Asbestos

Introduction

Monitoring in the Environment

Exposure Pathway and Exposure Types

Metabolism of Asbestos

Biomarkers of Asbestos

Organs Affected by Asbestos

Molecular Action of Asbestos

Measuring Human Exposure

Risk Assessment

Epidemiological Studies

Toxicodynamics

Fate and Transport

What Everyone Should Know

Asbestos Policy

Regulatory Standards

Asbestos Removal and Sealing

References

Toxicodynamics of Asbestos


A number of animal and human studies have been conducted over the decades to investigate the toxicodynamics of asbestos. In generally, these studies can be classified into two categories:
1) Acute exposure: This type of study is based on animal experiments. They provide a reliable estimate about the rapid clearance of asbestos from the lungs.
2) Chronic exposure: This type of study has been done with both animal experiment and long-term follow-up on asbestos-exposed workers. They are useful for studying the slow clearance of asbestos from the lungs.

Different asbestos fibers can stay in the lungs with a highly variable time-span. The estimated half life T1/2 varies from minutes to years. Several investigators have used multi-compartment mathematical models to describe the dynamic behaviors of asbestos in the lung. A typical model may consist of 4 clearance compartments:
1) Fast clearance compartment: T1/2 = minutes to hours
2) Medium clearance compartment: T1/2 = days
3) Slow clearance compartment: T1/2 = months
4) Very-slow clearance compartment: T1/2 = years
The inter-relationship among the compartments is complex. One proposed diagram is illustrated below (Vincent et al. 1985):

The most consistent finding reported from the researches is that the highly variable clearance rates are related to the fiber’s physical characteristics (for example, see the following table; the half life T1/2 is estimated for the very-slow clearance compartment only; human data are used; Finkelstein and Dufresne 1999). The “rule of thumb” is that longer fibers have a longer half life (slower clearance rate) and that amphiboles have a longer half life than chrysotile.

Fiber Length Chrysotile Tremolite
<5_m T1/2=4 years T1/2=14 years
5-10_m` T1/2=6 years T1/2=16 years
>10_m T1/2=8 years T1/2=150

When human subjects are concerned, the very-slow clearance compartment is most important. Dose contributions from other faster clearance compartments are considered negligible. In this case, a simple mathematical expression can be written down:

Here is the amount of asbestos in the lungs, the deposition rate, the clearance rate, and the exposure duration. If the exposure time is sufficiently long, this equation predicts that a plateau will be reached. In available human-epidemiological data (Finkelstein and Dufresne 1999), such a plateau phenomenon is observed, but only transiently. Possible explanations for this inconsistency include incorrect exposure-history assessment (e.g., is not a constant and has decreased over time) and the existence of a very-very-slow clearance compartment (also see Finkelstein and Dufresne 1999 for more discussions).

If the exposure to asbestos was discontinued at time , the lung burden is then expected to decrease:

Here is the time since the exposure cessation (see the figure below; some human-epidemiological data reported by Finkelstein and Dufresne are also enclosed for comparison).










In summary, asbestos toxicodynamics are best described by a multi-compartment model although some discrepancy with available human data is noted and needs to be resolved with further investigation in the future.

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