Toxicology - deck III Flashcards
Biodegradation of organic
environmental toxicants
occurs due to
direct contact with the microbial enzymes.
One enzyme molecule catalyzes decomposition of millions of organic molecules per minute.
Biodegradation of organic environmental toxicants is usually a multi-step process, occurring
in the cooperation of a number of
microorganisms that often act synergistically.
PAH
polyaromatic hydrocarbons or polycyclic aromatic hydrocarbons (PAHs) are a class of chemicals that occur naturally in coal, crude oil, and gasoline.
They result from burning coal, oil, gas, wood, garbage, and tobacco. PAHs can bind to or form small particles in the air.
Classification of bioremediation methods (5)
- Intrinsic bioremediation
- Biostimulation
- Bioaugmentation
- Phytoremediation
- Rhizoremediation
- Intrinsic bioremediation means
or natural attenuation,
happens naturally in the contaminated area, such as a petrol-polluted old gas station.
It relies on natural conditions and behavior of soil microorganisms that are indigenous
to soil.
Any site is unique, know-how obtained in one site is not directly conveyable to another contaminated site.
- Biostimulation remediation
means
adding nutrients and other substances to soil to catalyze natural attenuation.
Nutrients in a gas or liquid form are added to soil or water where there is a need to
remove contaminants.
Bacteria are already there, they are just stimulated for growth
and activity. Essentially, the bacteria turn the harmful substances (and other) into CO2.
- Bioaugmentation remediation
involves
introduction of exogenic microorganisms (sourced from outside the soil environment) capable of detoxifying and removing a particular contaminant, sometimes GMO are used.
- Phytoremediation is
Use of plants to clean up soil, water or air.
NB! These plants cannot be used for feed or food.
- Rhizoremediation is
the most evolved process of bioremediation,
involves removal of contaminants by mutual interaction of plant
roots and suitable microflora in the rhizosphere, the region of soil directly influenced by root secretions and associated soil
microbes.
- Pollutants remediated by this method are mainly organic compounds, unable enter the plant due to
their high hydrophobicity.
NB! Plants will not become toxic.
photolysis
also known as Photodegradation
Photolysis, as a chemical reaction that occurs under the influence of photons or light, may take place in the atmosphere and on the surface of either water or soil,but it does not occur in benthic sediments and deep
layers of soil.
There are two types of photochemical reactions:
- direct photolysis
- indirect photolysis
Ecotoxicology is a
subdiscipline of environmental toxicology studying
harmful effects of toxicants at the population and ecosystem levels.
Effects upon individuals are important if they are translated into effects at these levels.
Biomagnification
is a process which results in
higher concentration of a substance in an organism than in its food.
The higher concentration of a
substance in an organism than in its food.
Concentration of some chemicals in the fatty tissues of top
predators
can be ? of times higher than the concentration in the open water.
Concentration of some chemicals in the fatty tissues of top
predators
can be millions of times higher than the concentration in the open water.
The real reason for biomagnification is
the time factor. Organisms, dwelling at higher levels of the food chain live longer and, hence, have more time for the bioaccumulation
of toxicants.
QSAR
Quantitative structure-activity relationship (QSAR) analysis is a practical approach by which chemical structure is quantitatively correlated with biological activity or chemical reactivity.
QSAR is involved in drug discovery and designing to identify chemical structures with good inhibitory effects on specific targets and with low toxicity levels.
The most important purpose of QSAR modeling is to predict the activity/property/toxicity of new chemical entity (NCE) falling within the domain of applicability of the developed models.
QSAR models remain a good alternative to animal testing, which would otherwise be necessary to determine the toxicity of unknown substances.
Two basic truths in the design of the animal studies are:
- The adverse effect of a toxicant can, in “principle“, be extrapolated from animals to humans. (For human safety reasons, it is considered that humans are at least 10 times more
sensitive than animals.) - To minimize the number of necessary laboratory animals.
Genotoxicity tests
Genotoxicity tests can be defined as in vitro and in vivo tests designed to detect compounds which induce genetic damage directly or indirectly by various mechanisms. These tests should enable a hazard identification with respect to damage to DNA and its fixation.
These genotoxicity tests are done to identify if a drug or other substance have the potential to cause mutation and genotoxicity.
Comet assay
The comet assay (single-cell gel electrophoresis) is a simple method for measuring deoxyribonucleic acid (DNA) strand breaks in eukaryotic cells.
Allows for the detection of a wide array of DNA damage in single cells with a high sensitivity.
Salmonella/mammal microsome (Ames) test
enables detection of the reversed mutations formed in the DNA of Gram-negative enterobacterium Salmonella typhimurium after exposure to a genotoxic substance and to the rat liver homogenate. The number of mutant colonies, able to grow in the histidine-free environment is estimated.
The Ames test shows the number of bacterial cells, which after an exposure to the chemical, have mutated from His- genotype to His+ genotype.
The Ames test is a rapid and reliable bacterial assay used to evaluate a chemical’s potential genotoxicity by measuring its ability to induce reverse mutations at selected loci of several bacterial strains.
The following alternative oral acute toxicity animal tests have been developed:
- Fixed Dose Procedure (FDP)
- Acute Toxic Class (ATC)
- Up and Down Procedure (UDP
These methods guarantee significant improvements in animal welfare and permit to reduce dramatically the number of the test animals needed.
In water, the biodegradation rate depends on
presence of particulate matter,
concentration of inorganic and organic nutrients,
temperature,
oxygen concentration,
redox potential and
adaptation of the microbial population.
In soil, the range and rate of biodegradation depend on
temperature,
soil moisture content,
the composition and activity of bacterial flora,
the properties and “age” of a pollutant and
the content of nutritive ingredients.
The rate of photochemical reactions depends on
the number of chlorine atoms in a compound, the more C-Cl bonds, the slower the rate
for many PAHs in the aquatic environment photolysis is a major abiotic degradation process, followed by
microbial degradation.
Generally, compounds with higher molecular weight and more condensed aromatic rings have a higher rate of photolysis than smaller and less condensed ones.
The principal degradation pathways for pesticides involve (4)
photolysis,
hydrolysis,
dehalogenation
and oxidation
? is one of the major transformation processes and one of
the factors controlling the fate of pesticides in the environment.
Photochemical degradation is one of the major transformation processes and one of the factors controlling the fate of pesticides in the environment.
Photodegradation can destroy pesticides on foliage, on the soil surface, and even in the air.
Ecotoxicology:
Degree of toxic effect can vary depending on
where the organism is found within its food web.
Biomagnification is a process which results in
higher concentration of a substance in an organism than in its food.
Biomagnification comprises compounds, only slightly soluble in water that tend to accumulate in adipose tissues of an organism.
the first harmful effects of a toxicant in a water body often appear as
dead or malformed chicks due to bioaccumulation and egg yolk being rish in fatty material in which toxicants accumulate.
(main) 3 Sources of toxic components in feeds
- Environmental, mostly anthropogenic (industrial) pollutants, formed during burning of fossile fuels, industrial emissions, agriculture, nuclear disasters
- Toxic metabolites of microorganisms (mycotoxins)
- Endogenous toxic compounds of plants, part of which are synthesized for defence against herbivorous animals and other plants
name 3 main Environmental contaminants in feeds
Heavy metals.
Contamination of feeds/ herbage with Cd (cadmium) is a result of applying certain fertilizers to crops and pastures, with Pb from industrial and urban pollution, Hg from use of fishmeal.
Pesticide residues
that may contaminate feeds originate from most of the major
groups, including organochlorine, organophosphate and pyrethroid compounds. 21 percent of feeds in the UK contain pesticide residues.
Dioxins and polychlorinated biphenyls (PCBs)
exemplify industrial pollutants that may contaminate feeds, particularly herbage. Cows, grazing pastures that are close to industrial areas produce milk with higher dioxin content.
Fungal contaminants in feeds
the predominant genus in dairy is
In the tropics, Aspergillus is the predominant genus in dairy and other feeds.
Other species include Penicillium, Fusarium and Alternaria, which are also important contaminants of cereal grains.
Fungal contamination is undesirable because of
the potential for mycotoxin production.
Mycotoxin binding adsorbents exist for binding the toxins.
Plant toxicants in feeds may be divided into:
a heat-labile group
a heat-stable group
Probability of transfer of toxic substances from feed to food and the exact movement paths depend on
a complex of physico-chemical properties of the substance (molecule size, fat solubility or lipophilicity (log Pow), etc),
which determine the absorption of the substance into the blood and further into the tissues, the half-life in different parts of the animal’s body, metabolism and elimination through different channels,
ie. from toxicokinetics and dynamics of the substance, which, from the other side, depend on the animal species and the genetic baggage of a specific individual.
What is the log POW?
It is recognized that a simple physiochemical property can be used to indicate a product’s potential to bioaccumulate. This property is the Log Pow - defined as the ratio of the equilibrium concentration of a dissolved substance in a two-phase system comprising two largely immiscible solvents, n-octanol and water.
if the absorption of a substance from the digestive tract (low logPow ) is approximately 0%, this substance will definitely not reach the tissues.
if the substance is completely absorbed, for which the best logPow range is 3-5, it can also reach several edible tissues
Transfer factor (TFi) =
the residue concentration (Ci) in the animal commodity of interest (muscle, fat, liver, kidney, milk, eggs)
divided by the residue concentration (Cfeed) in the animal feed including any contribution from ingested soil
TFi = Ci / Cfeed
Food toxicology as a branch of toxicology investigates
ways and mechanisms of entrance of potentially toxic substances into food or their generation during food processing and storage, and the ways of avoiding or reducing food contamination
- methods of assessment of toxicity and risk of food components are investigated
- adverse effects on an organism produced by harmful components of foods are also investigated
Lectins are
nonenzymatic thermolabile glyco- or lipoproteins that selectively bind to saccharide (glucose, galactose, etc.) groups, discovered in more than 800 edible plants.
- are widely represented in the leguminous plants (pulses) (Leguminosae) like beans or peas.
have also been found in animals like sponges, molluscs, fish (in blood), amphibians (in the eggs), and in mammalian, including human, tissues.