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Exposure dermal

Blepharopigmentation with Al-silicate has been introduced during the last decade as a technique for creating a permanent line along the eyelid margin, thus simulating a cosmetic eyeliner. Patients can have a delayed hypersensitivity granulomatous reaction [179]. [Pg.32]

Dermal persperants in a preliminary study the dermal absorption of Al from antiperspirants have been estimated to be 0.03-4 pg/L, or 0.012% in one study. The clinical significance is unknown [180], [Pg.32]

Vaccins adjuvants the purpose of a vaccine adjuvant is to enhance the immune response of the vaccine. An adjuvanted vaccine will tend to have a higher, earlier, and longer-lasting immune response than a non-adjuvanted vaccine. Until recently, the only vaccine adjuvants approved for human use [Pg.32]


Eye and Skin Contact. Some nickel salts and aqueous solutions of these salts, eg, the sulfate and chloride, may cause a primary irritant reaction of the eye and skin. The most common effect of dermal exposure to nickel is allergic contact dermatitis. Nickel dermatitis may occur in sensitized individuals following close and prolonged contact with nickel-containing solutions or metallic objects such as jewelry, particularly pierced earrings. It is estimated that 8—15% of the female human population and 0.2—2% of the male human population is nickel-sensitized (125). [Pg.13]

Fig. 3. Schematic representation showing the anatomical basis for differences in the quantitative supply of absorbed material to the Hver. By swallowing (oral route), the main fraction of the absorbed dose is transported direcdy to the Hver. FoUowing inhalation or dermal exposure, the material passes to the pulmonary circulation and thence to the systemic circulation, from which only a portion passes to the Hver. This discrepancy in the amount of absorbed material passing to the Hver may account for differences in toxicity of a material by inhalation and skin contact, compared with its toxicity by swallowing, if metaboHsm of the material in the Hver is significant in its detoxification or metaboHc activation. Fig. 3. Schematic representation showing the anatomical basis for differences in the quantitative supply of absorbed material to the Hver. By swallowing (oral route), the main fraction of the absorbed dose is transported direcdy to the Hver. FoUowing inhalation or dermal exposure, the material passes to the pulmonary circulation and thence to the systemic circulation, from which only a portion passes to the Hver. This discrepancy in the amount of absorbed material passing to the Hver may account for differences in toxicity of a material by inhalation and skin contact, compared with its toxicity by swallowing, if metaboHsm of the material in the Hver is significant in its detoxification or metaboHc activation.
Methylenedianiline (MDA) 50 pmol total MDA/mol creatinine in urine (BGV) Post shift for inhalation and pre-shift next day for dermal exposure... [Pg.90]

EH 74/3 Dermal exposure to non-agricultural pesticides exposure assessment document... [Pg.574]

In addition, the use of chemical protective clothing was not supported by air or surface contamination monitoring to determine the potential for dermal exposure and the appropriate PPE. [Pg.190]

Very few data are available on the effects of organotins in humans. Of the reported unintentional occupational exposures, none has an estimate of exposure concentration. Exposure was largely via the inhalation route, with some possibility of dermal exposure. Neurological effects were the most commonly reported, and these can persist for long periods. [Pg.5]

Dermal exposure of rats to doses of dimethyltin dichloride at 80 mg/kg body weight produced dermal necrosis with the formation of black scars the same dose of dibutyltin dichloride produced little surface damage to the skin together with subcutaneous oedema. Dioctyltin dichloride produced no skin lesions (Barnes Stoner,... [Pg.21]

Dermal exposure to methyl parathion is not likely to be a health concern to the general population, with the possible exception of individuals in the immediate vicinity of a field during application of the pesticide. Dermal exposure, however, is a major source of exposure for workers directly involved in the manufacture, application, and cleanup of the chemical, and for field workers. Laundry workers cleaning the clothing of such workers may also be exposed. [Pg.32]

Estimates of exposure levels posing minimal risk to humans (Minimal Risk Levels or MRLs) have been made for methyl parathion. An MRL is defined as an estimate of daily human exposure to a substance that is likely to be without an appreciable risk of adverse effects (noncarcinogenic) over a specified duration of exposure. MRLs are derived when reliable and sufficient data exist to identify the target organ(s) of effect or the most sensitive health effect(s) for a specific duration within a given route of exposure. MRLs are based on noncancerous health effects only and do not consider carcinogenic effects. MRLs can be derived for acute, intermediate, and chronic duration exposures for inhalation and oral routes. Appropriate methodology does not exist to develop MRLs for dermal exposure. [Pg.40]

Death from a combination of inhalation and dermal exposures has been reported by Fazekas (1971) in four individuals who used methyl parathion (Wofatox) spray in a careless manner. These individuals were part of a larger series of 30 cases (20 men, 10 women) of fatal methyl parathion intoxication reported by Fazekas (1971). Since 26 of these fatalities followed oral exposure, this report is discussed in detail in Sections 3.2.2.1 and 3.2.2.2. [Pg.41]

Death in humans related to a combination of inhalation and dermal exposure was discussed in Sections 3.2.1.1 and 3.2.2.1. [Pg.76]

No studies were located in humans or animals regarding respiratory, gastrointestinal, hematological, musculoskeletal, hepatic, or renal effects after dermal exposure to methyl parathion. [Pg.78]

No studies were located regarding dermal effects in animals after dermal exposure to methyl parathion. [Pg.78]

Although the extent of absorption was not measured, the above evidence suggests that absorption in humans occurs rapidly following dermal exposure to commercial pesticide formulations of methyl parathion. [Pg.89]

There is limited information available regarding the distribution of methyl parathion after dermal exposure in humans. Two subjects, dermally exposed to methyl parathion, had 2.74 and 1.23 mg on their hands. Twenty-four hours after exposure, the serum levels were 0.027 and 0.032 mg/L, respectively (Ware et al. 1973). Twelve hours after cotton fields were sprayed, five men entered the treated fields for 5 hours. An average of 1.7 mg methyl parathion was detected on their hands. Serum concentrations averaged 0.156 mg/L in these subjects after 3 hours of exposure. Levels decreased to 0.1 and 0.002 mg/L at 2 and 24 hours postexposure, respectively (Ware et al. 1975). Although 0.5 mg methyl parathion was detected on the hands of four subjects, none was found in the serum (Ware et al. 1974). No information on the tissue distribution of methyl parathion in humans was found. [Pg.91]


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