Bioassay
A bioassay is an analytical method to determine the potency or effect of a substance by its effect on living animals or plants (in vivo), or on living cells or tissues (in vitro).[1][2] A bioassay can be either quantal or quantitative, direct or indirect.[3] If the measured response is binary, the assay is quantal; if not, it is quantitative.[3]
A bioassay may be used to detect biological hazards or to give an assessment of the quality of a mixture.[4] A bioassay is often used to monitor water quality as well as wastewater discharges and its impact on the surroundings.[5] It is also used to assess the environmental impact and safety of new technologies and facilities.[citation needed]
Bioassays are essential in pharmaceutical, medical and agricultural sciences for development and launching of new drugs, vitamins, etc.
Principle
A bioassay is a biochemical test to estimate the potency of a sample compound. Usually this potency can only be measured relative to a standard compound.[3][1] A typical bioassay involves a stimulus (ex. drugs) applied to a subject (ex. animals, tissues, plants). The corresponding response (ex. death) of the subject is thereby triggered and measured.[6]
History
The first use of a bioassay dates back to the late 19th century, when the foundation of bioassays was laid down by German physician Paul Ehrlich.[7] He introduced the concept of standardization by the reactions of living matter.[7][6] His bioassay on diphtheria antitoxin was the first bioassay to receive recognition.[8] His use of bioassay was able to discover that administration of gradually increasing dose of diphtheria in animals stimulated production of antiserum.[9]
One well known example of a bioassay is the "canary in the coal mine" experiment.[10] To provide advance warning of dangerous levels of methane in the air, miners would take methane-sensitive canaries into coal mines. If the canary died due to a build-up of methane, the miners would leave the area as quickly as possible.
Many early examples of bioassays used animals to test the carcinogenicity of chemicals.[11] In 1915, Yamaigiwa Katsusaburo and Koichi Ichikawa tested the carcinogenicity of coal tar using the inner surface of rabbit's ears.[11]
From the 1940s to the 1960s, animal bioassays were primarily used to test the toxicity and safety of drugs, food additives, and pesticides.[11]
Beginning in the late 1960s and 1970s, reliance on bioassays increased as public concern for occupational and environmental hazards increased.[11]
Classifications
Bioassay can be classified by how it is applied and how the response is recorded.
- Direct assay
- In a direct assay, the stimulus applied to the subject is specific and directly measurable, and the response to that stimulus is recorded. The variable of interest is the specific stimulus required to produce a response of interest (ex. death of the subject).[6][12]
- Indirect assay
- In an indirect assay, the stimulus is fixed in advance and the response is measured in the subjects. The variable of interest in the experiment is the response to a fixed stimulus of interest.[6][12]
- Quantitative response
- The measurement of the response to the stimulus is on a continuous scale (ex. blood sugar content, degree of color change in cell growth medium).[12]
- Quantal response
- The response is binary; it is a determination of whether or not an event occurs (ex. death of the subject).[12]
Examples
One classical bioassay is the Ames test. A strain of Salmonella that requires histidine to grow is put on two plates with growth medium containing minimal amounts of histidine and some rat liver extract (to mimick liver metabolism). A suspected mutagen is added to one plate. If the plate with the suspected mutagen grows more visible colonies, it is probably mutagenic: a mutagen might cause the strain of bacterium to regain the ability to make its own histidine.[13]
Most other forms of toxicology testing are also bioassays. Animals or cell cultures may be put under a number of levels of a suspected toxin to ascertain whether the substance causes harmful changes and at what level it does so. The LD50 value, a common measure of acute toxicity, describes the dose at which a substance is lethal to 50% of tested animals.[14]
The potency of a drug may be measured using a bioassay.[15]
Environmental bioassays
Environmental bioassays are generally a broad-range survey of toxicity.[16] A toxicity identification evaluation is conducted to determine what the relevant toxicants are. Although bioassays are beneficial in determining the biological activity within an organism, they can often be time-consuming and laborious. Organism-specific factors may result in data that are not applicable to others in that species. For these reasons, other biological techniques are often employed, including radioimmunoassays. See bioindicator.
See also
References
- ^ PMID 14449182.
- ^ "Guidance for Industry: Potency Tests for Cellular and Gene Therapy Products". Washington, D.C.: U.S. Food and Drug Administration. January 2011. p. 7.
- ^ PMID 3579242.
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- ^ a b "Permit Limits-Whole Effluent Toxicity (WET)". National Pollutant Discharge Elimination System (NPDES). Washington, D.C.: U.S. Environmental Protection Agency (EPA). 2021-10-11.
- ^ a b c d Saha, G. M (29 November 2002). Design and Analysis for Bioassays. Kolkata: Indian Statistical Institute. pp. 61–76.
- ^ PMID 2488614.
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- ^ "Environmental Inquiry - How Are Bioassays Used in the Real World?". ei.cornell.edu. Retrieved 2017-12-01.
- ^ S2CID 2269998.
- ^ a b c d Le, Chap. "Direct Bioassays & Estimation of Ratios" (PDF). Retrieved 15 June 2021.
- ^ Charnley G (2002). "Ames Test". Encyclopedia of Public Health. eNotes.com. Archived from the original on 4 February 2009. Retrieved 2014-05-02.
- ^ "Absolute lethal dose (LD100)". IUPAC Gold Book. International Union of Pure and Applied Chemistry. Archived from the original on 2019-07-01. Retrieved 2019-07-01.
- PMID 30846752.
- S2CID 255473013.
- ^ Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms (Report). EPA. October 2002. EPA-821-R-02-012.
- ^ "Whole Effluent Toxicity Methods". Clean Water Act Analytical Methods. EPA. 2020-08-01.
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