TOXICOLOGY 1153
TABLE 1
Some common references on environmental and occupational toxicology
Klaassen CD (1996), Casarett and Doulls Toxicology:
the basic science of poisons
An excellent reference on toxicology, although generally written at the
graduate level.
ACGIH® (2004), TLV’s and BEI’s Threshold limit values (TLVs) and biological exposure indices (BEIs) values,
which provide the upper exposure limit for many chemicals.
Hathaway et al. (1991), Proctor and Hughes’ chemical hazards of
the workplace
Provides information on many chemicals—including regulatory exposure
limits and basic information on the chemical.
OSHA (29 CFR 1910. 1000) Permissible exposure limits (PELs), which are the maximum exposure limit
set by the U.S. government.
NIOSH Criteria Documents Information on a specific chemical as provided by NIOSH. However, these
reports are not updates and some that are older will not have the most
up-to-date information.
Niesink et al. (1995), Toxicology: principles and applications General toxicology reference that focuses on the occupational environment.
Lippmann (1992), Environmental toxicants: human exposures and their
health effects
Provides information through chapters on specific topics that relate to both
environmental and occupational toxicology.
Rand and Petrocelli (1985), Fundamentals of aquatic
toxicology: methods and applications
A good basic textbook on aquatic toxicology.
NIOSH (1994), NIOSH pocket guide to hazardous chemicals Provides exposure values, physical properties, and keywords on health
hazards for many chemicals of industrial interest.
ACGIH ® —American Conference of Governmental Industrial Hygienists
OSHA—U.S. Occupational Safety and Health Administration
NIOSH—National Institute for Occupational Safety and Health (an example of these documents is NIOSH, Criteria for recommended standard
occupational exposure to hydrogen fluoride, Department of Health and Human Services (DHHS) (NIOSH) Pub Nos. 76–141)
the same organism. This is illustrated by the chemical copper
for Strongylocentrotus purpuratus using the endpoint EC 50 ,
which is the median effective concentration (where 50% of
the organisms are affected at a given period of time). ED 50 is
the median exposure dose,^ which is the concentration in air
or water. The other commonly used endpoint of measure for
industrial (occupational) toxicology is the median lethal dose
(LD 50 ; again, this is a value where 50% of the organisms die at
the given concentration, assuming that the mean and median
values are equal, as in a normal curve, although used in more
studies to refer to the median concentration). Obviously the
LD 50 is not useful in setting occupational-exposure limits, but
provides a relative comparison for different chemicals. Similar
in nature to the LD 50 is the EC 50. Here the concentration has
to be in some unit of air or liquid (water) for the endpoint
to be measured. The variability for a chemical as related to
effective endpoints (dose) can be illustrated using copper in
aquatic organisms (Table 3). The LD 50 of copper for the vari-
ous organisms listed have a large variation (log order). This
variation is commonly observed when evaluating a chemi-
cal among different organisms and even the same organism
between laboratories.
A toxic response can be reported as any endpoint mea-
surement that is reproducible. This can include death, as rep-
resented by an LD 50 or another, such as a behavior endpoint
measurement, which could be an EC 50. When evaluating
TABLE 2
Some areas of toxicology
Environmental Concerned with effects on the environment, which can
be considered pollution. This can be further divided
into air, soil, and water systems. There can also be a
measurement on a species as well.
Forensic The occurrence of toxic effects on people and possibly
other organisms, such as livestock, that is in relation
to a crime.
Occupational Effects of chemicals or substances on those in the
working environment and industry.
Regulatory Effects of chemicals (may also be drugs) in regard to
the risk associated with the purposes or in some
cases prevention of that chemical’s use. This is
often associated with some regulation or law, like
the U.S. Clean Air Act (CAA).
Mechanistic Evaluates a chemical’s mechanism of action and how
this action causes a toxic effect on the organism.
TABLE 3
Aquatic toxicology values of various organisms for copper
Organism LD 50 Reference
Mesocyclops peheiensis 75 g/l Wong and Pak, 2004
Tilapia zillii 6.1 mg/l Zyadah and Abdel-
Baky, 2000
Mysis sp. (from Nile River) 2.89 mg/1 Zyadah and Abdel-
Baky, 2000
Mugil cephalus 5.3 mg/1 Zyadah and Abdel-
Baky, 2000
Photobacterium phosphoreum 100 mg/1 Thomulka
et al., 1993
Strongylocentrotus purpuratus 15.3 g/1 Phillips
et al., 2003
Penaes merguiensis 0.38 mg/1 Ahsanullah and Ying,
1995
^ An EC 50.
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