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Insoluble dusts

The upper and lower respiratory tracts respond differently to the presence of toxicants. The upper respiratory tract is affected mostly by toxicants that are water soluble. These materials either react or dissolve in the mucus to form acids and bases. Toxicants in the lower respiratory tract affect the alveoli by physically blocking the transfer of gases (as with insoluble dusts) or reacting with the wall of the alveoli to produce corrosive or toxic substances. Phosgene gas, for example, reacts with the water on the alveoli wall to produce HC1 and carbon monoxide. [Pg.38]

Morrow PE, Gibb FR, Johnson L. 1964. Clearance of insoluble dust from the lower respiratory tract. Health Phys 10 543-555. [Pg.120]

For regulatory purposes, the Occupational Safety and Health Administration (OSHA 1992) concluded that there was insufficient evidence that nonasbestiform forms of tremolite, actinolite, and anthophyllite will produce adverse health effects of the same type and severity produced by chronic exposure to amphibole asbestos (OSHA 1992 Vu 1993). Nevertheless, the reader should be aware that repeated exposure to excessive amounts of insoluble dusts of any type can cause adverse health effects including interstitial pulmonary fibrosis (ACGIH 1996 OSHA 1992). [Pg.386]

The carcinogenicity of nickel compounds in industrial workers has been comprehensively reviewed in several publications (6,7,8,9,10). Increased incidences of cancer of the lung and nasal cavities have been documented by epidemiological investigations of nickel-refinery workers in Wales (11,12), Canada (13,14), Norway (15), and Russia (16). The identity of the nickel compounds that induce cancers in nickel-refinery workers remains uncertain although principal attention has been focused upon (a) insoluble dusts of nickel subsulfide (Ni3S2) and nickel oxides (NiO Ni203), (b) the vapor of nickel carbonyl (Ni(CO)4) and, (c) soluble aerosols of nickel sulfate, nitrate, or chloride (8,10,17). [Pg.74]

Inclusions of insoluble dust minerals (CaC03, Fe203, etc.) can increase the efflorescence RH of salts (Martin 2000). For example, for (NH4)2S04, the ERH can increase from 35% to 49% when CaC03 inclusions are present. These mineral inclusions provide well ordered atomic arrays and thus assist in the formation of crystals at higher RH and lower solution supersaturations. Soot, on the other hand, appears not to be an effective nucleus for crystallization of salts because it does not contain a regular array of atoms that can induce order at least locally in the aqueous medium (Martin 2000). [Pg.461]

The whole of the bronchial system is lined with hairs, known as cilia. The cilia offer some protection against insoluble dusts. These hairs will arrest all non-respirable dust (above 5 xm) and, with the aid of mucus, pass the dust from one hair to a higher one and thus bring the dust back to the throat. (This is known as the ciliary escalator). It has been shown that smoking damages this action. The nose will normally trap large particles (greater than 20 pm) before they enter the trachea. [Pg.280]

Another way of approaching the problem is to put the lung into overload, which for convenience, can be defined as a situation in which administration of sufficiently high loads of nontoxic insoluble dusts produces marked prolongation or even total failure of macrophage-mediated particle clearance (reviewed in 41,91). The mechanism of the overload effect is not entirely understood (see 91-94 for comments), but it is clear that, under overload conditions, the burden of free particles in the alveoli, the number of particles that are taken up by epithelial cells, and the number of particles translocated to the interstitium, all are greatly increased (41,91). [Pg.408]

C. Insoluble in water, soluble in organic solvents. Flavone occurs naturally as dust on the flowers and leaves of primulas. It has been prepared from o-hydroxyacetophenone and benzaldehyde. [Pg.176]

Before polyacrylamides are sold, the amount of residual acrylamide is determined. In one method, the monomer is extracted from the polymer and the acrylamide content is determined by hplc (153). A second method is based on analysis by cationic exchange chromatography (154). For dry products the particle si2e distribution can be quickly determined by use of a shaker and a series of test sieves. Batches with small particles can present a dust ha2ard. The percentage of insoluble material is determined in both dry and emulsion products. [Pg.144]

It is good practice to keep concentrations of airborne nickel in any chemical form as low as possible and certainly below the relevant standard. Local exhaust ventilation is the preferred method, particularly for powders, but personal respirator protection may be employed where necessary. In the United States, the Occupational Safety and Health Administration (OSHA) personal exposure limit (PEL) for all forms of nickel except nickel carbonyl is 1 mg/m. The ACGIH TLVs are respectively 1 mg/m for Ni metal, insoluble compounds, and fume and dust from nickel sulfide roasting, and 0.1 mg/m for soluble nickel compounds. The ACGIH is considering whether to lower the TLVs for all forms of nickel to 0.05 mg/m, based on nonmalignant respiratory effects in experimental animals. [Pg.14]

Handling of soluble uranium compounds requires appropriate clothing to prevent skin contact and eye protection to prevent any possible eye contact. Protective clothing requirements for insoluble uranium compounds should prevent repeated or prolonged skin contact. Eye protection for use in handling insoluble uranium compounds should prevent any possibiUty of eye contact. Respirators should always be worn to prevent inhalation of uranium dust, fumes, or gases (38). [Pg.189]

Health and Safety Factors. Terephthahc acid has a low order of toxicity. Inhalation by rats for 6 h/d, 5 d/wk for 4 wk produced no fatahties at a dust exposure level of 25 mg/m. The mean acute oral toxicity for rats is over 18 g/kg (86), and for mice over 6 g/kg (87). When terephthahc acid was fed as 3% of the diet to rats, urinary calcuh formed in 90 d, some of which led to cancer. High doses of terephthahc acid lead to formation of calcium terephthalate at levels exceeding its solubihty in urine. This insoluble material leads to the calcuh and provides a threshold below which cancer is not observed (88). Normal precautions used in handling industrial chemicals should be observed with terephthahc acid. If ventilation is inadequate, a toxic-dust respirator should be used to avoid prolonged exposure. [Pg.491]

Production and Economic Aspects. Thallium is obtained commercially as a by-product in the roasting of zinc, copper, and lead ores. The thallium is collected in the flue dust in the form of oxide or sulfate with other by-product metals, eg, cadmium, indium, germanium, selenium, and tellurium. The thallium content of the flue dust is low and further enrichment steps are required. If the thallium compounds present are soluble, ie, as oxides or sulfates, direct leaching with water or dilute acid separates them from the other insoluble metals. Otherwise, the thallium compound is solubilized with oxidizing roasts, by sulfatization, or by treatment with alkaU. The thallium precipitates from these solutions as thaUium(I) chloride [7791 -12-0]. Electrolysis of the thaUium(I) sulfate [7446-18-6] solution affords thallium metal in high purity (5,6). The sulfate solution must be acidified with sulfuric acid to avoid cathodic separation of zinc and anodic deposition of thaUium(III) oxide [1314-32-5]. The metal deposited on the cathode is removed, kneaded into lumps, and dried. It is then compressed into blocks, melted under hydrogen, and cast into sticks. [Pg.467]

Fully cured polyurethanes present no health ha2ard they are chemically inert and insoluble in water and most organic solvents. However, dust can be generated in fabrication, and inhalation of the dust should be avoided. Polyether-based polyurethanes are not degraded in the human body, and are therefore used in biomedical appHcations. [Pg.353]

In humans, inhaled insoluble barium salts are retained in the lung (47,49). Inhalation of high concentrations of the fine dusts of barium sulfate can result in the formation of harmless nodular granules in the lungs, a condition called baritosis (49). Baritosis produces no specific symptoms and no changes in pulmonary function. The nodulates disappear upon cessation of exposure to the barium salt. However, it is possible that barium sulfate may produce benign pneumoconiosis because, unlike barium carbonate, barium sulfate is poorly absorbed (21). [Pg.483]

The bacterial culture converts a portion of the supplied nutrient into vegetative cells, spores, crystalline protein toxin, soluble toxins, exoenzymes, and metabolic excretion products by the time of complete sporulation of the population. Although synchronous growth is not necessary, nearly simultaneous sporulation of the entire population is desired in order to obtain a uniform product. Depending on the manner of recovery of active material for the product, it will contain the insolubles including bacterial spores, crystals, cellular debris, and residual medium ingredients plus any soluble materials which may be carried with the fluid constituents. Diluents, vehicles, stickers, and chemical protectants, as the individual formulation procedure may dictate, are then added to the harvested fermentation products. The materials are used experimentally and commercially as dusts, wettable powders, and sprayable liquid formulations. Thus, a... [Pg.70]

A small flux is shown between the land and atmosphere. This represents the transport of dust particles to the atmosphere (F28) and the deposition of these particles back on land either as dry deposition or associated with atmospheric precipitation (F82). Similarly, fluxes that represent the transport of seasalt from the surface ocean to the atmosphere (Fss) and the deposition of soluble (F85) and insoluble (F81) atmospheric forms are also shown. As already discussed for the river fluxes, the insoluble particulate flux is represented as a direct transport of P to the sediment reservoir. [Pg.370]


See other pages where Insoluble dusts is mentioned: [Pg.409]    [Pg.455]    [Pg.455]    [Pg.409]    [Pg.91]    [Pg.409]    [Pg.296]    [Pg.543]    [Pg.280]    [Pg.409]    [Pg.455]    [Pg.455]    [Pg.409]    [Pg.91]    [Pg.409]    [Pg.296]    [Pg.543]    [Pg.280]    [Pg.391]    [Pg.123]    [Pg.527]    [Pg.134]    [Pg.336]    [Pg.1594]    [Pg.15]    [Pg.180]    [Pg.220]    [Pg.221]    [Pg.488]    [Pg.50]    [Pg.123]    [Pg.76]    [Pg.82]    [Pg.55]    [Pg.31]    [Pg.93]    [Pg.22]   
See also in sourсe #XX -- [ Pg.408 ]




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