Occupational toxicology is the application of toxicology to chemical hazards in the workplace. It focuses on substances and conditions that people may be exposed to in workplaces, including inhalation and dermal exposures, which are most prevalent when discussing occupational toxicology. These environmental and individual exposures can impact health, and there is a focus on identifying early adverse affects that are more subtle than those presented in clinical medicine.
Occupational toxicology interfaces heavily with other subfields of occupational safety and health. Occupational epidemiology studies may inspire toxicological study of causative agents, and toxicological investigations are important in establishing biomarkers for workplace health surveillance. Occupational toxicology studies may suggest or evaluate hazard controls used by industrial hygienists. Toxicological studies are also an important input for performing occupational risk assessment, and establishing standards and regulation such as occupational exposure limits.
As of 1983, around 60,000 chemical compounds were considered to be of occupational consequence. [1] Certain sectors have an increased potential for exposure to chemical and biological agents, including manufacturing, construction, mining, logging, and agriculture, as well as service sector workplaces such as in automobile repair, gasoline stations, pipelines, truck and rail transportation, waste management and remediation, and botanical gardens. [2] These sectors contain an increased risk of exposure largely due to the fact that they are working with heavy machinery that can emit potentially harmful fumes when being operated. [3] Additionally, these sectors involve directly handling various substances that can possibly contain harmful chemical compounds.
Toxicological studies are experimental laboratory studies on the response of organisms and biological pathways to a substance, and can generate data that are used for other occupational safety and health activities. [4] These studies can range anywhere from 2 weeks to 2 years and primarily focus on determining whether or not the compound is toxic/carcinogenic and how toxic it is if so. [5] To discover if a compound is toxic/carcinogenic, toxicologists expose mice to the compound being studied and examine them over a given amount of time. These toxicologists then look for any patterns in the mice that may suggest toxicity or carcinogenicity and draw a conclusion from this data.
Occupational toxicology generates data that is used to identify hazards and their physiological effects, and quantify dose–response relationships. [4] A major use of this data is for establishing standards and regulation. These may take the form of occupational exposure limits, which are based on ambient concentration levels of toxicants. They also include biological exposure indices, which are based on biomonitoring of a toxicant, its metabolites, or other biomarkers. [2] Toxicologists have a large role in determining what biomarkers may be used for biomonitoring during exposure assessment and workplace health surveillance activities. [4]
Occupational toxicology is complementary to occupational epidemiology, to a greater degree than toxicology and epidemiology in general. For example, outbreaks identified through epidemiological studies such as exposure assessment case studies or workplace health surveillance may inspire toxicological study of suspected or confirmed causative agents. [1] [2] Conversely, the results of toxicological investigation are important in establishing biomarkers for workplace health surveillance to identify overexposure and to test the validity of occupational exposure limits. These biomarkers are intended to aid in prevention by identifying early adverse affects, unlike diagnostics for clinical medicine that are designed to reveal advanced pathological states. [2]
Toxicological studies have the benefit over epidemiology that they can study new substances before there is exposure in commerce, [2] or when epidemiological data are not available. [4] Toxicology also has the advantage of elucidating not only overt health outcomes, but intermediate biochemical steps such as biotransformation processes, as well as early cellular changes. These can aid in developing measures to prevent or treat toxicity. [4]
Occupational toxicology studies may also suggest or evaluate hazard controls used by industrial hygienists. [1]
Occupational toxicology differs from environmental toxicology in that the former has smaller number of exposed individuals, but with a wider range of exposure levels. Environmental toxicology tends to focus on situations with low exposure levels for larger numbers of people, where adverse effects may be concentrated in people who are especially susceptible to a given toxicant due to genetic or other factors. [6]
Occupational toxicology has the challenge of performing studies that mimic actual workplace conditions, for which inhalation exposure and dermal exposure are most important, [1] [2] although in medical industries, injection exposure through needlestick injuries is a hazard. [4] In particular, experimental inhalation exposure studies require more complex methodology and equipment than for oral administration experiments. For example, measurement and control of particle size distribution is important, and the degree and location of particle retention within the respiratory tract. [2] Inhalation and injection exposure are often more dangerous than dermal exposure, where a major function of skin is to provide a barrier to outside toxins, and ingestion exposure, where toxins may be broken down by the gastrointestinal tract and liver. [4]
There is often exposure to mixtures of chemicals, whose effects may not be simply additive, as different toxins may interact in a way that enhances or reduces their toxicity relative to each toxin alone. [4] Mixtures may include undesired contaminants in a product, or products that deviate from manufacturer specifications. Exposures are not always acute, but may be at low levels prolonged over decades. [2] Workers may be exposed to toxic substances at higher levels than the general public, who are mainly exposed through consumer products and the environment. [7] Establishing a causal relationship between a worker's illness and work conditions is often difficult because work-related illnesses are often indistinguishable from those with other causes, and there may be a long interval between the exposure and the onset of disease. [2]
While the dose of a toxicant is a strong predictor of health outcomes, occupational diseases are often influenced or confounded by other environmental factors, or personal host factors such as preexisting health conditions, host genetics, or patterns of worker behavior. These affect the relationship between the concentration, duration, and frequency of the exposure, and the actual toxicant dose that reaches a target tissue and interacts with metabolic processes. For example, the ultimate dose from inhalation exposure depends on respiratory rate and breathing volume, and the dose from dermal exposure depends on the absorption rate through the skin, which is influenced by the chemical properties of the chemical, the thickness of the skin at the exposed location on the body, and whether the skin is intact. [2]
Occupational toxicology uses methods common to other forms of toxicology. Animal testing is used to identify adverse effects and establish acceptable exposure levels, as well as studying the mechanism of action and dose–response relationship. There are a number of in vitro alternatives to animal testing in a number of specific cases such as predicting skin sensitizers and potential for eye injuries, as well as quantitative structure–activity relationship models. Sometimes, controlled human challenge studies are performed in cases where the risk for volunteers is negligible; these are used to verify whether results from animal studies translate to humans. [2]
Many types of measurements may be made in occupational toxicology. These include external measurements of exposure, the internal dose measured via tissues and bodily fluids, the "biologically effective dose" measuring the compound that has actually interacted with host biomolecules such as DNA and proteins, and measuring downstream effects of mutations, cytogenetic effects, and aberrant gene expression. [8] Experimentation may focus on the operation and regulation of biotransformation processes that may detoxify or activate toxins. These processes are subject to difference between individuals, which is studied through the field of toxicogenomics. [4]
While the health hazards of substances used in the workplace have been recognized since antiquity, the first experimental studies of hazardous substances came in the late 19th and early 20th centuries, including the work of John Scott Haldane on mine gases, Karl Bernhard Lehmann on organic substances, and Ernest Kennaway on occupational skin cancer. [9]
Biomarkers began to be used in occupational toxicology and epidemiology in the 1970s, and the 1990s showed increasing focus on molecular mechanisms such as identifying specific enzymes that interact with toxicants, and studying their variation across individuals. [8]
A carcinogen is any substance, radionuclide, or radiation that promotes carcinogenesis. This may be due to the ability to damage the genome or to the disruption of cellular metabolic processes. Several radioactive substances are considered carcinogens, but their carcinogenic activity is attributed to the radiation, for example gamma rays and alpha particles, which they emit. Common examples of non-radioactive carcinogens are inhaled asbestos, certain dioxins, and tobacco smoke. Although the public generally associates carcinogenicity with synthetic chemicals, it is equally likely to arise from both natural and synthetic substances. Carcinogens are not necessarily immediately toxic; thus, their effect can be insidious.
Toxicology is a scientific discipline, overlapping with biology, chemistry, pharmacology, and medicine, that involves the study of the adverse effects of chemical substances on living organisms and the practice of diagnosing and treating exposures to toxins and toxicants. The relationship between dose and its effects on the exposed organism is of high significance in toxicology. Factors that influence chemical toxicity include the dosage, duration of exposure, route of exposure, species, age, sex, and environment. Toxicologists are experts on poisons and poisoning. There is a movement for evidence-based toxicology as part of the larger movement towards evidence-based practices. Toxicology is currently contributing to the field of cancer research, since some toxins can be used as drugs for killing tumor cells. One prime example of this is ribosome-inactivating proteins, tested in the treatment of leukemia.
Toxicity is the degree to which a chemical substance or a particular mixture of substances can damage an organism. Toxicity can refer to the effect on a whole organism, such as an animal, bacterium, or plant, as well as the effect on a substructure of the organism, such as a cell (cytotoxicity) or an organ such as the liver (hepatotoxicity). By extension, the word may be metaphorically used to describe toxic effects on larger and more complex groups, such as the family unit or society at large. Sometimes the word is more or less synonymous with poisoning in everyday usage.
Piperonyl butoxide (PBO) is a pale yellow to light brown liquid organic compound used as a synergist component of pesticide formulations. That is, despite having no pesticidal activity of its own, it enhances the potency of certain pesticides such as carbamates, pyrethrins, pyrethroids, and rotenone. It is a semisynthetic derivative of safrole.
Chlorfenvinphos is the common name of an organophosphorus compound that was widely used as an insecticide and an acaricide. The molecule itself can be described as an enol ester derived from dichloroacetophenone and diethylphosphonic acid. Chlorfenvinphos has been included in many products since its first use in 1963. However, because of its toxic effect as a cholinesterase inhibitor it has been banned in several countries, including the United States and the European Union. Its use in the United States was cancelled in 1991.
Occupational hygiene is the anticipation, recognition, evaluation, control, and confirmation (ARECC) of protection from risks associated with exposures to hazards in, or arising from, the workplace that may result in injury, illness, impairment, or affect the well-being of workers and members of the community. These hazards or stressors are typically divided into the categories biological, chemical, physical, ergonomic and psychosocial. The risk of a health effect from a given stressor is a function of the hazard multiplied by the exposure to the individual or group. For chemicals, the hazard can be understood by the dose response profile most often based on toxicological studies or models. Occupational hygienists work closely with toxicologists for understanding chemical hazards, physicists for physical hazards, and physicians and microbiologists for biological hazards. Environmental and occupational hygienists are considered experts in exposure science and exposure risk management. Depending on an individual's type of job, a hygienist will apply their exposure science expertise for the protection of workers, consumers and/or communities.
Chemical hazards are typical of hazardous chemicals and hazardous materials in general. Exposure to certain chemicals can cause acute or long-term adverse health effects. Chemical hazards are usually classified separately from biological hazards (biohazards). Main classifications of chemical hazards include asphyxiants, corrosives, irritants, sensitizers, carcinogens, mutagens, teratogens, reactants, and flammables. In the workplace, exposure to chemical hazards is a type of occupational hazard. The use of protective personal equipment (PPE) may substantially reduce the risk of damage from contact with hazardous materials.
Pentachlorophenol (PCP) is an organochlorine compound used as a pesticide and a disinfectant. First produced in the 1930s, it is marketed under many trade names. It can be found as pure PCP, or as the sodium salt of PCP, the latter of which dissolves easily in water. It can be biodegraded by some bacteria, including Sphingobium chlorophenolicum.
An environmental hazard is a substance, state or event which has the potential to threaten the surrounding natural environment or adversely affect people's health, including pollution and natural disasters such as storms and earthquakes. It can include any single or combination of toxic chemical, biological, or physical agents in the environment, resulting from human activities or natural processes, that may impact the health of exposed subjects, including pollutants such as heavy metals, pesticides, biological contaminants, toxic waste, industrial and home chemicals.
Exposure assessment is a branch of environmental science and occupational hygiene that focuses on the processes that take place at the interface between the environment containing the contaminant of interest and the organism being considered. These are the final steps in the path to release an environmental contaminant, through transport to its effect in a biological system. It tries to measure how much of a contaminant can be absorbed by an exposed target organism, in what form, at what rate and how much of the absorbed amount is actually available to produce a biological effect. Although the same general concepts apply to other organisms, the overwhelming majority of applications of exposure assessment are concerned with human health, making it an important tool in public health.
Skin absorption is a route by which substances can enter the body through the skin. Along with inhalation, ingestion and injection, dermal absorption is a route of exposure for toxic substances and route of administration for medication. Absorption of substances through the skin depends on a number of factors, the most important of which are concentration, duration of contact, solubility of medication, and physical condition of the skin and part of the body exposed.
1,1,2,2-tetrachloroethane (TeCA), also known by the brand names Bonoform, Cellon and Westron, is an organic compound. It is colorless liquid and has a sweet odor. It is used as an industrial solvent and as a separation agent. TeCA is toxic and it can be inhaled, consumed or absorbed through the skin. After exposure, nausea, dizziness or even liver damage may occur.
α-Naphthylthiourea (ANTU) is an organosulfur compound with the formula C10H7NHC(S)NH2. This a white, crystalline powder although commercial samples may be off-white. It is used as a rodenticide and as such is fairly toxic. Naphthylthiourea is available as 10% active baits in suitable protein- or carbohydrate-rich materials and as a 20% tracking powder.
Reproductive toxicity refers to the potential risk from a given chemical, physical or biologic agent to adversely affect both male and female fertility as well as offspring development. Reproductive toxicants may adversely affect sexual function, ovarian failure, fertility as well as causing developmental toxicity in the offspring. Lowered effective fertility related to reproductive toxicity relates to both male and female effects alike and is reflected in decreased sperm counts, semen quality and ovarian failure. Infertility is medically defined as a failure of a couple to conceive over the course of one year of unprotected intercourse. As many as 20% of couples experience infertility. Among men, oligospermia is defined as a paucity of viable spermatozoa in the semen, whereas azoospermia refers to the complete absence of viable spermatozoa in the semen.
Hexachlorocyclopentadiene (HCCPD), also known as C-56, Graphlox, and HRS 1655, is an organochlorine compound with the formula C5Cl6. It is a precursor to pesticides, flame retardants, and dyes. It is a colourless liquid, although commercial samples appear lemon-yellow liquid sometimes with a bluish vapour. Many of its derivatives proved to be highly controversial, as studies showed them to be persistent organic pollutants. An estimated 270,000 tons were produced until 1976, and smaller amounts continue to be produced today. Two prominent manufacturers are Velsicol Chemical Corporation in the US and by Jiangsu Anpon Electrochemicals Co. in China.
In analytical chemistry, biomonitoring is the measurement of the body burden of toxic chemical compounds, elements, or their metabolites, in biological substances. Often, these measurements are done in blood and urine. Biomonitoring is performed in both environmental health, and in occupational safety and health as a means of exposure assessment and workplace health surveillance.
The derived no-effect level (DNEL) is the level of exposure to a substance above which humans should not be exposed. The REACH regulation defines them as exposure levels beneath which a substance does not harm human health. According to the EU REACH legislation, manufacturers and importers of chemical substances are required to calculate DNELs as part of their chemical safety assessment (CSA) for any chemicals used in quantities of 10 tonnes or more per year. The DNEL is to be published in the manufacturer's chemical safety report (CSR) and, for hazard communication, in an extended safety data sheet.
Ethoprophos (or ethoprop) is an organophosphate ester with the formula C8H19O2PS2. It is a clear yellow to colourless liquid that has a characteristic mercaptan-like odour. It is used as an insecticide and nematicide and it is an acetylcholinesterase inhibitor.
The Dose That Makes the Poison: A Plain Language Guide to Toxicology is a book originally written by M. Alice Ottoboni and published in 1984 by Vincente Books to help laypeople understand what she considered to be an unfounded fear of synthetic chemicals. A second edition was published in 1991 and a third, revised by Patricia Frank, was released in 2011.
Toxicology of carbon nanomaterials is the study of toxicity in carbon nanomaterials like fullerenes and carbon nanotubes.