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Toxicokinetics

From Wikipedia, the free encyclopedia

Toxicokinetics (often abbreviated as 'TK') is the description of both what rate a chemical will enter the body and what occurs to excrete and metabolize the compound once it is in the body.

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  • Chemical mixtures and food safety
  • Elimination kinetics & compartment models (PK)
  • First Order Elimination Rate Constant and Half-life | A closer look - Lect 11

Transcription

Hello, my name is Jean-Lou. I’m a toxicologist at EFSA. My work involves developing methods for assessing the safety of chemicals in food and the environment. Today, I’m going to talk about the risk assessment of multiple chemicals in food often called chemical mixtures. First of all, what do we mean by ‘chemical mixtures’? “Chemical mixtures” refer to combined exposure to multiple chemicals. Food may contain many different chemicals naturally occurring such as nutrients and plant toxins produced by weeds, or man-made chemicals such as pesticides and environmental contaminants like dioxins. The number of combinations of chemicals is practically infinite and they can come from a variety of sources: food, medicines or consumer products such as cosmetics. These chemicals may raise health concerns depending on their toxicity and the level of exposure in food or the environment. So, how do scientists assess consumer safety for a single chemical? For a single chemical scientists review all the toxicological data to set a safe level of use and compare it with consumer exposure through food, to conclude on any potential health risk. What about multiple chemicals? For multiple chemicals, scientists have developed risk assessment methods which use the same principles as for single chemicals with some differences. First of all, the beginning of the process is the problem formulation to define whether a risk assessment for a group of chemicals is needed based on the nature of the exposure in consumers or depending on their toxicity. Who is exposed and by how much? Is the exposure a one-off or is spread over time? The next step is to assess the toxicity of the group of chemicals and identify how they act, often referred to as “mode of action”. Scientists analyse the information available on the toxicity using scientific criteria in a so-called “weight of evidence approach”. Three assumptions about the toxicity are used to then conclude on the health risks – dose addition, response addition and interaction –. Dose addition means that the chemicals have a similar toxicity/mode of action and after determining their individual potency, the doses are added for the risk assessment. Response addition means that the chemicals have independent toxic effects and the measures of toxicity are added for the risk assessment. Interactions are more complex. Chemicals can become more toxic when combined, which is called “synergism”. On the other hand, they can be less toxic when combined, which is known as “antagonism”. The mechanisms behind synergism and antagonism are complex, however, two important ones involve an increase or decrease in the body’s ability to detoxify and eliminate the compounds, which is called toxicokinetics, and an increase or decrease in toxicity, which is called toxicodynamics. If there is evidence of such interactions, scientists collect the information to take these effects into account in the risk assessment. Efsa is very active in this field and has developed methods for the risk assessment of multiple chemicals both for human health and the environment. Recent examples include risk assessment of multiple pesticides and contaminants in humans and risk assessment of multiple pesticides in bees. In addition, new tools such as mathematical and biological models are being used to predict toxicity and detoxification. Scientists will continue to push back the boundaries to ensure that policies aimed at protecting consumers are based on the latest and most reliable science available.

Relation to Pharmacokinetics

It is an application of pharmacokinetics to determine the relationship between the systemic exposure of a compound and its toxicity. It is used primarily for establishing relationships between exposures in toxicology experiments in animals and the corresponding exposures in humans. However, it can also be used in environmental risk assessments in order to determine the potential effects of releasing chemicals into the environment. In order to quantify toxic effects, toxicokinetics can be combined with toxicodynamics. Such toxicokinetic-toxicodynamic (TKTD) models are used in ecotoxicology (see ecotoxmodels a website on mathematical models in ecotoxicology).

Similarly, physiological toxicokinetic models are physiological pharmacokinetic models developed to describe and predict the behavior of a toxicant in an animal body; for example, what parts (compartments) of the body a chemical may tend to enter (e.g. fat, liver, spleen, etc.), and whether or not the chemical is expected to be metabolized or excreted and at what rate.

Processes

Four potential processes exist for a chemical interacting with an animal: absorption, distribution, metabolism and excretion (ADME). Absorption describes the entrance of the chemical into the body, and can occur through the air, water, food, or soil. Once a chemical is inside a body, it can be distributed to other areas of the body through diffusion or other biological processes. At this point, the chemical may undergo metabolism and be biotransformed into other chemicals (metabolites). These metabolites can be less or more toxic than the parent compound. After this potential biotransformation occurs, the metabolites may leave the body, be transformed into other compounds, or continue to be stored in the body compartments.

A well designed toxicokinetic study may involve several different strategies and depends on the scientific question to be answered. Controlled acute and repeated toxicokinetic animal studies are useful to identify a chemical's biological persistence, tissue and whole body half-life, and its potential to bioaccumulate. Toxicokinetic profiles can change with increasing exposure duration or dose. Real world environmental exposures generally occur as low level mixtures, such as from air, water, food, or tobacco products. Mixture effects may differ from individual chemical toxicokinetic profiles because of chemical interactions, synergistic, or competitive processes. For other reasons, it is equally important to characterize the toxicokinetics of individual chemicals constituents found in mixtures as information on behavior or fate of the individual chemical can help explain environmental, human, and wildlife biomonitoring studies.[1]

References

  1. ^ Szabo DT, Diliberto JJ, Hakk H, Huwe JK, Birnbaum LS (2010). "Toxicokinetics of the flame retardant hexabromocyclododecane gamma: effect of dose, timing, route, repeated exposure, and metabolism". Toxicological Sciences. 117 (2): 282–93. doi:10.1093/toxsci/kfq183. PMID 20562218.


This page was last edited on 20 July 2022, at 21:15
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