i. Introduction to Toxicology
Toxicology is defined as the study of chemical or physical agents which
interact with biologic systems to produce a response in the organisms.
Toxicity is the relative ability of a substance to cause injury to biologic
tissue. Given the broad range of toxicities any substance might eventually
invoke in an organism, it is easy to understand the wisdom of Paracelsus
(1493-1541) when he said, All substances are poisons; there is
none which is not a poison. The right dose differentiates a poison and
a remedy.
The dose determines if the effects of any substance are toxic, non-toxic,
or beneficial. Dose is the quantity of a substance to which an organism
is exposed. In toxicological studies, the dose given to test animals
is expressed in terms of quantity administered:
• Per unit weight, usually expressed as milligrams of substance
per kilogram of body weight (mg/kg).
• Per area of skin surface, also expressed as mg/kg.
• Per unit volume of air inhaled, usually expressed as parts of
vapor or gas per million parts (ppm) of air by volume. Solids would
be expressed as milligrams of material per cubic meter of air (mg/m3).
Inhaled doses can also be expressed by time.
ii. Toxicity Tests
The design of any toxicity test incorporates selection of:
• A test organism, which can range from cellular material and
selected strains of bacteria through higher order plants and animals.
• The response or biological endpoint, which can range from subtle
changes in physiology and behavior to death.
• An exposure or test period.
• Dose or series of doses.
The objective is to select a test species that is a good model of humans,
a response that is not subjective and can be consistently determined,
and a test period that is relatively short. Often tests must be selected
that yield indirect measurements or responses that supposedly correlate
well with the response of interest — for example, determining
carcinogenic potential by measuring mutagenic potential.
iii. Dose-Response Relationship
A particular toxicity test exhibits a dose-response relationship when
there is a consistent mathematical relationship between the proportion
of individuals responding and a given dose for a given exposure period.
For example, the number of mortalities increases as the dose of chemical
given to a group of organisms increases.
Measurement of Response
Different species of test organisms differ in how they respond to a
specific chemical. In addition, there are variations in response to
a given dose within a group of test organisms of the same species. Typically,
this intraspecies variation follows a normal (Gaussian) distribution
when the number of organisms responding is plotted against the degree
of response for a given dose.
Several basic relationships can be readily identified from the plots.
A dose is often described as either a lethal dose (LD) in a test where
the response is mortality, or effective dose (ED) in a test where the
response is some other observable effect.
Constructing an ultimate dose-response curve enables the identification
of doses which affect a given percent of the exposed population, e.g.,
the LD50 is that dose which is lethal to 50 percent of the test organisms.
Dose-Response Terms
The National Institute for Occupational Safety and Health (NIOSH) defines
a number of dose-response terms:
• Lethal dose fifty (LD50) calculated dose of a substance which
is expected to cause the death of 50 percent of an entire defined experimental
animal population.
• Lethal dose low (LDLo) The lowest dose of substance introduced
by any route other than inhalation which has been reported to have caused
death in humans or animals.
• Toxic dose low (TDLo): The lowest dose of a substance introduced
by any route other than inhalation, over any given period of time, and
reported to produce any toxic effect in humans or carcinogenic, neoplastigenic,
or teratogenic effects in animals or humans.
• Toxic concentration low (TCLo) The lowest concentration of a
substance in air to which humans or animals have been exposed for any
given period of time that has produced any toxic effect in humans or
carcinogenic, neoplastigenic, or teratogenic effects in animals or humans.
• Lethal concentration low (LCLo): The lowest concentration
of a substance in air which has been reported to have caused death in
humans or animals.
Use of Dose-Response Relationship
Comparing the LD50 of chemicals in animals gives a relative ranking
of acute toxicity of each. For example, DDT (LD50 for rats = 113 mg/kg)
would be considered more toxic than ethyl alcohol (LD50 for rats = 1400
mg/kg). Using this LD50 (mg/kg) and multiplying by 70 kg (average mass
of human) gives a rough extrapolation to humans, assuming they are as
sensitive as the species tested to the substance tested. However,
LD50 serves only as a rough estimate of one aspect of the toxic potential
of a substance.
TOXICITY
RATING CHART (oral) |
|
| Toxicity Rating | Oral Acute LD50 for Rats |
| Extremely toxic | 1 mg/kg or less (e.g., dioxin, butulin toxin) |
| Highly toxic | 1 to 50 mg/kg (e.g., strychnine) |
| Moderately toxic | 50 to 500 mg/kg (e.g., DDT) |
| Slightly toxic | 0.5 to 5 gm/kg (e.g., morphine) |
| Practically nontoxic | 5 to 15 gm/kg (e.g., ethyl alcohol) |
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