Do vitreous fibers break in the lung?

In order to determine whether breakage of long vitreous fibers in the lung could be responsible for removing significant numbers of these fibers, an intratracheal instillation study was done with a preparation consisting of mostly long fibers of two different types. Following instillation of both fibers, laboratory rats were sacrificed at 6 times up to 14 days. The NK (conventional borosilicate glass) fiber preparation had about 20% short fibers (length < or = 15 microm) initially, and fibers recovered from the lungs remained at that proportion for the entire 14 days.

Fiber glass and rock/slag wool exposure of professional and do-it-yourself installers.

The fiber glass (FG) and rock/slag wool (RSW) manufacturers have developed a Health and Safety Partnership Program (HSPP) with the participation and oversight of the Occupational Safety and Health Administration (OSHA). Among its many provisions the HSPP includes the continuing study of FG and RSW workplace concentrations in manufacturing facilities operated by FG/RSW producers and among their customers and end users. This analysis estimates the probable cumulative lifetime exposure (fiber-months/cubic centimeter [f-months/cc]) to those who install FG and RSW insulation in residential, commercial, and industrial buildings in Canada and the United States.

Quantitative risk assessment of durable glass fibers.

This article presents a quantitative risk assessment for the theoretical lifetime cancer risk from the manufacture and use of relatively durable synthetic glass fibers. More specifically, we estimate levels of exposure to respirable fibers or fiberlike structures of E-glass and C-glass that, assuming a working lifetime exposure, pose a theoretical lifetime cancer risk of not more than 1 per 100,000. For comparability with other risk assessments we define these levels as nonsignificant exposures.

Estimating rock and slag wool fiber dissolution rate from composition.

A method was tested for calculating the dissolution rate constant in the lung for a wide variety of synthetic vitreous silicate fibers from the oxide composition in weight percent. It is based upon expressing the logarithm of the dissolution rate as a linear function of the composition and using a different set of coefficients for different types of fibers. The method was applied to 29 fiber compositions including rock and slag fibers as well as refractory ceramic and special-purpose, thin E-glass fibers and borosilicate glass fibers for which in vivo measurements have been carried out.

Estimation of dissolution rate from in vivo studies of synthetic vitreous fibers.

Although the dissolution rate of a fiber was originally defined by a measurement of dissolution in simulated lung fluid in vitro, it is feasible to determine it from animal studies as well. The dissolution rate constant for a fiber may be extracted from the decrease in long fiber diameter observed in certain intratracheal instillation experiments or from the observed long fiber retention in short-term biopersistence studies. These in vivo dissolution rates agree well with those measured in vitro for the same fibers.

Estimating in vitro glass fiber dissolution rate from composition.

A method is presented for calculating the dissolution rate constant of a borosilicate glass fiber in the lung, as measured in vitro, from the oxide composition in weight percent. It is based upon expressing the logarithm of the dissolution rate as a linear function of the composition. It was found that the calculated dissolution rate constant agreed with the measured value within the variation of the measured data in a set of compositions in which the dissolution rate constant ranged over a factor of 100.

Quantitative risk assessment for a glass fiber insulation product.

California Proposition 65 (Prop65) provides a mechanism by which the manufacturer may perform a quantitative risk assessment to be used in determining the need for cancer warning labels. This paper presents a risk assessment under this regulation for professional and do-it-yourself insulation installers. It determines the level of insulation glass fiber exposure (specifically Owens Corning's R-25 PinkPlus with Miraflex) that, assuming a working lifetime exposure, poses no significant cancer risk under Prop65's regulations.

Comparison of biopersistence of experimental glass fibres in the lung and peritoneal cavity.

Thirty three female Fischer-344 rats were intra-peritoneally (IP) injected with 5 mg of an experimental glass fibre designated X7753. This fibre type had an in vitro dissolution rate of 600 ng cm-2h-1. Groups of three rats were killed at various times up to one year after injection.

The durability and distribution of glass fibres in the rat following intra-peritoneal injection.

Intra-peritoneal (IP) injection is being recommended as a means of assessing potential carcinogenicity of MMF following inhalation. Little is known of the behaviour of fibres in the peritoneal cavity or its relevance to the lung. This study considered both the biopersistence and the distribution of dose following IP injection of fibres.

The behavior of glass fibers in the rat following intraperitoneal injection.

Potential carcinogenicity of fibers is believed to be determined by three factors: the dose, dimensions and durability of the fibers concerned. Currently there is considerable debate on the appropriateness of using results from intraperitoneal (i.p.

Role of fiber dissolution in biological activity in rats.

This report deals with the role of dissolution in removing long fibers from the lung and with a mathematical model that predicts chronic effects in rats following inhalation or intraperitoneal (i.p.) injection of fibers.

Biopersistences of man-made vitreous fibers and crocidolite fibers in rat lungs following short-term exposures.

Biopersistence of commercial man-made vitreous fibers (MMVF) and crocidolite were studied in Fischer 344 rats. MMVF used were size-selected to be rat-respirable, and rats were exposed nose-only 6 h/day for 5 days to gravimetric concentrations (30 mg/m3) of two fiber glass compositions--a rockwool, and a slagwool--or to 10 mg/m3 of long-fibered crocidolite, or to filtered air. Animals were sacrificed at 1 hr, 1, 5, 31, 90, 180, 270, 365, and 545 days after exposure stopped.