratory system have been linked to asbestos exposure, including gastrointestinal carcinomas, cancer of the kidney, brain, bladder, larynx, and pancreas, and unspecified malignant lymphomas. The ACGIH places asbestos (all forms) in category A1, Confirmed Human Carcinogen. The IARC classifies asbestos in Group 1: Carcinogenic to humans. The NTP classifies asbestos as a known carcinogen.
    0.2.20) REPRODUCTIVE
    A) Transplacental transfer of asbestos may occur, but this has not been linked with any adverse reproductive outcomes in humans.
    0.2.21) CARCINOGENICITY
    A) Asbestos is a human carcinogen. The primary types of asbestos-related cancers are mesothelioma of the pleura and peritoneum and bronchogenic carcinoma.
    B) An increasing number of reports are suggesting an association between asbestosis and gastrointestinal, renal, or laryngeal malignancies; these reports have been refuted by others.

Laboratory Monitoring

    A) Monitor chest CT scan, chest x-ray, and pulmonary function tests in asbestos-exposed patients.
    B) Open lung biopsy is the only definitive diagnostic test for asbestosis.
    C) Bronchoalveolar lavage (BAL) has been recommended as an adjunct in the diagnosis of asbestos-related pulmonary diseases.
    D) OSHA has specific clinical monitoring requirements for workers exposed to asbestos.

Treatment Overview

    0.4.3) INHALATION EXPOSURE
    A) MANAGEMENT OF TOXICITY
    1) Since there is no effective therapy for an established case of asbestosis, treatment is aimed at maintaining vital capacity and reducing respiratory work load. Treatment may include the following: vaccination against pneumococcal pneumonia and influenza, bronchodilator administration, adequate nutrition, home oxygen therapy, rebreathing and exercise training, and smoking cessation. Pharmacological agents to limit the progression of fibrosis as yet have not been developed.
    B) DECONTAMINATION
    1) PREHOSPITAL: Most asbestos exposures are of a chronic nature, such that traditional first aid is not appropriate. In the event of a heavy acute exposure, move the patient to fresh air. Monitor for respiratory distress. Administer oxygen and assist ventilation as required.
    2) HOSPITAL: Most asbestos exposures are of a chronic nature, such that traditional first aid is not appropriate. In the event of a heavy acute exposure, move the patient to fresh air. Monitor for respiratory distress. Administer oxygen and assist ventilation as required. Treat bronchospasm with inhaled beta-2 agonist and oral or parenteral corticosteroids.
    C) AIRWAY MANAGEMENT
    1) Administer oxygen and assist ventilation as required. Treat bronchospasm with inhaled beta-2 agonist and oral or parenteral corticosteroids.
    D) ANTIDOTE
    1) None
    E) PATIENT DISPOSITION
    1) HOME CRITERIA: There is no role for home management.
    2) OBSERVATION CRITERIA: Patients with known asbestos exposure require outpatient monitoring to detect complications.
    3) ADMISSION CRITERIA: While there is no specific therapy for asbestos exposure, patients may require inpatient therapy for their poor pulmonary function or cancer treatment.
    4) CONSULT CRITERIA: A toxicologist may be consulted to aid in determining if a patient's symptoms or cancer is from a previous exposure to asbestos. Consult a pulmonologist for patients with evidence of asbestos-induced pulmonary complications.
    F) PITFALLS
    1) Failure to recognize a worker is exposed to asbestos and not instituting appropriate industrial hygiene protective measures.
    G) TOXICOKINETICS
    1) Asbestos fibers thicker than 3 micrometers (mcm) in diameter or longer than 100 mcm are either not inhaled or are rapidly cleared from the respiratory tract. On a weight basis, only a very small proportion of inhaled fibers are retained. When inoculated intrapleurally, the majority of asbestos fibers were cleared during the first 10 days. Subsequently, there was very small elimination through the gut.
    2) An inverse relationship between intensity of exposure and time of disease development has been suggested. Depending on the level of workplace exposure, the latency period may range from 5 to 6 years to 10 to 20 years.
    H) DIFFERENTIAL DIAGNOSIS
    1) The differential diagnosis of asbestosis includes coal workers, pneumonoconiosis, dermatomyositis, hypersensitivity pneumonitis, idiopathic pulmonary fibrosis, sarcoidosis, and silicosis.

Range Of Toxicity

    A) TOXICITY: Low-level exposures or occupational exposure for under two years were not associated with increased mortality. Asbestosis has rarely been reported with intense exposure of only one day's duration. Lowest observed adverse effect levels (LOAELs) for systemic effects, determined from human inhalation studies, range from 25 to 54 fiber-year/mL (f-yr/mL, obtained by multiplying years of exposure times the average air concentration in fibers/mL) for intermediate exposure duration of 15 to 364 days. At the chronic exposure duration level (365 days or more), LOAELs ranged from 20 to 207 f-yr/mL for less serious systemic effects (those not expected to cause significant dysfunction or death or the significance is not entirely clear) and from 15 to 1271 f-yr/mL for serious systemic effects (those that evoke failure in a biological system and can lead to morbidity or mortality). LOAELs for cancer from chronic inhalation exposure, based on human studies, ranged from 5 to 1050 f-yr/mL.

Summary Of Exposure

    A) USES: Asbestos has been mined for use in a variety of manufactured products due to its low cost and desirable properties, such as heat and fire resistance, wear and friction characteristics, tensile strength, heat, electrical, and sound insulation, adsorption capacity, and resistance to chemical and biological attack. It has been mostly used in building materials, friction products, and heat-resistant fabrics.
    B) TOXICOLOGY: Asbestos exposure occurs from inhalation of airborne fibers or from ingestion of fibers. All asbestos fiber types are fibrogenic and known to cause asbestosis, pleural changes, lung cancer, and mesothelioma. Most human studies have examined exposure to chrysotile, the most widely used type of asbestos. Asbestosis has been reported in populations exposed to amosite, crocidolite, tremolite, and anthophyllite asbestos. Crocidolite has the greatest potential to produce disease, followed by amosite and chrysotile.
    C) EPIDEMIOLOGY: It has been estimated that of the 4 million workers heavily exposed to asbestos, at least 1.6 million (35% to 44%) are expected to die of asbestos-related cancers. It is estimated that between 58,000 and 75,000 asbestos-associated deaths will occur each year, which will account for between 13% and 18% of the total cancer deaths in the United States.
    D) WITH POISONING/EXPOSURE
    1) CHRONIC TOXICITY: Asbestos exposure increases the risk for non-malignant asbestos-related lung and pleural disorders (asbestosis, pleural plaques, pleural thickening, and pleural effusions), lung cancer, and mesothelioma. Chronic inhalation of asbestos fibers may lead to a characteristic pneumoconiosis termed asbestosis, a diffuse interstitial lung fibrosis. Individuals with fully developed asbestosis will experience dyspnea, which is often accompanied by rales or cough. Deficits in pulmonary function variables, (ie, forced expiratory volume in one second (FEV1) and forced vital capacity (FVC)), also occur. Asbestosis can cause cardiovascular effects, such as pulmonary hypertension and compensatory hypertrophy of the right heart (cor pulmonale). Besides asbestosis, chronic asbestos exposure causes lung cancer, mesothelioma (primarily of the pleura but also of the peritoneum), pleural disease, and pleural plaques. Tobacco smokers, exposed to asbestos, are at greater risk for lung cancer than nonsmokers. Cancers at sites other than the respiratory system have been linked to asbestos exposure, including gastrointestinal carcinomas, cancer of the kidney, brain, bladder, larynx, and pancreas, and unspecified malignant lymphomas. The ACGIH places asbestos (all forms) in category A1, Confirmed Human Carcinogen. The IARC classifies asbestos in Group 1: Carcinogenic to humans. The NTP classifies asbestos as a known carcinogen.

Heent

    3.4.6) THROAT
    A) LARYNGEAL ASBESTOSIS: Hyperplastic chronic laryngitis was identified in 10 workers in an asbestos cement factory (Kambic et al, 1989). Three of 4 tissue specimens examined by scanning electron microscopy had asbestos fibers on the epithelial surface.

Cardiovascular

    3.5.2) CLINICAL EFFECTS
    A) COR PULMONALE
    1) WITH POISONING/EXPOSURE
    a) In patients with asbestosis, severe pulmonary fibrosis and pulmonary hypertension secondary to increased resistance to pulmonary capillary blood flow can cause compensatory hypertrophy of the right heart (ATSDR, 1990).
    B) PERICARDITIS
    1) WITH POISONING/EXPOSURE
    a) Chronic constrictive pericarditis has been associated with asbestos exposure (Abejie et al, 2008; Fischbein et al, 1988; Davies et al, 1991).
    b) CASE REPORT: Constrictive pericarditis was reported in a 59-year-old boiler operator following a 30-year history of occupational exposure to asbestos-containing material without respiratory protection. His past medical history included an episode of pneumonia and chronic bronchitis. He also had a 20 pack-year history of smoking, although he had quit smoking approximately 23 years prior to the diagnosis of constrictive pericarditis. Chest radiographs showed pleural and pericardial calcifications and cardiac catheterization revealed intermittent equalization of left and right ventricular end diastolic filling pressures, indicative of constrictive pericarditis. Pulmonary function tests also indicated mild obstruction and mildly decreased diffusion capacity (Abejie et al, 2008).
    C) DISORDER OF CORONARY ARTERY
    1) WITH POISONING/EXPOSURE
    a) An association between pleural plaques and coronary disease has been suggested based on the observation that there has been an abnormal increase in the occurrence of these two diseases together. Further study is still required (Korhola et al, 2001).
    D) CHEST PAIN
    1) WITH POISONING/EXPOSURE
    a) In a comparison study of previously exposed workers to crocidolite and non-exposed individuals, radiographic findings of parenchymal or pleural disease were associated with the presence of chest pain, in particular anginal pain. More severe pain occurred among former workers, those with heavier exposure and in older subjects, which the authors suggested may be due to a dose-response effect of asbestos exposure. The results were based on a self-administered questionnaire (to assess quality of chest pain; further evaluation not performed) and chest radiography, which were graded independently by two examiners based on International Labor Organization standards (Mukherjee et al, 2000).

Respiratory

    3.6.2) CLINICAL EFFECTS
    A) ASBESTOSIS
    1) WITH POISONING/EXPOSURE
    a) DEFINITION: Asbestosis is defined as an irreversible diffuse bilateral interstitial fibrosis primarily affecting the lower 2/3 of the lung (ATSDR, 1990; Newhouse, 1983). Either heavy exposure for a short time or lower-level exposure over a longer period may result in asbestosis; cases have resulted from intense exposure of one day's duration (ATSDR, 1990).
    1) The development of defined asbestosis in an individual an exposure level above 20-25 fibers/mL times year (Muir, 1999).
    b) CLINICAL MANIFESTATIONS: Pleural asbestosis generally develops from chronic, low-level exposure; parenchymal asbestosis is related to higher-level exposures (ATSDR, 1990).
    1) Signs and symptoms include dyspnea on exertion, finger clubbing, clicking, and rales (bilaterally in the posterior axillae) (ILO, 1983; Newhouse, 1983). Persistent pleuritic pain may be a manifestation of asbestos-induced pleural disease (Miller, 1990).
    2) Cough is usually not present except in the late stages when distressing paroxysms occur (ILO, 1983). Increased sputum production is not present unless there is concomitant smoker's bronchitis (ILO, 1983).
    3) Early x-rays may not be diagnostic (Newhouse, 1983; Talcott & Antman, 1988).
    4) Clinical manifestations typically appear 10 to 40 years after onset of exposure (ATSDR, 1990; Demers et al, 1990). However, radiologic changes can occur before 20 years.
    5) Signs, symptoms, and abnormalities increase with longer duration of exposure (Demers et al, 1990; Selikoff et al, 1990). The typical restrictive pulmonary dysfunction can be obscured by chronic obstructive pulmonary disease due to smoking (Mossman & Gee, 1989).
    6) A long latency period of at least a decade exists between onset of histologic lesions and radiologically detectable stigmata (Kagan, 1988).
    7) Clubbed finger (digital hippocratism) can occur in 32% to 44% of cases, and is considered a late outcome, in general, which bears a poor prognosis (Begin et al, 1989) Boutin, 1994; (Valeyre & Letourneux, 1999).
    c) DIAGNOSIS: The diagnostic evidence is based on histopathology of the lesions (Craighead, 1982), and it relies on two criteria:
    1) The evidence of a rather diffuse pulmonary fibrosis that is limited to the peribronchiolar spaces and;
    2) the lesions bear asbestotic nodules.
    3) The diagnosis may also be obtained without a lung biopsy, by adopting the following procedures (Murphy, 1986; Rosenberg, 1997; (Mossman & Churg, 1998) Vleire, 1999):
    a) Risk estimation of asbestosis supported by a proper risk characterization of the work environment (i.e., exposure assessment) in a latency time of 15 years at least;
    b) positive diagnosis for infiltrating diffuse pneumopathy fostered by clinical observations, chest x-ray, computed tomography scan, and lung function (spirometry) tests; and
    c) the causal relationship between the age at first employment and the clinical, functional, and imaging aforementioned criteria, with differential diagnoses eliminated.
    d) CLINICAL COURSE: Pleural thickening progresses at the greatest rate among crocidolite miners and millers who develop early thickening after exposure. This progression decreases with time so that no progression may be noted more than 15 years after onset (de Klerk et al, 1989).
    1) Asbestosis may progress even after exposure terminates (Kagan, 1988; Talcott & Antman, 1988).
    2) Although asbestosis progresses slowly and may cease at any time, death may occur from cor pulmonale or from lung cancer (Newhouse, 1983).
    3) Progressive restrictive pleural fibrosis in a small proportion of patients can cause severe dyspnea, decreased vital capacity, total lung capacity, residual volume, and diffusing capacity, with eventual ventilatory failure and death (Miller et al, 1983; Mossman & Gee, 1989).
    4) Asbestosis patients may also present with superimposed infections because of increased susceptibility caused by immunologic derangements (ATSDR, 1990).
    5) CLINICAL PREDICTORS OF OUTCOME: In a review of 74 cases of asbestos deaths, the 10 year risk of death was increased in the presence of increasing interstitial fibrosis as seen on baseline chest x-ray, dyspnea, low forced vital capacity, and clinical symptoms of interstitial fibrosis (rales, clubbing and cyanosis) (Markowitz et al, 1997).
    B) PLEURAL PLAQUE
    1) WITH POISONING/EXPOSURE
    a) DEFINITION: Pleural plaques are focal, irregular thickenings composed of dense bands of avascular collagen occurring predominantly in the submesothelial parietal pleura (Gefter & Conant, 1988).
    b) SITES: Plaques may be bilateral and asymmetrical, and are usually located on the parietal pleura of the thorax, diaphragm, mediastinum, or pericardium (Dark & Pingleton, 1983; Mossman & Gee, 1989). Less often, they may occur on the visceral pleura within the interlobar fissure (Gefter & Conant, 1988).
    c) CAUSES: Although plaques are the most common chest radiographic manifestation of asbestos exposure, no such exposure can be established for 22% of autopsy-proven cases (Gefter & Conant, 1988). While the overall incidence of plaques increases with dose, there is no linear correlation between plaque severity and total dust exposure (Gefter & Conant, 1988).
    d) CLINICAL MANIFESTATIONS: Plaques by themselves are not symptomatic until they become calcified and large enough to restrict chest wall movements and thus affect vital capacity (ATSDR, 1995; (Dark & Pingleton, 1983; Dunn, 1989; Gefter & Conant, 1988; Mossman & Gee, 1989).
    e) MALIGNANCY: Pleural plaques are not lung cancer precursors, although persons with pleural plaques have an increased incidence of lung cancer (ATSDR, 1990; Gefter & Conant, 1988; Mossman & Gee, 1989) and possibly malignant mesothelioma (Bianchi et al, 1997).
    C) PLEURAL EFFUSION
    1) WITH POISONING/EXPOSURE
    a) INCIDENCE of BENIGN ASBESTOS PLEURAL EFFUSIONS: The overall incidence of benign asbestos-related pleural effusions was 3.1%, with a 7% incidence in the heavily exposed group and a 0.2% incidence in the indirectly exposed group in one report (Gefter & Conant, 1988). Of all the asbestos-related diseases, it has the shortest latency period, with detection within the first 10 years after exposure (Dunn, 1989; Gefter & Conant, 1988).
    b) CLINICAL MANIFESTATIONS: Acutely, fever, chest pain, leukocytosis, and an increased erythrocyte sedimentation rate (ESR) may be seen (Dark & Pingleton, 1983; Dunn, 1989).
    1) Chronically, there are few, if any, signs or symptoms (Dunn, 1989).
    2) The effusions are mostly exudative, sterile, and frequently blood-tinged (Dunn, 1989; Gefter & Conant, 1988; ILO, 1983).
    3) Most effusions identified were asymptomatic and small (and often overlooked); as many as 28% may recur (Gefter & Conant, 1988).
    c) DIAGNOSIS: Benign asbestos-related pleural effusion is a diagnosis of exclusion. The differential diagnosis includes mesothelioma, metastatic tumor, tuberculosis, and disease involving the superior vena cava, mediastinal nodes, thoracic duct, or pericardium (Gefter & Conant, 1988).
    d) CLINICAL COURSE: Although termed "benign," asbestos-related effusions may precede the development of mesothelioma in a small number of patients, necessitating long-term follow-up (Gefter & Conant, 1988). Benign pleural effusions may also lead to functional respiratory impairment because of ensuing fibrosis and pleural thickening (Gefter & Conant, 1988).
    D) THICKENING OF PLEURA
    1) WITH POISONING/EXPOSURE
    a) DEFINITION: Diffuse pleural thickening is a uniform, homogenous, uninterrupted pleural density extending over at least 1/4 of the chest wall with or without accompanying costophrenic angle obliteration (Gefter & Conant, 1988).
    b) CAUSES: In a series of 1,373 asbestos-exposed workers, 31.4% of the cases were related to asbestos exposure, 25.4% to confluent plaques, 33% to malignant effusion, trauma, infection, or a combination of these, and 10.3% were presumed extensions of parenchymal fibrosis (McLoud et al, 1985).
    c) CLINICAL COURSE: Diffuse pleural thickening may develop as an acute, rapidly progressive process associated with chest pain, or it may assume an indolent, asymptomatic course (Gefter & Conant, 1988). Chronic cases may present with significant pulmonary insufficiency and may require surgical decortication (Gefter & Conant, 1988). Patients presenting with stable pleural plagues are at risk for diffuse pleural thickening and subsequent greater ventilatory impairment (Miller & Miller, 1993).
    E) TOBACCO USE AND EXPOSURE - FINDING
    1) WITH POISONING/EXPOSURE
    a) SMOKING: An apparent synergism exists between asbestos-related pulmonary diseases and smoking. The mechanism for this has yet to be established, although several theories have been postulated and tested (Blanc et al, 1988; deShazo et al, 1988; Hobson et al, 1988; Kronenberg, 1989; Mossman & Gee, 1989; Talcott & Antman, 1988) ATSDR, 1995).
    1) Those who are occupationally exposed to asbestos and who smoke have a 5 to 6 times greater than expected incidence of pleural plaques on chest x-ray in later years (Hillerdal et al, 1983).
    2) CASE SERIES: A retrospective review of shipyard workers found cigarette smoking-asbestos exposure interactions for parenchymal opacities, but not for decreased lung capacity (Blanc et al, 1988). The ILO-interpreted opacities may reflect smoking-associated parenchymal changes among asbestos-exposed smokers.
    3) Smoking and asbestos exposure were shown to interact and thus decrease mononuclear cell natural killer function (deShazo et al, 1988).
    4) Smoke-exposed cultures of tracheal implants from rats had a greater number of asbestos fibers in the epithelium and greater proliferative activity, compared to cultures unexposed to cigarette smoke (Hobson et al, 1988).
    5) Smoking may impair the lung's ability to clear asbestos fibers and thus enhance asbestos-induced fibrogenesis (Mossman & Gee, 1989).
    6) Lung macrophages, in response to foreign bodies such as asbestos fibers, may release enzymes and oxidants and thus destroy normal lung tissue in the same way that they would react to cigarette smoke (Kronenberg, 1989).
    F) SPUTUM ABNORMAL - AMOUNT
    1) WITH POISONING/EXPOSURE
    a) FERRUGINOUS BODIES have been found in the sputum of asbestos workers (Stewart & Haddow, 1929).
    1) McLarty et al (1980) demonstrated a significant association between ferruginous (chalybeate) bodies found in the sputum and radiographic findings of interstitial pulmonary disease, pleural fibrosis, and spirometric abnormalities (McLarty et al, 1980).
    2) Increased age and smoking were also related to an increased number of ferruginous bodies (McLarty et al, 1980).
    3) Although hemolytic activity has been said to be a factor influencing pathogenesis, there have been few attempts to correlate hemolytic activity with ferruginous bodies (Ayer et al, 1972).
    4) While they are probably formed as a protective mechanism, ferruginous bodies are not biologically inert. Included iron can induce DNA damage and may play a role in formation of hydroxyl radicals and lipid peroxidation (Lund et al, 1994).
    G) ASBESTOSIS
    1) WITH POISONING/EXPOSURE
    a) Asbestos, as a component of industrial dust, may also produce chronic obstructive airways disease, but further study is required to confirm and understand this relationship (Zejda, 1996).
    H) MALIGNANT TUMOR OF LUNG
    1) WITH POISONING/EXPOSURE
    a) RISK FACTOR: Asbestosis patients with progression of small opacities on chest x-ray over several years are at higher risk of developing lung cancer (Oksa et al, 1998). Although smoking history is also a factor in lung cancer, progression of pulmonary fibrosis may be an independent risk factor.

Genitourinary

    3.10.2) CLINICAL EFFECTS
    A) ACUTE RENAL FAILURE SYNDROME
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Acute renal failure has been reported secondary to retroperitoneal fibrosis which developed in a man with diffuse asbestos-related pleural fibrosis (Maguire et al, 1991).
    B) RETROPERITONEAL FIBROSIS
    1) WITH POISONING/EXPOSURE
    a) In a case-control study of 43 patients with retroperitoneal fibrosis, the disease was highly associated with occupational asbestos exposure. The age-standardized incidence was 0.10 per 100,000 person-years (Uibu et al, 2003).

Hematologic

    3.13.2) CLINICAL EFFECTS
    A) ACUTE LEUKEMIA
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Two men who worked in a shipyard for 40 years were diagnosed with acute myelocytic leukemia (Kishimoto et al, 1988).
    1) The concentrations of asbestos bodies in their lungs were comparable to those in a control group of 10 patients with lung cancer and similar occupational histories.
    2) Both patients, but none of the controls, had asbestos bodies in the bone marrow.

Dermatologic

    3.14.2) CLINICAL EFFECTS
    A) MALIGNANT NEOPLASM OF SKIN
    1) WITH POISONING/EXPOSURE
    a) ASBESTOS CORNS: Warts or areas of thickened skin surrounding implanted asbestos fibers do NOT lead to skin tumors and disappear on removal of the fibers (ILO, 1983).

Immunologic

    3.19.2) CLINICAL EFFECTS
    A) DISORDER OF IMMUNE FUNCTION
    1) WITH POISONING/EXPOSURE
    a) COMPLEMENT ACTIVATION: Asbestos activates complement by an alternative pathway, resulting in leukocyte concentration and lysosomal enzyme release (Dark & Pingleton, 1983).
    1) With activation of the alternative complement pathway, C5a cleavage product is generated, which serves as a chemotactic agent for alveolar macrophages (Kagan, 1988).
    b) CELLULAR/HUMORAL IMMUNOLOGIC CHANGES: Reports of serum abnormalities have not been consistent (Nash et al, 1981). Despite some variability, most studies indicate that cell-mediated immunity can be depressed (ATSDR, 1995; (Weill & Hughes, 1988). Asbestos, especially chrysotile, can suppress natural killer cell activity and thus interfere with the recognition and destruction of malignant cells (Robinson, 1989).
    1) Other studies have reported increased cellular immune responses (Anton-Culver et al, 1988; Delclos et al, 1989).
    2) Elevated bronchoalveolar T4/T8 lymphocyte ratios were noted in 32 subjects with significant asbestos exposure (Delclos et al, 1989).
    3) Shipyard workers with radiographically detectable asbestosis had greater numbers of T helper and T suppressor cells (disproportionately more of the latter) compared to blood donor controls (Anton-Culver et al, 1988). Increased pokeweed mitogen stimulation was also noted.
    4) Differences in humoral immune response have also been reported (Anton-Culver et al, 1988) ATSDR, 1995; (Talcott & Antman, 1988; Weill & Hughes, 1988).
    5) Elevated carcinoembryonic antigen levels have been identified with colorectal cancers, but the clinical relevance of elevated immunoglobulins and other serum proteins have yet to be determined (Talcott & Antman, 1988).
    6) Autoantibodies (rheumatoid factor, antinuclear antibodies) are typically abnormally high in asbestos-exposed workers (ATSDR, 1995; (Weill & Hughes, 1988). Caplan's syndrome (pneumoconioses with rheumatoid changes) has been noted in asbestos workers which can lead to rheumatoid arthritis (ATSDR, 1995). In a retrospective study of 109 environmentally-exposed persons, those with pleural plaques had an increased incidence of antinuclear antibodies, as well as increased IgA levels (Zerva et al, 1989).
    7) Increased levels of anti-double strand DNA antibodies were seen in persons occupationally exposed to asbestos, compared with a non-exposed group (Marczynski et al, 1994).
    8) Higher IgG and IgA levels were noted among shipyard workers with radiographically detected asbestosis (Anton-Culver et al, 1988). Higher IgG and IgA levels were also noted in environmental (nonoccupational) asbestos exposures. The pressure of pleural plaques accentuated the effect on humoral immunity (Zerva et al, 1989).
    B) INFECTIOUS DISEASE
    1) WITH POISONING/EXPOSURE
    a) PREDISPOSITION TO INFECTION: Bronchiectasis and unexplained (but commonly encountered) immunologic deficiencies can predispose an asbestotic patient to infections, including tuberculosis (Baris et al, 1988; (Finkel, 1983). Infection can cause further progressive fibrosis, which leads to cor pulmonale.

Reproductive

    3.20.1) SUMMARY
    A) Transplacental transfer of asbestos may occur, but this has not been linked with any adverse reproductive outcomes in humans.
    3.20.2) TERATOGENICITY
    A) LACK OF EFFECT
    1) ANIMAL STUDIES
    a) When administered in the drinking water, asbestos had no effect on embryo survival and was not teratogenic in rats (Schneider & Mauere, 1977). It has been reported to affect embryonic development in mice (Valerio, 1980). Chrysotile asbestos was not teratogenic in mice at an oral dose of 143 mcg (Shepards, 2001; (Schardein, 1993).
    3.20.3) EFFECTS IN PREGNANCY
    A) HUMANS
    1) PLACENTAL BARRIER
    a) Uncoated chrysotile asbestos fibers were found in lung, liver, and/or placenta digests of 5 stillborn infants, suggesting transplacental transfer of asbestos (Haque et al, 1992).
    b) Asbestos is believed to cross the mammalian placental barrier (HSDB , 2001; Lemesch, 1980).
    c) Uncoated chrysotile asbestos fibers were found in lung, liver, and/or placenta digests of 5 stillborn infants, indicating transplacental transfer (Haque et al, 1992).
    d) Asbestos fibers were found in tissues of stillborn infants at higher frequencies and concentrations than for normal deliveries. Maximum concentrations were seen in lungs, then in liver and placenta. Although placentas from stillbirths averaged 164,500 fibers/g (n = 4), no asbestos fibers were seen in the placentas from normal births. Presence of asbestos fibers was strongly correlated with working status of the mothers (Haque et al, 1996).
    B) ANIMAL STUDIES
    1) Asbestos can cross the placenta to the fetuses in rats following maternal intravenous injection (Cunningham & Ponternet, 1974).
    2) Blastocyst exposure to asbestos did not result in decreased postimplantation survival (Shepards, 2001).

Carcinogenicity

    3.21.1) IARC CATEGORY
    A) IARC Carcinogenicity Ratings for CAS12172-73-5 (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):
    1) Not Listed
    B) IARC Carcinogenicity Ratings for CAS14567-73-8 (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):
    1) Not Listed
    C) IARC Carcinogenicity Ratings for CAS12001-28-4 (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):
    1) Not Listed
    D) IARC Carcinogenicity Ratings for CAS17068-78-9 (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):
    1) Not Listed
    E) IARC Carcinogenicity Ratings for CAS13768-00-8 (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):
    1) Not Listed
    F) IARC Carcinogenicity Ratings for CAS1332-21-4 (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):
    1) IARC Classification
    a) Listed as: Asbestos
    b) Carcinogen Rating: 1
    1) The agent (mixture) is carcinogenic to humans. The exposure circumstance entails exposures that are carcinogenic to humans. This category is used when there is sufficient evidence of carcinogenicity in humans. Exceptionally, an agent (mixture) may be placed in this category when evidence of carcinogenicity in humans is less than sufficient but there is sufficient evidence of carcinogenicity in experimental animals and strong evidence in exposed humans that the agent (mixture) acts through a relevant mechanism of carcinogenicity.
    G) IARC Carcinogenicity Ratings for CAS12001-29-5 (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):
    1) Not Listed
    3.21.2) SUMMARY/HUMAN
    A) Asbestos is a human carcinogen. The primary types of asbestos-related cancers are mesothelioma of the pleura and peritoneum and bronchogenic carcinoma.
    B) An increasing number of reports are suggesting an association between asbestosis and gastrointestinal, renal, or laryngeal malignancies; these reports have been refuted by others.
    3.21.3) HUMAN STUDIES
    A) CARCINOMA
    1) The ACGIH considers all forms of asbestos confirmed human carcinogens (Group A1) (ACGIH, 2003).
    a) TYPES: Primary types of asbestos-related malignancies are bronchial carcinoma and mesothelioma of the pleura and peritoneum (Dunn, 1989; Talcott & Antman, 1988; ATSDR , 2001; Crosignani et al, 1995). There is considerable literature on the relationship between occupational exposure to asbestos and risk for cancer, including mesothelioma (cancer of the lining of the pleural cavity or peritoneum) and lung, laryngeal, ovarian and gastrointestinal cancers (Wu et al, 2015; Swiatkowska et al, 2015; Dunn, 1989; Talcott & Antman, 1988; (IARC, 1987); Sittig, 1991).
    b) A positive link between asbestos exposure and mesothelioma has been established both epidemiologically and experimentally.
    2) Epidemiologic data have conflicting estimates of risk among asbestos workers for developing gastrointestinal cancer and cancers of the larynx, esophagus, pancreas, kidneys, and ovaries (Wolff et al, 2015; Albin et al, 1990; ATSDR , 2001; Brown et al, 1988; Dark & Pingleton, 1983; Edelman, 1988; Finkelstein, 1989; Frumkin & Berlin, 1988; McLure & Poole, 1990; Mollo et al, 1990; Mossman & Gee, 1989; Neuberger & Kundi, 1990; Parnes, 1990; Raffn et al, 1989; Sebastien et al, 1989; Sluis-Cremer & Bezuidenhout, 1989; Smith, 1990; Smith et al, 1989; Talcott et al, 1989; Weiss, 1990; Demers et al, 1994; Kraus et al, 1995).
    3) All forms of asbestos have been linked with cancer in humans, but some forms are more potent than others for inducing cancer (ACGIH, 2001a). Crocidolite seems to be the most potent form of asbestos for inducing tumors, followed by amosite and finally chrysotile (ACGIH, 2001a). Ex-workers with a history of crocidolite exposure had an increased lung cancer risk, with squamous cell carcinoma being greater than adenocarcinoma (de Klerk et al, 1996).
    4) Although chrysotile is 2 to 4 times less active than crocidolite in causing mesothelioma, it is of comparable potency in inducing lung cancer (Stayner et al, 1997; Landrigan et al, 1999).
    5) A critical analysis of published studies has concluded that chrysotile is similar in potency to amphibole forms of asbestos for inducing malignant pleural mesothelioma (Smith & Wright, 1996). The "amphibole hypothesis," which postulates the role of confounding exposure to amphiboles in chrysotile-linked cancers, has less experimental support. Some authors feel that chrysotile should be treated as being "virtually" as carcinogenic as the amphibole forms (Stayner et al, 1996).
    6) An occupational cohort exposed exclusively to amosite had duration-related excess deaths from respiratory cancer and pleural and peritoneal mesothelioma; significant excess deaths were seen even with less than 6 months of employment. This study confirms that amosite is a hazard for these forms of cancer (Levin et al, 1998).
    7) In one ongoing study of persons occupationally exposed to asbestos in a nitric acid plant, cancers that have increased in incidence over time since the first exposure to asbestos are those of the lung, pleura, stomach, unknown origin, and total cancers (Hilt et al, 1991). This same group has been studied for more than 60 years and will continue to be followed indefinitely.
    8) McDonald et al (1999) evaluated chest radiographs of 294 male asbestos mine workers from two mines, one with a high tremolite asbestos concentration and the other with a low tremolite asbestos concentration. From the high tremolite mine, 129 workers were evaluated. The low tremolite mine sample yielded 81 miners and 84 miners had worked in both locations. After adjusting the data for cigarette smoking, age, smoking-age interaction, and cumulative exposure, the authors concluded that amphibole fibers including tremolite were more fibrogenic than chrysotile asbestos (McDonald et al, 1999).
    B) PREDISPOSING FACTORS
    1) CONFOUNDING/SYNERGISTIC FACTORS: The cancer-causing ability of asbestos seems to be related to fiber length, type, size, geometry, and insolubility in aqueous solutions (Brown et al, 1990; Churg et al, 1989; Gibbs, 1990; ILO, 1983; Lippmann, 1988; McDonald et al, 1989; Mossman & Gee, 1989; Sebastien et al, 1989; Spurny et al, 1983; ACGIH, 2001a)
    a) Asbestos fibers in order of toxicity are crocidolite, amosite, and chrysotile.
    1) In a fatality due to widely metastatic malignant mesothelioma, asbestos fibers were extracted from many tissues, including lungs, pleura, pericardium, tunica vaginalis testis, lymph nodes with tumor metastasis, small intestine, liver, spleen and kidney. All tissues examined contained asbestos fibers, with lung parenchyma containing numerous fibers (Watanabe et al, 1994). The precise mechanism of carcinogenesis by asbestos fibers is unclear. The role of pulmonary macrophages has been postulated.
    b) Respirable particles are generally between 0.5 and 5 microns in diameter, with a length-to-width ratio of 3:1. However, in the case of asbestos, some fibers as large as 10 microns in diameter may penetrate to the lower pulmonary regions (ATSDR, 1990).
    1) An increased incidence of lung cancer has been produced by fibers longer than 5 microns (ATSDR , 2001).
    c) Asbestos fibers were found in lymph nodes of 13 of 21 non-occupationally exposed individuals at appreciably higher levels than in the lung. The authors suggested that lymph nodes may be a better indicator of lifetime exposure to asbestos than lung tissue (Dodson et al, 2000).
    d) Following tissue analysis in 20 individuals that died of malignant mesothelioma (17 cases were pleural; 3 were peritoneal), it was found that asbestos fibers could reach the omentum and mesentery. The likelihood of this occurrence could be predicted by the following: heavier inhaled exposures and total amphibole burden tended to favor the migration of amphibole fibers to other extrapulmonary sites. In this study, longer chrysotile fibers were more likely to be present in the extrapulmonary sites (Dodson et al, 2000a).
    2) TRACE METALS: Some authors think that trace metals may contribute to asbestos' cancer-causing abilities. Nickel, cobalt, chromium, manganese, and iron have been found in samples of amosite, crocidolite, and chrysotile (Roy-Chowdhury et al, 1973).
    3) CIGARETTE SMOKING: Generally, lung cancer occurs with heavy asbestos exposure; the incidence is increased among smokers (Swiatkowska et al, 2015; Gefter & Conant, 1988; Mossman & Gee, 1989; Newhouse, 1983; Robinson, 1989). However, the synergistic effect of smoking and asbestos on development of cancers of the stomach, colon-rectum, and kidney has not yet been confirmed (ATSDR, 1990). In addition, the effects of asbestos exposure on the risk of developing mesothelioma does not appear to be increased by smoking (Clayton & Clayton, 1993; ATSDR , 2001).
    a) Smoking may impair the lung's ability to clear asbestos fibers and enhance asbestos-induced fibrogenesis (Mossman & Gee, 1989).
    b) There has been some controversy as to the quantitative effects between asbestos and tobacco smoke in the occurrence of lung cancer. It was hypothesized that embedded asbestos fibers may provide an area for the deposition of carcinogens from tobacco smoke (Clayton & Clayton, 1993).
    c) Although asbestosis and lung cancer are related, the risk for mesothelioma seems to be separate and not related to smoking (ATSDR , 2001; Berry et al, 1985).
    d) Rat studies showed that asbestos potentiates physical transport of adherent molecules (including hydrocarbon carcinogens) into the lung where phagocytosis of asbestos fibers incorporates hydrocarbons into pulmonary macrophages (Talcott & Antman, 1988).
    4) ASBESTOSIS: While individuals with radiographic or clinical evidence of asbestosis probably have, on average, a higher risk of cancer due to heavier exposure to asbestos (Edelman, 1990); asbestosis is not required for increased cancer risk in those with asbestos exposure. Cancer risk is increased even in the absence of overt asbestosis (Finkelstein, 1997; Hillerdal & Henderson, 1997; Egilman & Reinert, 1996).
    C) RISK FACTORS
    1) EVIDENCE OF CAUSATION includes the following:
    a) DOSE-RESPONSE: The chance of developing tumors is dose-related to asbestos exposure, but there is no "critical level" where the risk of cancer is zero (ATSDR, 1990). No known threshold for asbestos induced lung cancer has been established (ATSDR , 2001).
    1) However, a literature review concluded that a threshold for asbestos-induced mesothelioma may exist, based on a background of "spontaneous" and non-asbestos-related cases (Ilgren & Browne, 1991). Another reviewer has stated that the risk of LUNG cancer is higher in persons with asbestosis than in those in whom it is absent (Craighead, 1992).
    2) There was no evidence for a threshold for induction of either lung cancer or asbestosis in a cohort mortality study of South Carolina textile workers. The excess lifetime risk for 45 years of exposure at the current OSHA standard was 5/1000 for lung cancer, and 2/1000 for asbestosis, in this cohort (Stayner et al, 1997). A literature review also found no evidence for a threshold for asbestos-induced mesothelioma (Hillerdal, 1999).
    b) Although mesothelial tumors may have a long latency period of up to 68 years, these may occur with an exposure of less than 1 year (ATSDR, 1990; Mowe et al, 1984; Newhouse, 1983).
    1) A multiplicative relative risk of 1.9 for mesothelioma was estimated for each fiber-year/mL of exposure (Albin et al, 1990).
    2) The rate of mesothelioma continues to rise, with estimated lifetime risks of 1.3% in British persons born between 1893 and 1948, 1% in those born between 1943 and 1948, and 0.6% for those born between 1948 and 1953.
    3) According to one model, deaths from mesothelioma will peak in approximately the year 2020, and may account for 1% of all deaths for men born in the 1940s (Peto et al, 1995).
    4) Mesothelioma is currently occurring in epidemic proportions in Europe. One study estimates the death rate will double by 2018, with approximately 1 in 150 men born between 1945 and 1950 dying of it (Peto et al, 1999).
    2) CONSISTENCY/RISK ESTIMATES includes the following:
    a) Risk estimates for bronchogenic cancer among workers with asbestosis or significant exposure to asbestos have not been consistently high. This variability can be due to methodological differences.
    b) Although persons exposed to asbestos by inhalation have a twofold greater risk of colorectal cancer than unexposed individuals, data were conflicting and insufficient to clearly relate GI tumors or peritoneal mesotheliomas to the direct ingestion of asbestos fibers (Albin et al, 1990; ATSDR, 1990; Edelman, 1988; Weiss, 1990).
    c) A 3.4-fold increase in mortality from malignancy (compared to expected rates) has been noted among workers in a factory where the average asbestos level was 80 particles/mL and where crocidolite-containing cigarette filters were manufactured (Talcott et al, 1989).
    d) In one study of mesothelioma cases among miners and millers, amphibole (crocidolite and amosite), chrysotile, and tremolite were found in lung fibers and at the highest concentrations among workers with mesothelioma (Dufresne et al, 1995).
    e) There is convincing evidence that a relationship exists between pleural malignant mesothelioma and occupational exposure to commercial brands of asbestos. However, many patients with malignant mesothelioma had no previous history of exposure to the fibers. Low-dose asbestos exposure has been related to household and non-occupational (environmental) circumstances. The former consisted of asbestos fibers being brought home by exposed workers in their own clothes, while the latter consisted of exposure that was normally a result of environmental contamination in urban areas near asbestos-producing mines, industries, or factories (living up to 3 miles away from the source may be a risk factor for acquiring asbestosis). Both situations have been responsible for localized outbreaks of pleural mesothelioma, although they are not considered of great relevance in national formal epidemiological studies (Magnani et al, 2000).
    f) With respect to occupations involving exposure to asbestos, British construction workers had the highest death rates from peritoneal cancer (PMR=990), and a relatively low rate (PMR=160) for pleural cancer. Other occupations had higher risks of death from pleural tumors and no excess rates of peritoneal cancer. As a rule, the mortality risk for asbestosis followed that of peritoneal, rather than pleural, cancer (Coggon et al, 1995).
    g) Very brief exposure to asbestos may be sufficient to increase the risk for cancer. Even a single high-level acute exposure might be enough to increase one's risk. IT IS NOT KNOWN IF THERE IS ANY SAFE ASBESTOS EXPOSURE DOSE ((IARC, 1987)), although one survey suggested a threshold of 25 to 100 fibers/cc years for lung cancer (Browne, 1986).
    3) TEMPORALITY is shown as follows:
    a) Reports of asbestosis and colorectal cancer showed temporality but not causality of association (Weiss, 1990).
    4) BIOLOGIC SENSE is shown as follows:
    a) Asbestos fibers have been identified within some human specimens of colorectal adenocarcinomas and in extrapulmonary tissues, including the tonsils, thoracic and abdominal lymph nodes, small intestines, pancreas, kidneys, and bone marrow (ATSDR, 1990; Finkel, 1983; Smith et al, 1989). This establishes only site-specific evidence of exposure, not causation (Weiss, 1990).
    b) Lung cancer patients had significantly higher levels of ferruginous bodies in lung digests than did controls, even though only one cancer patient had any known exposure to asbestos (Warnock & Churg, 1975). This finding suggests that asbestos may be commonly involved in lung cancer.
    c) Animal studies revealed that asbestos fibers can penetrate the GI tract (ATSDR, 1990). Tumorigenesis has also been noted in animal bioassays (Smith et al, 1989).
    5) OZONE effects are shown as follows:
    a) Prolonged exposure to low levels of ozone appears to impair clearance of asbestos from the lungs. In a study of rats exposed to low levels of ozone for 6 weeks and then exposed to aerosolized asbestos fibers for 5 hours, fiber mass and fiber number were significantly greater (P<0.05) than those of a control group of rats exposed only to aerosolized asbestos (Pinkerton et al, 1989).
    D) MESOTHELIOMA
    1) Although asbestos was thought to be the only cause of mesothelioma, a recent reclassification of these tumors has concluded that some cases may be spontaneous or related to non-asbestiform agents (Ilgren & Wagner, 1991). Mesothelioma is a rapidly invasive and fatal malignancy (ATSDR, 1990; Neuberger & Kundi, 1990; Newhouse, 1983; Roggli et al, 1993).
    a) In a Swedish study, mesothelioma was thought to be underreported as an occupational disease (Andersson & Toren, 1995).
    b) A significant increase in the number of mesothelioma cases occurred between 1979 and 1993 in the Cappadocian region of Turkey and are considered closely related to environmental exposure to zeolite (a silicate-containing mineral fiber) (Greim, 1997).
    2) Serum osteopontin levels were used to discriminate between persons with asbestos exposure without early pleural mesothelioma and those with exposure to asbestos with pleural mesothelioma. Serum osteopontin levels were significantly higher in those with pleural mesothelioma than in those without pleural mesothelioma (Pass et al, 2005).
    3) CLINICAL PRESENTATIONS include the following:
    a) A large unilateral pleural effusion is the most frequent presenting manifestation of malignant mesothelioma (Gefter & Conant, 1988). Mesothelioma may occasionally present as a solitary pleural mass.
    b) A characteristic aching, nonpleuritic chest pain may precede the development of any radiographic findings (Gefter & Conant, 1988; Miller, 1990). In a Japanese study of 106 patients with malignant pleural mesothelioma, chest pain was the most common complaint reported (67 cases) (Kishimoto et al, 2004).
    c) A small percentage of patients may present with repeated episodes of benign pleurisy with resolving effusions (Gefter & Conant, 1988).
    d) Abdominal pain, a palpable mass, or increased abdominal girth are the usual presenting symptoms of peritoneal mesothelioma (Talcott & Antman, 1988).
    e) Pericardial effusion and tamponade, brachial plexopathy, Horner's syndrome, dysphagia, and superior vena cava syndrome are less common presentations (Talcott & Antman, 1988).
    4) In a review of 16 malignant mesothelioma patients with a documented history of asbestos exposure, 13 had malignant pleural mesothelioma. Of them, 11 presented with dyspnea and pleural effusion; only 2 reported chest pain. Initial closed pleural biopsies and pleural fluid cytology were negative in all patients who presented with pleural effusion. Diagnosis was confirmed by thoracoscopy.
    a) The 3 remaining patients in this review presented with peritoneal mesothelioma. Two presented with weight loss, abdominal pain, and peritoneal masses on CT. The third patient presented with only ascites. Diagnosis was confirmed by laparotomy in the patients with peritoneal masses and by laparoscopy in the patient with ascites only.
    b) The median time from first exposure to symptoms was 35.5 (range, 16 to 53) years. In this study, the overall prognosis was poor and treatment was palliative in most cases; median survival was 6 months(Chan et al, 2003)
    5) In a Japanese study of 106 patients with malignant pleural mesothelioma, the latent period for the occurrence of mesothelioma was 15 to 72 years (mean; 37.0 +/- 13.3 years). Sixty months was the longest survival period; death occurred within 12 months in 43 cases (72%). Mean survival was 9.2 +/- 11.6 months (Kishimoto et al, 2004).
    6) CLINICAL COURSE: The 1-year survival rate of mesothelioma patients is less than 30%; no efficacious treatment has been identified, although intensive multimodality therapy has been shown to prolong the disease-free interval (ATSDR, 1990; Newhouse, 1983; Talcott & Antman, 1988).
    7) DOSE-RESPONSE RELATIONSHIP: Although there is a correlation between asbestosis and risk of mesothelioma, pleural and peritoneal tumors may occur with exposures of less than a year (ATSDR, 1990; Newhouse, 1983). An increased relative risk of 1.9 was estimated for each fiber-year/mL of exposure (Albin et al, 1990).
    a) A meta-analysis of 69 occupational cohorts concluded that asbestos exposure is linked with mesothelioma deaths in a dose-related manner (Goodman et al, 1999).
    b) A study of residential proximity to asbestos in California reported that the odds of mesothelioma decreased by approximately 6.3% for every 10 km farther the residents lived from the nearest asbestos source (Pan et al, 2005).
    8) SMOKING: Unlike asbestos-related bronchogenic carcinoma, mesothelioma risk does not appear to be influenced by smoking (ATSDR , 2001; Berry et al, 1985; Muscat & Wynder, 1991).
    9) FAMILIAL MESOTHELIOMA: Reports of mesothelioma among family members with no direct occupational exposure to asbestos have been reported and attributed to "bystander" exposure to other family members who have direct asbestos exposure (Langhoff et al, 2014; Huncharek et al, 1989; Li et al, 1989; Giarelli et al, 1997; Schneider et al, 1996; Maltoni et al, 1995; Dodoli et al, 1992; ATSDR , 2001). Others have suggested the role of genetic factors (Hammar et al, 1989).
    a) Domestic exposure from husbands, fathers, or sons who had direct contact with asbestos was reported in 11 out of 24 women diagnosed with mesothelioma. The epitheloid subtype of mesothelioma was reported in 18 of 24 women followed by biphasic (3 of 24) and sarcomatoid (2 of 24) subtypes (Langhoff et al, 2014).
    b) Two genotypes have been identified with increased risk of mesothelioma: GSTM null and NAT2 (slow acetylator). Each confers a 2-fold increased risk, and individuals with both genotypes have a 4-fold higher risk; when combined with asbestos exposure, this risk increases to 7-fold compared to those with "beneficial" genotypes GSTM1 and NAT2 (fast acetylator) (Hirvonen et al, 1995).
    10) COMMUNITY-ACQUIRED EXPOSURE: Numerous reports and case series have been published that document an increased risk of mesothelioma in non-asbestos workers in various locations where local asbestos industries exist (Berry, 1997; Magnani et al, 1997; Rogers & Nevill, 1995). Local asbestos-bearing deposits also appear to increase risk (Selcuk et al, 1992). In some cases, local asbestos containing minerals are used to produce whitewash (Sakellariou et al, 1996; Constantopoulos et al, 1991).
    a) Non-occupational exposure to asbestos has been associated with diffuse malignant pleural mesothelioma in persons living in areas with high environmental asbestos levels. In this study, the latent time for the development of mesothelioma was longer than with occupational exposure and independent of exposure duration (Metintas et al, 1999).
    b) A few cases of mesothelioma have been reported in persons who washed asbestos-contaminated clothes. In one study, 13 of 262 total cases of pleural mesothelioma were thought to be due to such exposure (Dodoli et al, 1992). In another study, five fatal cases of mesothelioma were seen in the wives of asbestos-exposed workers who cleaned their husbands' contaminated clothes and shoes (Schneider et al, 1996).
    11) OCCUPATION/INDUSTRY: Proportionate mortality ratios (PMRs) adjusted for age, sex, and race for malignant mesothelioma by occupation were 4.76 for plumbers, pipefitters and steam fitters and 3.04 for mechanical engineers. PMRs calculated for industries were 5.95 for ship and boat building and repair, 4.81 for industrial a miscellaneous chemicals, 3.80 for petroleum refining, and 3.08 for electric light and power. This ratios were calculated using the data from the National Center for Health Statistics multiple-cause-of-death data files, 1999 to 2001 for US residents greater than 15 years of age (Bang et al, 2006).
    a) Three cases of mesothelioma were reported in which exposure to asbestos was from drywall joint compound. In 2 of the cases, the men worked directly with drywall products in previous occupations. Patient 1 worked as an assembler and installer of kitchen cabinets for 2 years starting in 1968, when he applied and sanded joint compound as part of the installation of new cabinets. Later, in the 1970s, he worked with joint compound remodeling homes, which included mixing, applying, sanding, and sweeping of joint compound for approximately 5 years at 3 to 5 days/week. He never wore a mask or respirator. Approximately 30 years later, the man developed a benign pleural effusion. The following year, at age 75 years, he was diagnosed with mesothelioma after tissue was obtained from a thorascopic procedure. Special stains were positive for calretinin, CK7, and EMA but negative for CEA, CK20, and TTF1. He died shortly after refusing chemotherapy. Patient 2 was a maintenance worker at various apartment complexes for approximately 20 years from the 1950s until the 1970s, during which time he frequently worked with several drywall products. Not only did he demolish and replace drywall, he performed minor plumbing and electrical repairs. His use of and exposure to joint compound occurred in visibly dusty conditions, in which he sanded, mixed, and swept joint compound. In 1999, the man presented with a recurrent pleural effusion, shortness of breath, right-sided chest pain, and weight loss.In 2001, at age 75 years, he was diagnosed with mesothelioma. The calretinin and keratin 5/6 stains were positive, while the CEA and Leu MJ stains were negative. While the time from first presentation of the pleural effusion to diagnosis was 2 years, he died soon after being diagnosed and declining all therapy. Patient 3 experienced domestic exposure to asbestos from birth through most of his childhood years. His father worked in construction from 1968 to 1974, during which time he frequently used joint compound. Specifically, the father sanded the joint compound, creating a visible dust that settled on his clothes and skin that came home with him. The father also started making home renovations using joint compound when the patient was approximately 6 years old. Approximately 25 years later, he presented with chest pain and shortness of breath. A pleural effusion was revealed by imaging studies and a diagnosis of epithelioid mesothelioma (with a few spindle cells) was made following a biopsy at age 32 years. Stains were positive for calretinin and keratin AE1/AE3 but negative for CEA. The patient was treated with chemotherapy and debulking surgery; however, the tumor was very aggressive and he died. Asbestosis was not observed in these cases; no autopsies were performed. These cases highlight the need to obtain a complete history of exposure to asbestos-containing products, including joint compound used in the 1950s through the 1970s (Dahlgren & Peckham, 2012).
    12) FIBER TYPE effects include the following:
    a) A retrospective study of 94 asbestos-related mesotheliomas found amosite asbestos in 81% of the cases. Amosite fibers accounted for 58% of all fibers 5 mcm or greater in length. Tremolite/actinolite/anthophyllite were found in 55% of all cases; chrysotile was found in 21% of all cases; and crocidolite was found in 16% of all cases. This suggests that crocidolite asbestos may not be responsible for most mesotheliomas in the USA (Roggli et al, 1993).
    b) A case-referent analysis of asbestos miners from two mining areas in Quebec, Canada, one with high levels of tremolite asbestos and the other with low levels, revealed increased risks of mesothelioma in miners employed at mines producing asbestos with high tremolite concentrations compared to mines with low tremolite concentrations (McDonald et al, 1997).
    E) PULMONARY CARCINOMA
    1) BRONCHOGENIC CARCINOMA is a major cause of death in asbestos-exposed workers (estimated to affect 20 to 25 percent of heavily exposed workers) because of the combined risks of smoking and asbestos (Gefter & Conant, 1988).
    2) The latency period is 15 to 35 years following exposure (Gefter & Conant, 1988). The prevalence is greater in those persons handling finished products than in miners or millers (Dark & Pingleton, 1983).
    3) Adenocarcinomas are most frequently seen (ATSDR, 1990; Dark & Pingleton, 1983; Gefter & Conant, 1988; Mollo et al, 1990; Talcott et al, 1989). Other tumors were characterized as adenomas and squamous cell carcinomas(ATSDR , 2001). The 1999 World Health Organization classification also lists sarcomatoid and adenosquamous carcinoma among the types of cancers associated with asbestos exposure (Wolff et al, 2015).
    4) There are no diagnostic clinical or radiographic features to indicate that a given lung cancer has been caused by asbestos (Gefter & Conant, 1988). However, most asbestos-related tumors are peripheral lower-lobe lesions (Gefter & Conant, 1988; Karjalainen et al, 1993).
    5) Risk estimates for bronchogenic cancer among workers with asbestosis or significant exposure to asbestos have not been consistently high. This variability can be due to methodological differences or individual differences in susceptibility.
    a) A case-control study conducted in 8 Canadian provinces from 1994 to 1997 showed that occupational exposure to asbestos is associated with an increased risk of lung cancer. In this study, 1681 cases of lung cancer and 2053 controls were identified. Compared with those who were not exposed, workers who were ever exposed to asbestos had a 28% increased risk of lung cancer (odds ratio [OR], 1.28). A 2-fold increase in lung cancer risk occurred in those who had ever been exposed to medium or high levels of asbestos (OR, 2.16) compared with those who were exposed to low concentrations (OR, 1.17) or those unexposed. Duration of exposure to asbestos was found to be unrelated to lung cancer risk. The interaction between smoking and asbestos was multiplicative, with those who had 40 or more pack-years of smoking and were exposed to medium or high asbestos levels having the highest risk of lung cancer, nearly 38-fold higher (OR, 38.59) than those with less than 10 pack-years and no asbestos exposure. The calculated value of the synergy index was 2.1 and the multiplicativity index was 0.99 (Villeneuve et al, 2012).
    b) A case-control study of 175 lung cancer patients and 176 controls showed a strong and significant association between asbestos exposure and small cell carcinoma (Relative Risk = 3) and a weaker, but equally significant, association with adenocarcinoma (RR = 2.2) (Kjuus et al, 1986).
    c) Although an increased mortality and morbidity from respiratory cancer was noted in a cohort of asbestos cement workers compared to unexposed industrial workers, the overall risk for respiratory cancer (excluding mesothelioma) was not increased compared to the general population (Albin et al, 1990).
    d) Deaths from lung cancer in asbestos cement workers were not significantly different after adjustments for age and smoking (standardized mortality ratio decreased from 1.7 to 1.04) (Neuberger & Kundi, 1990).
    e) Necropsy studies of 339 amphibole asbestos miners stressed the significant association between asbestosis (and not merely asbestos exposure) and bronchial cancer (Sluis-Cremer & Bezuidenhout, 1989).
    f) The risk for lung cancer was higher in persons with radiologic evidence of pulmonary fibrosis, but the risk was also elevated in persons with asbestos exposure and no fibrosis (Wilkinson et al, 1995).
    g) A case control study failed to confirm asbestos exposure, but concluded that there was no association between lung cancer and the duration of employment in automotive parts factories (Finkelstein, 1989).
    h) Excess risk for cancer of the lung (Relative Risk = 1.8; 95% Confidence Interval = 1.54 to 2.1), pleura (RR = 5.46, 95%; CI = 2.62 to 10.05), and mediastinum (RR = 5; 95% CI = 1.01 to 14.61) were found in a cohort study of 7,996 men and 584 women employed in the Danish asbestos cement industry where fiber levels were more than 0.5 to 2 fiber/mL (Raffn et al, 1989).
    i) Danish men employed in the asbestos cement industry have been reported to be at increased risk for lung cancer. In one study, all Danish men with lung cancer from 1943 to 1984 were included, and cancers were stratified according to type. An increase in lung cancer incidence was confirmed, with the highest relative risk being for adenocarcinoma (3.31-fold). Risk was correlated with duration of employment and time since first employment (Raffn et al, 1993).
    j) In studies of Finnish cancer patients, lung fiber concentrations of greater than one million per gram of dry tissue were associated with an increased risk for mesothelioma (Tuomi et al, 1991).
    k) In a histological study of 414 consecutive cases of lung carcinoma, approximately 60% of the male cases could be attributed to asbestos (Bianchi et al, 1999).
    l) Until 1954, most of the world’s chrysotile asbestos production came from 2 mining areas in Quebec, Canada. Non-occupational exposure to chrysotile asbestos and lung cancer risk in women in these two regions compared to 60 control regions was investigated. The number of deaths in women aged 30 or greater between 1970 and 1989 was used to derive age-standardized mortality ratios. An expert panel estimated past asbestos exposure in the asbestos manufacturing regions and the control areas. No excess risk of death from lung cancer from non-occupational asbestos exposure was found. A data analysis compared the observed relative risk of death to the EPA’s asbestos risk assessment model. The EPA model was shown to overestimate the risk of asbestos-induced lung cancer by at least a factor of 10 (Camus et al, 1998).
    1) A case-referent analysis of asbestos miners from two mining areas in Quebec, Canada, one producing asbestos with high levels of tremolite and the other with low levels, revealed an increased risk of carcinogenicity risk in the miners exposed to high concentrations of tremolite asbestos (McDonald & McDonald, 1997).
    F) LARYNGEAL CARCINOMA
    1) Risk estimates for laryngeal cancer among workers with asbestosis or significant exposure to asbestos have not been consistently high. This variability could be due to methodological differences, or to differences in individual susceptibility.
    a) Under the condition of asbestos exposure with a relative risk (RR) of 2 for lung cancer, the estimated RR is 1.6 for laryngeal cancer with an estimated attributable fraction of approximately 37% for asbestos causation in the exposed population. Therefore, asbestos exposure should be considered a cause of laryngeal cancer in humans (Wolff et al, 2015).
    b) A matched case-control interview study that corrected for potential confounding by cigarette smoking and alcohol consumption showed a nonsignificant but elevated risk (RR = 1.46) for laryngeal carcinoma among those with occupational asbestos exposure (i.e., boilermakers, sheetmetal workers, pipefitters/plumbers, and carpenters) (Brown et al, 1988).
    c) A case control study failed to confirm asbestos exposure but concluded that there was no association between laryngeal cancer and employment duration in automotive parts factories (Finkelstein, 1989).
    d) The cross-sectional and longitudinal data derived from personnel in a brake manufacturing plant did not support asbestos as an etiologic factor for laryngeal cancer, but an irritant effect of asbestos was suggested (Parnes, 1990).
    e) An excess risk of laryngeal cancer (RR = 5.5) was found among a group of workers first employed in the Danish asbestos cement industry where fiber levels were more than 0.5 to 2 fiber/mL from 1928 to 1940 (Raffn et al, 1989).
    f) After correcting for smoking and alcohol consumption, workers heavily exposed to asbestos (with lung cancer RR estimates of 4.06 and 3.28) also had high relative risk estimates for laryngeal cancer (RR = 1.91 and RR = 3.75, respectively) (Smith, 1990).
    g) A case-control study was conducted to confirm an association between occupational exposure to asbestos and the risk of developing laryngeal cancer. The study involved 73 cases and 158 controls who reported asbestos exposure, either via job-specific questionnaires or a substance checklist. After adjusting for smoking and alcohol consumption, the odds ratio for laryngeal cancer was 1.2, suggesting there might be a slightly elevated risk of laryngeal cancer in workers with occupational exposure to asbestos, although the results were not statistically significant (Ramroth et al, 2011).
    2) No clear dose-response relationship with laryngeal cancer was noted when asbestos exposure in the Texas Gulf Coast was analyzed by exposure duration, but a positive gradient was found when asbestos was categorized by exposure intensity (Brown et al, 1988).
    3) A meta-analysis of 69 occupational cohorts concluded that asbestos exposure is linked with mesothelioma deaths in a dose-related manner and suggested an association with laryngeal carcinoma (Goodman et al, 1999).
    G) GASTROINTESTINAL CARCINOMAS
    1) Risk estimates for gastrointestinal cancer among workers with asbestosis or significant asbestos exposure have not been consistently high but have been much lower than those reported for lung cancer and mesothelioma (Talcott & Antman, 1988). This variability can be due to methodological differences or different individual susceptibilities.
    a) A review of published studies on independent cohorts of asbestos workers showed no consistently higher standardized mortality ratios (SMRs) among exposed compared to unexposed populations and no apparent dose-response relationship (Edelman, 1988).
    b) A meta-analysis and review of published cohort data stratified cohorts by dose and showed that significant asbestos exposure (as indicated by a lung cancer SMRof at least 200) is associated with an elevated gastrointestinal cancer SMR (Frumkin & Berlin, 1988).
    c) A case control study did not confirm asbestos exposure but concluded that there was no association between gastrointestinal cancer and duration of employment in automotive parts factories (Finkelstein, 1989).
    d) Excess risk for gastric cancer (relative risk = 1.43) was found in a cohort study of 7996 men and 584 women employed in the Danish asbestos cement industry, where fiber levels were more than 0.5 to 2 fibers/mL (Raffn et al, 1989).
    e) No overall excess risk from cancer of the upper and lower gastrointestinal tract was found in a cohort of asbestos cement workers compared to a local reference cohort of unexposed industrial workers (Albin et al, 1990). Another case-control study also failed to find an association between colon cancer and asbestos exposure (Garabrant et al, 1992).
    f) Norwegian lighthouse keepers, who consumed cistern drinking water contaminated with asbestos from runoff from asbestos-cement roof tiles for 2 decades, had an excess risk of stomach cancer but not malignant mesothelioma (Andersen et al, 1993).
    g) Colorectal cancer occurred with an estimated increase of 1.6% in the incidence density ratio for each fiber-year/mL of asbestos exposure, but no relationship was found between development of colorectal cancer and exposure duration (Albin et al, 1990). A two-fold increase in colon cancer was related to high-level asbestos exposure in one case-control study (Fredriksson et al, 1989).
    h) A review of published data from 21 cohorts of asbestos-exposed workers found a 0.97 estimate of the summary standardized mortality or morbidity ratio for colorectal cancer and no dose-response relationship between asbestos exposure and colorectal cancer (Weiss, 1990).
    i) Pooled standardized mortality ratio data for stomach cancer among asbestos-exposed men revealed a significantly increased risk of stomach cancer in men exposed to crocidolite or mixed asbestos. Pooled estimates were also significant for mortality. Working in the mining industry appeared to increase the risk of stomach cancer due to asbestos exposure, and a long study follow-up revealed a significantly excess risk of stomach cancer (Peng et al, 2015).
    j) Under the condition of asbestos exposure associated with a relative risk (RR) of 2 for lung cancer, the estimated RR for colorectal cancer is 1.1, with the estimated attributable fraction (AF) of 9% for asbestos causation of colorectal cancer in the exposed population, and the estimated RR for stomach cancer is 1.2, with the estimated AF of 17% for asbestos causation of stomach cancer in the exposed population. Thus, the association between asbestos exposure and colorectal cancer is uncertain in humans; the same is true of the association between asbestos exposure and stomach cancer (Wolff et al, 2015).
    2) Reports suggest that ingested asbestos is excreted in the feces and that malignancy could be caused by swallowed asbestos fibers removed from the upper respiratory regions by the ciliary mechanism (ATSDR, 1990).
    3) A meta-analysis of 30 published studies on asbestos and colorectal cancer found an overall relative risk of 0.99, which does not support the idea that asbestos is related to colorectal cancer (Weiss, 1995).
    4) In a large mortality study on 4,943,566 persons, mortality ratios were slightly increased for esophageal, gastric, and colorectal cancer for occupations involving asbestos exposure (Kang et al, 1997).
    5) A slight increase in standard incidence ratio (SIR) for colorectal cancer was found in Danish asbestos cement workers (SIR = 1.23, 95% CI 1.01 - 1.48). The SIR increased to 1.47 with a latency period of 15 years (Raffn et al, 1996).
    6) A study of 3897 participants occupationally exposed to asbestos reported a relative risk for colorectal cancer of 1.54 among those with asbestos-induced pleural plaques at baseline with the risk increasing with worsening pulmonary asbestosis (Aliyu et al, 2005).
    H) RENAL CARCINOMA
    1) GENITAL CANCER: Excess risk for cancer of male genital organs (relative risk = 3.03) was as found in a cohort study of 7996 men and 584 women employed in the Danish asbestos cement industry where fiber exposure levels were more than 0.5 to 2 fibers/mL (Raffn et al, 1989).
    2) RENAL CANCER: Excess mortality from kidney cancer among asbestos-exposed workers was noted in a review of occupational cohort studies of insulators (standardized mortality ratio [SMR] = 2.22), asbestos products company workers (SMR = 2.76), and shipyard workers (SMR = 1.98) (Smith et al, 1989).
    3) Case-control studies with low prevalence of heavy asbestos occupational exposure are unable to provide evidence for or against a possible association between asbestos exposure and kidney cancer (Smith, 1990).
    4) An association between asbestos exposure and renal cell cancer was seen in an international case-control study of 1732 cases (Mandel et al, 1995).
    5) An association between asbestos exposure and bladder cancer was reported in one case-control study (Bravo et al, 1988).
    6) Occupational exposure to asbestos was not a factor in kidney cancer in a meta-analysis of 37 cohorts (Sali & Boffetta, 2000).
    I) RETROPERITONEAL FIBROSIS
    1) There is a limited body of literature to suggest that retroperitoneal fibrosis, a rare disease consisting of the proliferation of fibrous tissue in the retroperitoneal cavity, can be caused by asbestos exposure (Wolff et al, 2015).
    J) OVARIAN CARCINOMA
    1) Under the condition of asbestos exposure with a relative risk (RR) of 2 for lung cancer, the estimated RR is 2.2 for ovarian cancer with an estimated attributable fraction of approximately 54% for asbestos causation in the exposed population. Therefore, asbestos exposure should be considered a cause of ovarian cancer in humans (Wolff et al, 2015).
    2) There appears to be evidence that exposure to asbestos increases the risk of developing ovarian cancer (Heller et al, 1999).
    3) Excess ovarian cancer was found among female asbestos workers (HSDB , 2001).
    4) Asbestos can be transferred to the ovary. Asbestos fibers were found at significant levels in the ovarian tissue of 13 women with household exposure. Counts were as high as greater than 1 million/g wet weight in exposed women. These findings are consistent with reports linking asbestos with ovarian cancer (Heller et al, 1996). Asbestos was one of the risk factors found for ovarian cancer in a study of 892,591 Finnish women (Vasama-Neuvonen et al, 1999).
    K) LYMPHOMA-LIKE DISORDER
    1) Increased risk for non-Hodgkin's lymphoma has been associated with asbestos exposure (Ross et al, 1982), but this finding was not replicated in a subsequent report (Olsson & Brandt, 1983).
    2) A more recent ecologic study found no correlation between occupational exposure to asbestos and the incidence of non-Hodgkin lymphoma of the gastrointestinal tract (Treggiari & Weiss, 2004).
    L) LEUKEMIA LYMPHOCYTIC
    1) B-CELL CANCERS: A modest dose-related increase in chronic lymphocytic leukemia, but not multiple myeloma, was seen in one case-control study (Schwartz et al, 1988). Another study confirmed the lack of an association between asbestos exposure and multiple myeloma (Boffetta et al, 1989).
    M) TESTICULAR CARCINOMA
    1) There is also a rare association between asbestos exposure and testicular cancer (Fligiel & Kaneko, 1976).
    3.21.4) ANIMAL STUDIES
    A) PULMONARY CARCINOMA
    1) Pulverized asbestos pipe-covering dust induced pulmonary carcinomas in rats exposed to 85 mg/m(3) for 6 hours/day, 5 days per week for 7 months, followed by a lifetime period of observation (Leong et al, 1978).
    B) MESOTHELIOMA
    1) A single injection of each of the following kinds of fibers was sufficient to induce mesothelioma in hamsters: soft chrysotile, harsh chrysotile, amosite, diatomaceous earth, crocidolite, and anthophyllite (p 26).
    C) LACK OF EFFECT
    1) Asbestos was not carcinogenic by the oral route in hamsters (NTP, 1990).
    2) Chrysotile asbestos was not carcinogenic in Wistar Han rats when given in the diet at daily doses up to 360 mg for 24 months (Truhaut & Chouroulinkov, 1989).

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) Monitor chest CT scan, chest x-ray, and pulmonary function tests in asbestos-exposed patients.
    B) Open lung biopsy is the only definitive diagnostic test for asbestosis.
    C) Bronchoalveolar lavage (BAL) has been recommended as an adjunct in the diagnosis of asbestos-related pulmonary diseases.
    D) OSHA has specific clinical monitoring requirements for workers exposed to asbestos.
    4.1.2) SERUM/BLOOD
    A) BLOOD/SERUM CHEMISTRY
    1) SERUM PEPTIDE LEVELS: Serum type III procollagen peptide (PIIIP; a lung structural protein precursor) concentrations were shown to be significantly higher among 36 asbestos-exposed workers, compared to 13 healthy controls; the levels were significantly related to duration of asbestos exposure (Cavalleri et al, 1988). This potential diagnostic tool has yet to be validated.
    4.1.4) OTHER
    A) OTHER
    1) MONITORING
    a) PULMONARY FUNCTION TESTS: After correcting for smoking, age, and other confounders, a restrictive pattern of pulmonary dysfunction with preserved diffusing capacity is expected in patients with asbestosis, unless severity impairs diffusion as well (ATSDR, 1990; Demers et al, 1990; Jones et al, 1988; Kilburn & Warshaw, 1990) 1990a; (Mossman & Gee, 1989; Robins & Green, 1988; Schwartz et al, 1990) 1990a; (Siracusa et al, 1988).
    1) Nonsmoking patients with asbestosis typically have spirometric changes indicative of small airway disease and restrictive defects; smokers with asbestosis may have a combined obstructive/restrictive pattern (ATSDR, 1990; Mossman & Gee, 1989).
    2) Smoking-adjusted forced vital capacity (FVC) and forced expiratory volume at one second (FEV1) decreased with increasing years of work as boilermakers (Demers et al, 1990). These respiratory function changes were also noted among other asbestos exposed workers (Robins & Green, 1988; Siracusa et al, 1988). Cessation of asbestos exposure for about 10 years did not arrest lung function decline (Siracusa et al, 1988).
    3) A study of 120 workers in an asbestos and cement products factory examined the relationship between years at work and asbestos air concentrations. Lung function (VC, FEV1, MEF25-75) deteriorated over time with increasing years of asbestos exposure. A significant association was also shown between decreases in VC and FEV1 and the presence of pleural changes (Petrovic et al, 2004).
    4) Linear multivariate regression analysis which controlled for potential confounders showed that asbestos-induced circumscribed plaques and diffuse pleural thickening were independently associated with decrements in FVC, but not with decrements in the FEV1/FVC ratio (Schwartz et al, 1990).
    5) Of 24 nonsmoking sheet metal workers, all had normal parenchyma on chest x-ray postero-anterior view, 7 had normal pleura, 9 had circumscribed plaques, and 8 had diffuse pleural thickening (Schwartz et al, 1990a). Those with pleural thickening had lower FVC, total lung capacity, and CO-diffusing capacity. Those with plaques had reduced FVC.
    6) Significant pulmonary dysfunction (reduced FEV1, FVC, terminal flow, and increased thoracic gas volume) were associated with pleural asbestos signs (plaques or diffuse pleural thickening) among men who never smoked (Kilburn & Warshaw, 1990) 1990a). Current and ex-smokers had additional dysfunction, even after adjustment for duration of smoking.
    7) Patients with combined obstructive/restrictive patterns should be followed with studies of carbon monoxide diffusion capacity and static lung volumes (ATSDR, 1990).
    2) OTHER
    a) LUNG BIOPSY: Open lung biopsy is the only definitive diagnostic test for asbestosis (ATSDR, 1990).
    1) Pathologic diagnosis requires the presence of diffuse interstitial fibrosis and asbestos bodies in tissue sections (Churg, 1989).
    2) Asbestos bodies identified on a histologic section of a hilar lymph node are generally indicative of a heavy asbestosis lung burden (Roggli & Benning, 1990).
    3) Asbestos fiber counts in lung may also be useful in confirming a diagnosis of asbestosis and appear in some studies to correlate with severity of pulmonary fibrosis (Green et al, 1997) and with other indices of exposure (Karjalainen et al, 1996).
    4) The asbestos lung burden has also been used for confirming asbestos-related mesothelioma (Kishimoto et al, 1989a; Warnock, 1989).
    b) SPUTUM STUDIES: Sputum inspection for asbestos fibers or ferruginous bodies lacks sensitivity and specificity (ATSDR, 1990; McDonald et al, 1992). However, sputum cytology remains a useful diagnostic test for neoplasia and lung cancer (ATSDR, 1990). Election microscopy analysis of sputum may be effectively used to assess exposure to asbestos (Harber & Smitherman, 1991).
    c) BRONCHOALVEOLAR LAVAGE: Bronchoalveolar lavage (BAL) has been recommended as an adjunct in the diagnosis of asbestos-related pulmonary diseases (Barbers & Abraham, 1989; Delclos et al, 1989; Hayes et al, 1989).
    1) Amosite fibers were noted in a sample obtained by bronchoalveolar lavage and analyzed with scanning electron microscopy-energy dispersive x-ray (Barbers & Abraham, 1989), confirming the diagnosis in a 55-year-old man who had typical clinical and radiologic evidence of asbestosis 36 years after exposure for less than a year, but a negative transbronchial lung biopsy.
    2) Bronchoalveolar lavage detected significant increases in neutrophils and T4/T8 ratios among 32 asbestos-exposed males compared to controls (Delclos et al, 1989). Because the simultaneously increased gallium scan activity did not correlate with radiological and functional parameters, BAL and gallium scan may reflect inflammation that is not clinically apparent.
    3) Bronchoalveolar lavage and gallium scans were abnormal in varying proportions of asbestos-exposed workers with definitive, equivocal, and no chest x-ray evidence of pneumoconioses, suggesting a possible role in detecting active subclinical inflammation (Hayes et al, 1989).
    d) OTOLARYNGOLOGIC EXAMINATION: Asbestos workers with hoarseness, pain, or soreness of the throat should be referred for a detailed otolaryngologic examination of the upper respiratory tract looking for the presence of laryngeal cancer (HSDB , 1995).
    e) SERUM OSTEOPONTIN: Serum osteopontin levels were used to discriminate between persons with asbestos exposure without early pleural mesothelioma and those with exposure to asbestos with pleural mesothelioma. Serum osteopontin levels were significantly higher for those with pleural mesothelioma, compared with those without pleural mesothelioma (Pass et al, 2005).
    f) OSHA REQUIREMENTS: OSHA has specific clinical monitoring requirements for workers exposed to asbestos.

Radiographic Studies

    A) CHEST RADIOGRAPH
    1) The sensitivity and specificity of radiographic studies for detection of plaques and asbestos-exposure are varied, because of different radiographic and patient selection criteria. False positive readings (compared to autopsy findings) ranged from 8.4% to 58%, and false negatives ranged from 60% to 92% (Gefter & Conant, 1988).
    a) In autopsy series, pleural plaques have been identified in approximately one-third to one-half of persons 20 years after significant asbestos exposure, and many of these plaques were not identified on antemortem x-rays (Talcott & Antman, 1988).
    2) Radiographically-detected pleural plaques have been shown to correlate well with asbestos bodies on autopsy if the lung burden is more than 500 asbestos bodies/5 grams of autopsy lung tissue (Kishimoto et al, 1989).
    3) The association of pleural thickening and calcification enhances diagnostic accuracy (ATSDR, 1990). There are several conditions which can mimic asbestos-related diseases, including scarring adjacent to old disease, trauma, fat or muscle shadows, healed tuberculosis, histoplasmosis, and other conditions (Reger et al, 1990).
    4) Using the ILO criteria, as many as 10% to 20% of workers with histological evidence of asbestosis will have normal chest x-ray films (Rockoff & Schwartz, 1988). In the other extreme, positive radiographical ILO readings of pulmonary fibrosis have been found with normal lungs.
    5) Variations in classifying pleural changes and inadequacy in describing features believed to be important by some readers were problems identified with the ILO 1980 International Classification of the Radiographic Appearances of Pneumoconioses (Rossiter et al, 1988). A survey found an intraobserver variation of 3.9%, and an interobserver variation of 18% (Gefter & Conant, 1988).
    6) Despite the discrepancies between histologic and radiographic diagnosis, roentgenographic interpretations are still deemed useful however subjective they may be (Ducatman, 1989).
    7) Because of intra- and interobserver variations in interpretations, chest x-rays are only supportive diagnostic tools (Gefter & Conant, 1988). An ILO grade of less than 1/0 implies that the diagnosis is unlikely, but diagnosis still rests on multiple clinical criteria (Gefter & Conant, 1988; Schwartz et al, 1988).
    8) Reviews of smoking and roentgenographic opacities in asbestos workers suggest that parenchymal opacities alone will not reliably differentiate between the impacts of asbestos exposure and smoking in patients who have both risk factors (Blanc et al, 1988; Ducatman et al, 1990; Hnizdo & Sluis-Cremer, 1988). A cross-sectional study confirmed that smoking can be dose-related with parenchymal, but not pleural, changes (Delclos et al, 1990).
    9) CT scan has been recommended as a sensitive means of differentiating asbestos-related pleural plaques from soft-tissue densities (ATSDR, 1990).
    10) The strong association of both circumscribed plaques and diffuse pleural thickening with parenchymal fibrosis on high-resolution computerized tomography (HRCT) suggest that HRCT scan may be useful in identifying parenchymal injury not detected with postero-anterior chest radiographs (Schwartz et al, 1990a; Paris et al, 2004; Neri et al, 1996).
    a) HRCT detected pleural and/or pulmonary involvement in a group of 72 asbestos-exposed workers who did not have clear evidence of lung disease on chest radiographs (Falaschi et al, 1995).
    b) A study of 630 retired workers with documented asbestos occupational exposure histories revealed that HRCT detected early-stage asbestosis in individuals with normal chest radiographs (Paris et al, 2004).
    11) Gallium scanning and/or bronchoalveolar lavage have been recommended as adjuncts for the detection of active (even subclinical) pulmonary inflammation in asbestos-exposed workers (Barbers & Abraham, 1989; Delclos et al, 1989; Hayes et al, 1989). Gallium-67 hyperfixation into the lungs has occurred in over 80% of patients with asbestosis; it is therefore possible to detect an infraradiographic attenuation (decay), using Gallium-67 scintillography, in patients exposed to asbestos fibers (Valeyre & Letourneux, 1999).
    12) A prospective study of 3893 shipyard workers found no strong association between different exposure parameters (e.g., chest radiographs, spirometry, and questions about smoking habits, asbestos exposure, and respiratory symptoms) and risk of mesothelioma. Traditional health monitoring parameters appear to be of little value in assessing persons with a high risk of mesothelioma following asbestos exposure (Sanden & Jaruholm, 1991).
    B) RADIOGRAPHIC-OTHER
    1) Chest x-ray is useful, but the diagnosis is often difficult to make from x-rays taken early in the disease process, especially as there do not appear to be any pathognomonic radiographic findings in asbestosis (Gefter & Conant, 1988).
    2) Oblique postero-anterior chest x-ray views are sometimes useful (Gefter & Conant, 1988; Newhouse, 1983).
    3) Localized fibrous thickenings 3 to 5 mm in size in the parietal pleura are the most common asbestos-related changes on chest radiographs (Talcott & Antman, 1988).
    4) Only minor pleural changes are seen 10 to 20 years after initial exposure; calcification is apparent on chest radiographs after 20 years (Talcott & Antman, 1988).
    5) In early cases, blunting of the costophrenic zones may be seen (Gefter & Conant, 1988; Lilis et al, 1988). Diffuse pleural thickening with concomitant blunted costophrenic angle is also the most frequent residual radiological abnormality after benign pleural effusion (Lilis et al, 1988).
    6) The "shaggy" cardiac border described in advanced asbestosis is an uncommon finding (Talcott & Antman, 1988).
    7) Pleural effusion occurs in 3% to 5% of asbestos workers as early as 3 years after the first exposure. Rule out primary or secondary pleural malignancies and other entities such as tuberculosis. A unilateral pleural effusion more than 20 years after asbestos exposure suggests malignant mesothelioma (Talcott & Antman, 1988).
    8) In a general health survey, men 30 to 59 years old had a 2.7% incidence of pleural effusions in non-asbestos exposed individuals and a 5.7% incidence in asbestos exposed individuals. The authors estimated that 10% or more of cases of pleurisy (with effusion) could be associated with asbestos exposure (Malberg & Hillerdal, 1990).
    9) Thickened lobar fissures, especially with extensive pleural abnormalities, suggest mesothelioma (Talcott & Antman, 1988).
    10) A positive gallium scan indicates lung inflammation and predicts a decline in FVC and the development of progressive radiographic abnormality (Harber & Smitherman, 1991).

Methods

    A) OTHER
    1) OSHA REQUIRED AIR MONITORING: The OSHA Asbestos Standards specify required air monitoring in worksites with asbestos exposure.

Life Support

    A) Support respiratory and cardiovascular function.

Patient Disposition

    6.3.3) DISPOSITION/INHALATION EXPOSURE
    6.3.3.1) ADMISSION CRITERIA/INHALATION
    A) While there is no specific therapy for asbestos exposure, patients may require inpatient therapy for their poor pulmonary function or cancer treatment.
    6.3.3.2) HOME CRITERIA/INHALATION
    A) There is no role for home management.
    6.3.3.3) CONSULT CRITERIA/INHALATION
    A) A toxicologist may be consulted to aid in determining if a patient's symptoms or cancer is from a previous exposure to asbestos. Consult a pulmonologist for patients with evidence of asbestos-induced pulmonary complications.
    6.3.3.5) OBSERVATION CRITERIA/INHALATION
    A) Patients with known asbestos exposure require outpatient monitoring to detect complications.

Monitoring

    A) Monitor chest CT scan, chest x-ray, and pulmonary function tests in asbestos-exposed patients.
    B) Open lung biopsy is the only definitive diagnostic test for asbestosis.
    C) Bronchoalveolar lavage (BAL) has been recommended as an adjunct in the diagnosis of asbestos-related pulmonary diseases.
    D) OSHA has specific clinical monitoring requirements for workers exposed to asbestos.

Oral Exposure

    6.5.1) PREVENTION OF ABSORPTION/PREHOSPITAL
    A) PREHOSPITAL: Most asbestos exposures are of a chronic nature, such that traditional first aid is not appropriate. In the event of a heavy acute exposure, move the patient to fresh air. Monitor for respiratory distress. Administer oxygen and assist ventilation as required.

Inhalation Exposure

    6.7.1) DECONTAMINATION
    A) Most asbestos exposures are of a chronic nature, such that traditional first aid is not appropriate. In the event of a heavy acute exposure, move the patient to fresh air. Monitor for respiratory distress. Administer oxygen and assist ventilation as required. Treat bronchospasm with inhaled beta-2 agonist and oral or parenteral corticosteroids.
    6.7.2) TREATMENT
    A) SUPPORT
    1) ASBESTOSIS: Since there is no effective therapy for an established case of asbestosis, treatment is aimed at maintaining vital capacity and reducing respiratory work load (Mossman & Gee, 1989; Muir, 1999).
    2) Similar to other patients with chronic pulmonary diseases, treatment is aimed at supportive efforts and may include the following: vaccination against pneumococcal pneumonia and influenza, bronchodilator administration, adequate nutrition, home oxygen therapy, and rebreathing and exercise training. Pharmacological agents to limit the progression of fibrosis as yet have not been beneficial (Wagner, 1997).
    3) MESOTHELIOMA: Neither surgery, chemotherapy, nor radiotherapy have been successful in producing remission of mesothelioma (Newhouse, 1983). Multimodal therapy has been employed to prolong disease-free intervals (Talcott & Antman, 1988) Melloni, 2001).
    4) PLEURAL PLAQUES: Plaques by themselves have little effect on pulmonary function and life expectancy, and do not produce complications that necessitate treatment (Dark & Pingleton, 1983; Jones et al, 1988).
    5) PLEURAL EFFUSION: No therapy is necessary for this complication; however, close monitoring is mandatory to rule out mesothelioma and other possible causes (Dark & Pingleton, 1983).
    B) MONITORING OF PATIENT
    1) Monitor CT scan, chest x-ray, and pulmonary function tests in asbestos-exposed patients.
    2) Open lung biopsy is the only definitive diagnostic test for asbestosis.
    3) Bronchoalveolar lavage (BAL) has been recommended as an adjunct in the diagnosis of asbestos-related pulmonary diseases.
    4) OSHA has specific clinical monitoring requirements for workers exposed to asbestos.
    C) EXPERIMENTAL THERAPY
    1) MESOTHELIOMA: Currently, research is being conducted on irinotecan, a novel drug, that has been used in combination with cisplatin and mitomycin. Another pilot study is recruiting patients with mesothelioma to compare the efficacy of three drug regimens: vinorelbine tartrate alone; mitomycin, vinblastine plus cisplatin; and active supportive care. Other studies have monitored the effectiveness of thalidomide in the treatment of mesothelioma and suggested that the drug can actually inhibit the growth of blood vessels in new formed tumors (Kazan-Allen, 2001).
    a) In Brazil, experimental work in rodents found positive results in diminishing lung fibrosis induced by paraquat (experimental model for lung fibrosis) when the animals were treated with thalidomide (an anti-mRNA TNF-alpha forming agent) in combination with montelukast (a cysteinyl leukotriene receptor blocker) and acetyl salicylic acid (a prostaglandin-forming inhibitor) (Caldas et al, 1999).

Case Reports

    A) ADULT
    1) A 44-year-old woman diagnosed with mesothelioma had been exposed to talc for over 12 years (Barnes & Rogers, 1984). Lung tissue revealed elevated levels of amosite.
    2) A 76-year-old nonsmoking housewife with no direct occupational exposure to asbestos presented with pleural effusion and died of malignant mesothelioma, believed to have been acquired after "bystander" exposure from her husband who worked for 34 years as a machinist in a shipyard (Huncharek et al, 1989).
    3) A 72-year-old man with known asbestos exposure presented with dyspnea on exertion and chest discomfort for about six months prior to admission. Computed tomography of the thorax revealed mild pleural thickening of the right upper thorax and severe pleural thickenings on the left interior and posterior thorax. Pleural biopsy demonstrated a diffuse fibrosis.
    a) Six weeks later, the patient returned with progressive weakness, malaise, weight loss, BUN of 63 mg/dL, creatinine of 4.5/dL, potassium of 5.3 mmol/L, and phosphate of 6.2 mg/dL. Abdominal ultrasound revealed bilateral hydronephrosis which was confirmed with an MRI scan. Fibrosis was noted surrounding the distal abdominal aorta and proximal iliac arteries. Intraoperative procedures revealed retroperitoneal and peri-iliac fibrosis with encasement of the right and left ureters in the fibrotic process.
    b) Lysis of the retroperitoneal fibrosis and periureteral adhesions was performed. The ureteral segment was found to have periureteral fibrosis, consistent with retroperitoneal fibromatosis with invasion of the right ureter; 36 months after discharge, no further progression of symptoms was observed (Moguire et al, 1991).

Summary

    A) TOXICITY: Low-level exposures or occupational exposure for under two years were not associated with increased mortality. Asbestosis has rarely been reported with intense exposure of only one day's duration. Lowest observed adverse effect levels (LOAELs) for systemic effects, determined from human inhalation studies, range from 25 to 54 fiber-year/mL (f-yr/mL, obtained by multiplying years of exposure times the average air concentration in fibers/mL) for intermediate exposure duration of 15 to 364 days. At the chronic exposure duration level (365 days or more), LOAELs ranged from 20 to 207 f-yr/mL for less serious systemic effects (those not expected to cause significant dysfunction or death or the significance is not entirely clear) and from 15 to 1271 f-yr/mL for serious systemic effects (those that evoke failure in a biological system and can lead to morbidity or mortality). LOAELs for cancer from chronic inhalation exposure, based on human studies, ranged from 5 to 1050 f-yr/mL.

Minimum Lethal Exposure

    A) Data from autopsies of asbestos workers showed that asbestosis doesn't occur until the lung fiber burden exceeds 5 x 10(5) fibers/g of dried lung (>5 micron fiber length). Severe cases had counts as high as 10(10) fibers/g (ACGIH, 2001).

Maximum Tolerated Exposure

    A) Health effects from asbestos exposure will depend on the type of fiber, the potency associated with the particular fiber type, and the internal dose. Dose is influenced by airborne concentrations, exposure patterns, and fiber shape, diameter, and length. A dose-effect relationship has been established based on epidemiological studies, and is evident for asbestos exposure and asbestosis and lung cancer but is less marked with mesothelioma (ACGIH, 2001) Bingham, et al, 2001; (Harbison, 1998).
    1) In vitro studies have shown that fibers less than 5 microns in length are not likely to be pathogenic. Inhalation studies in rats showed that at very high exposure all respirable fibers over 5 microns long cause lung fibrosis and some lung cancer. Longer fibers are too long to be cleared by macrophages. Straight fibers in the size range 5-15 microns long and of the order 0.1 micron thick are most hazardous at low exposure due to the risk of mesothelioma (ACGIH, 2001) Baxter, et al, 2000).
    2) Inhalation studies on rats showed that chrysotile had a half-life in the lung of weeks or months, as compared to the amphiboles which last indefinitely. Lung burden studies showed that chrysotile fibers deposited in the lung are cleared more rapidly than tremolite fibers, increasing the tremolite/chrysotile ratio over time following exposure. The lower carcinogenicity of chrysotile in humans versus animals may be associated with high doses and insufficient time for clearance in the short animal life span (Baxter, et al, 2000; Bingham, et al, 2001).
    3) An early study of asbestos textile workers used the presence of persistent high-pitched rales in the basal portions of the lung as the criterion for asbestosis diagnosis. It was determined that less than 100 fiber-years of exposure (2 fibers/cc over a 50-year working period or 4 fibers/cc over a 25-year period) would cause development of asbestosis in no more than 1% of the workers. Results contributed to refinement of existing occupational exposure recommendations. This cohort was further studied by other investigators, and is the only cohort of asbestos workers in the world where health effects were correlated with definitive exposure data defined as fibers/cc (ACGIH, 2001).
    4) A study of 1176 asbestos cement workers in Sweden showed no statistically significant increase in lung cancer, possibly due to low exposure levels and relatively few smokers in the cohort. Levels were approximately 10 mg/m(3) in the early period of exposure and averaged 1 to 2 fibers/ml later in the exposure period (Harbison, 1998).
    5) Cement workers with a cumulative exposure level below 30 to 40 fibers/cc-years were found to show very little radiological evidence of asbestosis. The same study reported crocidolite exposure at one plant led to a higher prevalence and faster progression of asbestosis than with chrysotile exposure alone (ACGIH, 2001).
    6) Asbestosis prevalence rates were about 20% for cumulative exposure of about 25 fibers/cc-years where chrysotile was used in a Quebec textile mill and 8% for cumulative exposure of about 60 fibers/cc-years in Quebec miners and millers (ACGIH, 2001).
    7) A study of chrysotile exposure that examined a cohort of Quebec miners and millers estimated no detectable increase in lung cancer with a 20 year exposure below 50 fibers/cc (ACGIH, 2001).
    8) Lowest observed adverse effect levels (LOAELs) for systemic effects determined from human inhalation studies range from 25 to 54 f-yr/ml for intermediate exposure duration (15 to 364 days). At the chronic exposure duration level (365 days or more), LOAELs ranged from 20 to 207 f-yr/ml for less serious systemic effects (those not expected to cause significant dysfunction or death or the significance is not entirely clear) and from 15 to 1271 f-yr/ml for serious systemic effects (those that evoke failure in a biological system and can lead to morbidity or mortality). Systemic effects observed after inhalation exposure include respiratory, cardiovascular, and gastrointestinal effects (ATSDR , 2001).
    9) A LOAEL of 54 f-yr/ml was provided for cancer at the intermediate exposure duration level based on a study of human inhalation exposure. LOAELs for cancer from chronic inhalation exposure (human studies) ranged from 5 to 1050 f-yr/ml (ATSDR , 2001).
    10) A LOAEL of 500 mg/kg/day for rats was reported for a cancer effect level of intestinal polyps in a lifetime oral exposure study. A LOAEL of 20 mg/kg/day was reported for less serious systemic effects resulting from chronic oral exposure in rats (ATSDR , 2001).
    B) OCCUPATIONAL
    1) CARCINOGENICITY -
    a) ACGIH - asbestos (all forms), A1, Confirmed Human Carcinogen based on the association between human exposure and lung cancer and mesothelioma (ACGIH, 2001).
    b) IARC classifies asbestos (actinolite, amosite, anthophyllite, chrysotile, crocidolite, tremolite) as a Group 1, known carcinogen ((IARC, 1987)).
    c) USEPA Evidence for Human Carcinogenicity from the Integrated Risk Information System (IRIS) (EPA, 1993):
    1) Classification: A, human carcinogen.
    a) Basis: Observation of increased mortality and incidence of lung cancer, mesotheliomas and gastrointestinal cancer in occupationally exposed workers are consistent across investigators and study populations. Animal studies by inhalation in two strains of rats showed similar findings for lung cancer and mesotheliomas. Animal evidence for carcinogenicity via ingestion is limited (male rats fed intermediate-range chrysotile fibers; i.e., >10 um length, developed benign polyps), and epidemiologic data in this regard are inadequate (EPA, 1993).
    d) NTP classifies asbestos as a known carcinogen, where there is sufficient evidence of carcinogenicity from studies in humans that indicate a causal relationship between exposure to the substance and human cancer (ACGIH, 2001).
    e) NIOSH considers asbestos (i.e., actinolite, amosite, anthophyllite, chrysotile, crocidolite, and tremolite) to be a potential occupational carcinogen (NIOSH , 2002).

Workplace Standards

    A) ACGIH TLV Values for CAS12172-73-5 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    B) ACGIH TLV Values for CAS14567-73-8 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    C) ACGIH TLV Values for CAS12001-28-4 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    D) ACGIH TLV Values for CAS17068-78-9 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    E) ACGIH TLV Values for CAS13768-00-8 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    F) ACGIH TLV Values for CAS1332-21-4 (American Conference of Governmental Industrial Hygienists, 2010):
    1) 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.
    a) Adopted Value
    1) Asbestos, all forms
    a) TLV:
    1) TLV-TWA: 0.1 f/cc
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: A1
    2) Codes: F
    3) Definitions:
    a) A1: Confirmed Human Carcinogen: The agent is carcinogenic to humans based on the weight of evidence from epidemiologic studies.
    b) F: Respirable fibers: length greater than 5 µm; aspect ratio 3:1 or greater, as determined by the membrane filter method at 400 to 450X magnification (4-mm objective), using phase-contrast illumination.
    c) TLV Basis - Critical Effect(s): Pneumoconiosis; lung cancer; mesothelioma
    d) Molecular Weight: NA
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:

    G) ACGIH TLV Values for CAS12001-29-5 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Not Listed

    H) NIOSH REL and IDLH Values for CAS12172-73-5 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    I) NIOSH REL and IDLH Values for CAS14567-73-8 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    J) NIOSH REL and IDLH Values for CAS12001-28-4 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    K) NIOSH REL and IDLH Values for CAS17068-78-9 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    L) NIOSH REL and IDLH Values for CAS13768-00-8 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    M) NIOSH REL and IDLH Values for CAS1332-21-4 (National Institute for Occupational Safety and Health, 2007):
    1) Listed as: Asbestos
    2) REL:
    a) TWA:
    b) STEL:
    c) Ceiling:
    d) Carcinogen Listing: (Ca) NIOSH considers this substance to be a potential occupational carcinogen (See Appendix A in the NIOSH Pocket Guide to Chemical Hazards).
    e) Skin Designation: Not Listed
    f) Note(s): See Appendix A; See Appendix C
    3) IDLH: Not Listed

    N) NIOSH REL and IDLH Values for CAS12001-29-5 (National Institute for Occupational Safety and Health, 2007):
    1) Not Listed

    O) Carcinogenicity Ratings for CAS12172-73-5 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    P) Carcinogenicity Ratings for CAS14567-73-8 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    Q) Carcinogenicity Ratings for CAS12001-28-4 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    R) Carcinogenicity Ratings for CAS17068-78-9 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    S) Carcinogenicity Ratings for CAS13768-00-8 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    T) Carcinogenicity Ratings for CAS1332-21-4 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A1 ; Listed as: Asbestos, all forms
    a) A1 :Confirmed Human Carcinogen: The agent is carcinogenic to humans based on the weight of evidence from epidemiologic studies.
    2) EPA (U.S. Environmental Protection Agency, 2011): A ; Listed as: Asbestos
    a) A : Human Carcinogen.
    3) 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): 1 ; Listed as: Asbestos
    a) 1 : The agent (mixture) is carcinogenic to humans. The exposure circumstance entails exposures that are carcinogenic to humans. This category is used when there is sufficient evidence of carcinogenicity in humans. Exceptionally, an agent (mixture) may be placed in this category when evidence of carcinogenicity in humans is less than sufficient but there is sufficient evidence of carcinogenicity in experimental animals and strong evidence in exposed humans that the agent (mixture) acts through a relevant mechanism of carcinogenicity.
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Asbestos
    a) Ca : NIOSH considers this substance to be a potential occupational carcinogen (See Appendix A in the NIOSH Pocket Guide to Chemical Hazards).
    5) MAK (DFG, 2002): Category 1 ; Listed as: Asbestos (chrysotile, crocidolite, amosite, anthophyllite, actinolite, tremolite) (fibrous dust)
    a) Category 1 : Substances that cause cancer in man and can be assumed to make a significant contribution to cancer risk. Epidemiological studies provide adequate evidence of a positive correlation between the exposure of humans and the occurence of cancer. Limited epidemiological data can be substantiated by evidence that the substance causes cancer by a mode of action that is relevant to man.
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): K ; Listed as: Asbestos
    a) K : KNOWN = Known to be a human carcinogen

    U) Carcinogenicity Ratings for CAS12001-29-5 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) 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
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    V) OSHA PEL Values for CAS12172-73-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    W) OSHA PEL Values for CAS14567-73-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    X) OSHA PEL Values for CAS12001-28-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    Y) OSHA PEL Values for CAS17068-78-9 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    Z) OSHA PEL Values for CAS13768-00-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    AA) OSHA PEL Values for CAS1332-21-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

    AB) OSHA PEL Values for CAS12001-29-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

Toxicity Information

    7.7.1) TOXICITY VALUES
    A) ACTINOLITE References: RTECS, 2002
    B) AMOSITE References: RTECS, 2002
    1) TCLo- (INHALATION)RAT:
    a) 11 mg/m(3) for 2Y-intermittent -- carcinogenic by RTECS criteria; tumors associated with lung, thorax, or respiratory system
    C) ANTHOPHYLLITE References: RTECS, 2002
    1) TCLo- (INHALATION)RAT:
    a) 11 mg/m(3) for 1Y-intermittent -- carcinogenic by RTECS criteria; tumors associated with lung, thorax, or respiratory system
    D) ASBESTOS References: RTECS, 2002
    1) TCLo- (INHALATION)HUMAN:
    a) 1.2 fb/cc for 19Y-continuous -- pulmonary effects
    E) CHRYSOTILE References: RTECS, 2002
    1) TCLo- (INHALATION)HUMAN:
    a) 2.8 fb/cc for 5Y -- effects on lung, thorax, or respiration including fibrosis, focal (pneumoconiosis), cough, and dyspnea
    b) 400 mppcf for 1Y-continuous -- carcinogenic by RTECS criteria; effects to lung, thorax, or respiration such as fibrosis, focal (pneumoconiosis) and tumors
    2) TCLo- (INHALATION)RAT:
    a) 11 mg/m(3) for 26W-intermittent -- carcinogenic by RTECS criteria; tumors associated with lung, thorax, or respiratory system
    b) 8210 ug/m(3) for 6H/20D- intermittent -- fibrosis (interstitial)
    F) CROCIDOLITE References: RTECS, 2002
    1) TCLo- (INHALATION)MOUSE:
    a) 13600 ug/m(3) for 6H/5D -intermittent -- fibrosing alveolitis
    2) TCLo- (INHALATION)RAT:
    a) 10 mg/m(3) for 6H/1Y-intermittent -- fibrosis (interstitial); fibrosing alveolitis
    b) 7200 ug/m(3) for 6H/20D- intermittent -- fibrosis (interstitial)
    c) 11 mg/m(3) for 1Y-intermittent -- carcinogenic by RTECS criteria; tumors associated with lung, thorax, or respiratory system
    G) TREMOLITE References: RTECS, 2002
    7.7.2) RISK ASSESSMENT VALUES
    A) LOAEL- (ORAL)RAT:
    1) 500 mg/kg/day -- reported for a cancer effect level of intestinal polyps in a lifetime exposure study (ATSDR , 2001)
    2) 20 mg/kg/day -- reported for less serious systemic effects resulting from chronic oral exposure in rats (ATSDR , 2001).

Toxicologic Mechanism

    A) CYTOTOXICITY - The actual toxic mechanisms of the different asbestos fibers is not well understood.
    1) Experimental animal studies have suggested a role for lipid peroxidation, adsorption of red blood cells on asbestos fibers, decreased calcium- and magnesium-activated ATPase activities, stimulated phosphatidylinositol turnover, activation of protein kinase C, and increased cytochrome C oxidase activity (Bissonnette et al, 1990; Goodglick et al, 1989; Goodglick & Kane, 1990; Elferink et al, 1989; HSDB , 1995; Iguchi & Kojo, 1989; Roney & Holian, 1989).
    2) In vitro studies found that more than 20 mcg/mL of chrysotile can increase prostaglandin E2 production by macrophages and target cells and inhibit the cytotoxicity of rat alveolar macrophages (Bissonnette et al, 1990).
    3) In vitro studies found that crocidolite fibers induce lipid peroxidation and disrupt the mitochondrial membrane potential in mouse macrophages (Goodglick & Kane, 1990; Goodglick et al, 1989). Hemolysis of human erythrocytes was attributed to the same mechanism (Iguchi & Kojo, 1989).
    4) With asbestos exposure, polymorphonuclear leukocytes can generate hydrogen peroxide which causes hemolysis and injury to human pulmonary epithelial cells (Iguchi & Kojo, 1989; Kamp et al, 1989). Superoxide anion production has also been noted in asbestos-exposed guinea pig and human alveolar macrophages (Rom et al, 1987; Roney & Holian, 1989).
    5) Iron was required for hydroxyl radical production in alveolar epithelial cells cultured with asbestos. Both cytotoxicity and DNA damage were dependent on the production of hydroxyl radicals (Kamp et al, 1995).
    6) Chrysotile asbestos induced release of lactic dehydrogenase from rabbit peritoneal polymorphonuclear leukocytes and caused membrane damage and cytotoxicity (Elferink et al, 1989). With extracellular calcium, asbestos activated exocytosis and release of lysozymes and glucuronidase.
    7) Asbestos fibers exerted a dose-dependent functional suppressive, rather than cytotoxic, effect on the natural killer (NK) effector cells, thus rendering the NK cells "paralyzed" once bound to their targets (deShazo et al, 1988; Robinson, 1989).
    8) Studies with human breast carcinoma cells and human laryngeal carcinoma cells suggest an interaction between asbestos fibers and the normal mitotic process. After fiber penetration of the cell cytoplasm, a rearrangement of the cytoskeletal apparatus appears to occur. Internalization of fibers appears to lead to formation of giant multinucleated cells (Malorni et al, 1990).
    B) FIBROGENESIS - The mechanisms that govern the fibrogenic effects of asbestos in the lungs have not been completely elucidated. Two currently popular theories (not mutually exclusive) involve a central role of oxygen radicals generated by the asbestos fibers, versus induction of various growth factors and cytokines to mediate fibrosis (Brody, 1993).
    1) With asbestos inhalation, alveolar macrophages accumulate at the area of fiber deposition (Mossman et al, 1990).
    2) With phagocytosis of the fiber, the activated macrophages produce a mixture of fibroblast growth factors, chemoattractants, fibronectin, prostaglandins, procoagulants, leukotriene B4, lysozomal enzymes, active oxygen metabolites, tumor necrosis factor-alpha, and interleukin 1 (ATSDR, 1990; Bissonnette et al, 1990; Callahan et al, 1990; Dark & Pingleton, 1983; Elferink et al, 1989; Garcia et al, 1989; Goodglick et al, 1989; Goodglick & Kane, 1990; Hayes et al, 1988; HSDB , 1995; Iguchi & Kojo, 1989; Kagan, 1988; Mossman et al, 1990; Roney & Holian, 1989; Schwartz et al, 1989; Ljungman et al, 1994).
    3) Lung injury can be induced by an asbestos-related increase in neutrophils which release a collagenase and neutrophil chemotactic factors (Delclos et al, 1989; Garcia et al, 1989; Hayes et al, 1988; Mossman & Gee, 1989).
    4) These inflammatory mediators incite widespread tissue destruction, granuloma formation, and pulmonary fibrosis (ATSDR, 1990; Callahan et al, 1990; Chang et al, 1988; Dark & Pingleton, 1983; Garcia et al, 1989; Hayes et al, 1988; Kagan, 1988; Schwartz et al, 1989).
    5) Once inside the macrophages, the fibers may be coated with a mucopolysaccharide and iron matrix, thus forming the drumstick configuration of the ferruginous asbestos bodies (ATSDR, 1990; Dark & Pingleton, 1983). In asbestosis, coated fibers may be much fewer than uncoated fibers which exert the most damage (Dark & Pingleton, 1983).
    6) Because the fibers concentrate in the lower lung fields, fibrosis tends to occur first in the lung bases; pleural effects are generally confined to the lower two-thirds of the thorax.
    7) Plaques are formed when sharp fibers (such as anthrophyllite) penetrate into the pleura during breathing or via the lymphatic system (Dark & Pingleton, 1983).
    8) Asbestos fibers can also penetrate to the terminal bronchioles and elicit a fibrogenic response upon entry into the peribronchiolar space (ATSDR, 1990).
    9) The pneumoconiotic reaction appears to be more closely related to the surface area as opposed to the number of retained fibers per gram of lung tissue (Becklace, 1991).
    C) CARCINOGENESIS - The mechanism(s) by which asbestos can induce cancer is not known. It is unclear whether or not asbestos can induce carcinogenesis by initiating a heritable genetic change and promoting this with proliferative and genotypic changes (Mossman et al, 1990).
    1) The reactive oxygen metabolites produced in asbestos-induced lipid peroxidation can cause mutations, DNA strand breaks, chromosomal breaks, nuclear changes, and epigenetic changes (Goodglick & Kane, 1990).
    2) Because 144 patients with asbestos-related mesotheliomas had important differences from the epidemiological pattern of asbestos-related bronchogenic cancer, it was suggested that asbestos may not act as a complete carcinogen, but rather as a promoter (Browne, 1983).
    3) Longitudinal and cross-sectional data from a brake manufacturing plant also suggest the irritant role of asbestos (Parnes, 1990).
    4) Asbestos absorbs carcinogens like benzo(a)pyrene and catalyzes the oxidation of weak to potent carcinogens (Dunn, 1989). Hydrogen peroxide in cigarette smoke and asbestos may induce DNA strand breaks via a hydroxyl radical dependent mechanism.
    5) Asbestos fibers can provoke inflammation by generating reactive oxygen and nitrogen species. The more important metabolites in the pathogenesis of this disease are manganese superoxide dismutase, hydrogen peroxide, hydroxyl radicals and nitric oxide. Recently, the asbestos fibers have been pointed out as responsible for a dose-dependent apoptosis of mesothelial cells in rats, rabbits and humans. A chrysotile and crocidolite may cause apoptosis in human alveolar macrophages following a 48-hour exposure. Alveolar and bronchiolar epithelial cells from rats exposed to asbestos have shown apoptosis as opposed to the lungs of normal rats never exposed to these fibers (Pinnula, 1999).
    6) The development of mesothelioma seems to be related to the length and diameter of fibers and to prolonged exposure, although there have been reports with very minimal asbestos exposure (Dunn, 1989). Unlike bronchogenic carcinoma, there is no association with smoking.
    7) The actual mechanism of induction of lung tumors involves formation of free radicals as a result of the direct contact of the organic molecules with the crystal fibers, in the presence of iron (Greim, 1997).
    D) There is growing interest in the possible role of free radicals in asbestos-mediated carcinogenesis. Peroxides enhance the activity of asbestos in causing DNA damage (Mahmood et al, 1993; Mahmood et al, 1994). Peroxides react with ferrous ion complexed to asbestos particles to generate free radicals and DNA damage (Ghio et al, 1994).
    E) Mononuclear peripheral leukocytes from patients with lung cancer were more active for generating reactive oxygen species in the presence of asbestos than were cells from patients without cancer. The level of reactive oxygen generation was inversely correlated with one-year survival rates in these patients (Nyberg et al, 1994).
    F) Asbestos can induce expression of c-fos and c-jun oncogenes in rat pleural mesothelial cells; crocidolite was more active than chrysotile for this effect, as it is for induction of mesothelioma (Heintz et al, 1993).

Physical Characteristics

    A) Asbestos is a generic name for a class of naturally occurring, hydrated, fibrous silicate minerals of the serpentine or amphibole mineralogical series. Asbestos is characterized by bundles of fine, crystalline fibers. Parallel bundles will easily separate and split longitudinally into finer and finer individual fibrils. Serpentine fibers are flexible and coiled or curly, while amphibole fibers are brittle, thin, straight, and needle- or rod-shaped (ACGIH, 2001) ATSDR, 2001; (S Budavari , 2001; Harbison, 1998).
    B) Asbestos is composed of silicon, oxygen, hydrogen, and various metal cations. The compound crystallized metallic silicates that make up asbestos minerals will vary in metal content according to the limitations of the crystal lattice structure (Bingham, et al., 2001; ((EPA, 2002h)).
    C) Asbestos is fire-resistant, insoluble, moldable, and generally chemically inert. It has unique tensile strength and a high friction coefficient. Asbestos is a poor conductor of heat and will resist corrosion, although chrysotile is attacked by acid `(ATSDR, 2001; (Bingham et al, 2001; S Budavari , 2001; Lewis, 1998).
    1) Order of typical tensile strengths: crocidolite > chysotile > amosite > anthophyllite > tremolite > actinolite (HSDB , 2002a).
    a) Typical chrysotiles have tensile strengths approximately 3,727 Mpa (5.4 x 10(5) psi), which is greater than steel piano wire and fiberglass (HSDB , 2002c).
    b) Chrysotile asbestos has a tensile strength of 31,000 kg/cm(2) (HSDB , 2002c).
    2) Relative order of acid resistance: tremolite > anthophyllite > crocidolite > actinolite > amosite > chrysotile (HSDB , 2002a).
    D) Asbestos fibers do not have a detectable odor or taste. They do not dissolve or evaporate and are resistant to chemical or biological degradation (ATSDR, 2001).
    E) Serpentine asbestos is the mineral chrysotile, also referred to as white asbestos. It is a magnesium silicate and is structurally different from the amphiboles. It is usually white to grayish green and has a silky luster. It consists of strong, flexible fibers that occur in bundles up to several centimeters long. The bundled cylindrical fibers easily divide into smaller bundles and into individual fibrils (Baxter et al, 2000; Bingham et al, 2001; Lewis, 2001).
    1) Chrysotile is a curled sheet silicate that is spiraled as a helix around a central capillary. Double sheets of brucite and silica surround a small core of amorphous magnesium silicate, similar to a curved tube. Due to their strength and flexibility, the thin crystalline fibers are capable of being woven. The intrinsic structure of the chrysotile fiber aggregate also allows more intermediate shapes during mechanical treatment, better than with the amphiboles which are more brittle (Baxter et al, 2000; Bingham et al, 2001; HSDB , 2002c).
    2) Chrysotile is a selectively adsorptive material. This characteristic is likely related to the very small fiber diameter, the high specific surface area, and a relatively reactive surface. Commercial grades of chrysotile can adsorb as much as 2-3% weight percent moisture from saturated air. Adsorption studies examining a variety of organic compounds have shown that chrysotile has greater affinity for polar molecules (HSDB , 2002c).
    F) Amphibole asbestos includes various silicates of magnesium, iron, calcium, and sodium, including amosite, crocidolite, and the fibrous varieties of tremolite, actinolite, and anthophyllite. Amphibole fibers are generally more brittle than serpentine asbestos and cannot be spun. They are more resistant to chemicals and heat than serpentine asbestos. The amphiboles can form a variety of polymeric structures by forming Si-O-Si bonds. The linear double chain structure crystallizes into long, thin, straight fibers that are characteristic of this type of asbestos. (Baxter et al, 2000; Lewis, 2001).
    1) Amphibole fibers will undergo dehydroxylation and decomposition at elevated temperatures. Compared to chrysotile, the amphibole fibers are relatively acid resistant. However, under boiling conditions and high acid concentrations the amphiboles can exhibit weight losses of approximately 2-20% (HSDB , 2002a).
    2) Amosite, or fibrous grunerite, is an iron magnesium silicate. It is also known as brown asbestos, but may be yellowish-gray to dark brown in color. It has a vitreous to pearly luster. The fibers of amosite are course (Baxter et al, 2000; Bingham et al, 2001).
    3) Anthophyllite is the fibrous form of another iron magnesium silicate (i.e., this silicate is dissimilar from grunerite). It has similar properties as amosite (Baxter et al, 2000).
    4) Crocidolite, or blue asbestos, is a cobalt blue to lavender blue mineral. It is the fibrous form of riebeckite, a sodium iron silicate. It can appear from silky to dull in luster. Fiber bundles are shorter and more stiff than chrysotile and readily split to straight fibrils. Compared to chrysotile, crocidolite is much more acid-resistant and has a slightly higher heat tolerance (Baxter et al, 2000; Bingham et al, 2001).
    5) Tremolite is a calcium magnesium silicate that crystallizes as an amphibole fiber or as a platey talc. It may be gray-white, green, yellow, or blue and has a silky luster. Fibrous tremolite is found as a contaminant with other fibers, such as chrysotile. Tremolite and actinolite form a continuous mineral series with iron (II) and magnesium substitution ongoing while maintaining the same three-dimensional crystal structure. Tremolite contains little or no iron, and actinolite contains iron (ATSDR, 2001; Baxter, et al., 2000; (Bingham et al, 2001).

Molecular Weight

    A) Varies (NIOSH , 2002)
    B) Not applicable. All forms of asbestos are indefinite polymers (ATSDR, 2001).

General Bibliography

    1) 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.
    2) 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.
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    7) 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.
    8) 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.
    9) 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.
    10) 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.
    11) 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.
    12) 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.
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