This page outlines some of the basic principles of toxic exposure assessment. ATSDR
(U.S. Agency for Toxic Substances and Disease Registry) defines a toxic exposure as
"contact with a toxic substance by swallowing, breathing or touching the skin
or eyes. Exposure may be short-term [acute], of intermediate duration or long-term
[chronic]."1
The expert toxicologist's primary tasks are to (a) identify toxic substances and/or
chemicals of concern (COCs), (b) document and characterize the circumstances under
which exposure occurred, (c) identify the pathways, durations and conditions of
exposure and (d) determine the respective dosage of each chemical or substance.
This process is referred to as an exposure assessment. When exposed to
a toxic substance, the organ affected at the lowest dose is referred to as the
target organ.
Exposure Assessment in Toxicology
Exposure assessment is merely one step in a multi-step process called risk assessment.
Although the precise steps and methods vary according to the type and circumstances
of exposure, the underlying principles are the same. Whether the result establishes
(or refutes) an excessive blood-alcohol concentration in the driver of a motor vehicle,
or addresses a variety of substances over many years in an entire community, the
expert toxicologist must follow the same objective steps to arrive at scientifically credible
results which must fulfill the criteria of reasonable toxicological certainty.
Exposure assessment can be thought of as a process whereby the toxicologist calculates
the magnitude, frequency and duration of exposure to a toxic agent. As shown in
the chart to the right, this requires compiling sets of information which describe
exposure concentrations and intake variables to arrive at a pathway-specific exposure dose
for each substance. This means characterizing the sources, pathways and routes of
exposure as well as the number and characteristics of the person(s) exposed.
In addition, the expert toxicologist must take uncertainties into account. Many
factors must be identified and assessed (some of which may have occurred in the
distant past). Such an investigation may fall within the realm of forensic toxicology.
Thus, an exposure assessment measures (a) the dose of a toxic agent that was likely
to have been absorbed by an exposed individual or population, (b) the form of the
toxic agent, (c) the rate at which the agent was delivered, (d) how much of the
agent was actually available in the body to produce the biological effect(s) at
issue and (e) whether mitigating factors or uncertainties may have altered the outcome.
This method produces results which establish the path, transport and anticipated
effects of a toxic agent on a biological basis. If a well-documented and recognized
cause/effect relationship is demonstrated, this is referred to as a toxicological
endpoint.
Exposure Pathways
In reviewing a case, the expert toxicologist may find that the route(s) of exposure
are self-evident. For example, acute ingestion of a poison, drinking contaminated water or
acute inhalation of toxic fumes are often singular events. These can usually be assessed
by applying direct dose calculations to established dose-response relationships.
However, widespread environmental contamination, particularly cases involving the
release of several toxic substances (sometimes over a period of many years) creates a vastly more complicated situation.
In such cases, contamination by (for example) dioxin, trichloroethylene or LNAPL may
involve contamination in the air, soil, drinking water, food, dust, etc. In
these cases, there are many mechanisms for oral, dermal and inhalation uptake with
chemical-specific exposures through multiple pathways.
Thus, the toxicologist must first assess the possible routes of exposure by seeking
answers to environmental considerations:
- Inhalation: Was the contaminant inhaled or persistent in fine-particle
respirable dust within the environment?
- Dermal Absorption: Was the contaminant absorbed through the skin?
- Ingestion: Was the contaminant ingested through food, drinking, dust,
hand-to-mouth behavior, etc.?
Multiple Pathways
In some cases, a primary route of exposure may not be immediately obvious. For example,
trichloroethylene (TCE) can be ingested by drinking contaminated water. However,
TCE also readily vaporizes and as such, it can be inhaled from hot shower steam
and other household sources. TCE can also be absorbed through the skin while swimming
or washing.2 Even inhaling TCE vapors when opening
the lid of a washing machine can resuly in a significant quantified dose if the
concentration is sufficiently high and if performed with sufficient frequency. These
examples underscore the potential complexity of a toxic exposure assessment in a
widespread contamination scenario.
Calculating Cumulative Exposure
In the illustration below, TCAS calculated TCE concentrations over time
for residents who were exposed through inhaling TCE vapors while showering (among
several exposure pathways). As each person aged, they fell into a different group
with a different dose absorption factor corresponding to their body weights, water
evaporation rates and inhalation rates. Thus, each individual had to be treated
as "several" individuals at different points in time. The resulting sums
of dosages were then applied to different exposure periods to arrive at a resulting
"cumulative inhalation dose" which is itself merely one ledger item in
a longer series of additive doses.
Although this illustration demonstrates how such calculations may be performed in
a community-exposure scenario, it should be noted that this is merely one page from
a much longer set of calculations detailing other routes of exposure (water ingestion,
dermal absorption, etc.). However, this methodology typifies the requirements imposed
upon the expert toxicologist when conducting an exposure assessment in a widespread
contamination scenario. Thus, the toxicologist's role is to apply the concise methods
necessary to delineate exposure conclusions to reasonable toxicological certainty.
Summary
The general information presented herein serves to illustrate the fact that
organizing a toxic exposure assessment on the basis of the exposure circumstances
is just as important as performing the exposure calculations themselves. U.S. EPA's
Exposure Factors Handbook3 provides a wealth of information
regarding methods for applying generally-accepted default values to compile pathway-specific
exposure data. This is extremely helpful when investigating and objectively assessing
the relevant factors governing the possible exposure pathways including whether
exposures occurred simultaneously or at different times. Uncertainties, other possible
contamination sources and any relevant historical data should also be taken into
account.
When all of the exposure points have been identified and fully characterized, the
toxicologist applies a set of generally-accepted equations to the variables (as
guided by U.S. EPA, RECAP or other regulatory body). This methodological approach
allows all exposure pathways to be quantified with respect to exposure concentrations
and their related intake levels and cumulative dose. This is the last step in
the toxic exposure assessment process. Each exposure pathway must be fully
documented and the resulting concentrations applied using generally-accepted, peer-reviewed
calculation methods.
Thus, through a meticulous process with concise attention to detail, the expert toxicologist
compiles scientifically credible, pathway-specific exposure data. Although pure reasoning
can assist in interpreting results, reasonable toxicological certainty
is largely subordinated to the weight of objective evidence. There should be few
(if any) a priori4 determinations in a well-constructed
toxic exposure assessment.
Toxic Substances
The universe of toxic substances is vast as there are more than 7 million recognized
chemicals in existence. The U.S. General Accounting Office (GAO) references approximately
80,000 chemicals used on a regular basis.5 The US
Agency for Toxic Substances and Disease Registry (ATSDR) has published a large body
of information covering a wide range of toxic substances.6
Armed with the enormous body of toxicological literature and guided by generally-accepted,
peer-reviewed methods, the expert toxicologist's goal is to identify and characterize
the circumstances of exposure, identify the exposure pathways and determine the
dosage of each chemical or substance.
For more than 34 years, TCAS has been retained to perform investigative
assessments of toxic exposures. We have conducted exposure assessments for a wide
variety of substances under many different circumstances. Some of these can be reviewed
in our
areas of specialization and in our case studies. This website provides
reference information for six (6) classes of toxic substances with which TCAS
has extensive professional experience. Click on your particular area of interest
to view additional information.
Notes and References
- Agency for Toxic Substances and Disease Registry, "Health Effects
of Exposure to Substances and Carcinogens (Glossary)"
- U.S. Environmental Protection Agency, "Chemical Summary, TCE"
- U.S. Environmental Protection Agency, "Environmental
Assessment, Exposure Factors Program "
- a priori; A type of conclusion which favors pure reason or intuition
over objective evidence.
- General Accounting Office, "1994b. Toxic Substances Control Act," Federal Register, 1994
- ATSDR, Division of Toxicology and Environmental Medicine, "Toxic Substances," Evaluations of hazardous substances and their potential health effects (2013)
Images
- Graphical image © Copyright 2023 TCAS, LLC. Adapted from
U.S. EPA Exposure Factors Handbook
- TCAS report demonstrative (redacted), graphical image © Copyright 2023 TCAS, LLC.
- TCAS report demonstrative (redacted), graphical image © Copyright 2023 TCAS, LLC.
- Risk assessment report table (redacted), graphical image © Copyright 2023 TCAS, LLC.
- Thumbnail images from multiple sources as noted on referenced pages.