TL;DR: The prediction of biological responses elicited by interaction of pesticides with each other (or with other chemicals) will benefit from using a systems toxicology approach and the identification of core features of pesticide mixtures at molecular level could be helpful to assess or predict the occurrence of interactive effects giving rise to unpredicted responses.
Abstract: Pesticides can interact with each other in various ways according to the compound itself and its chemical family, the dose and the targeted organs, leading to various effects. The term interaction means situations where some or all individual components of a mixture influence each other's toxicity and the joint effects may deviate from the additive predictions. The various mixture effects can be greatly determined by toxicokinetic and toxicodynamic factors involving metabolic pathways and cellular or molecular targets of individual pesticides, respectively. However, the complexity of toxicological interactions can lead to unpredictable effects of pesticide mixtures. Interactions on metabolic processes affecting the biotransformation of pesticides seem to be by far the most common mechanism of synergism. Moreover, the identification of pesticides responsible for synergistic interactions is an important issue for cumulative risk assessment. Cholinesterase inhibiting insecticides (organophosphates and N-methylcarbamates), triazole fungicides, triazine herbicides, and pyrethroid insecticides are overrepresented in the synergistic mixtures identified so far. Since the limited available empirical evidence suggests that synergisms at dietary exposure levels are rather rare, and experimentally occurred at unrealistic high concentrations, synergism cannot be predicted quantitatively on the basis of the toxicity of mixture components. The prediction of biological responses elicited by interaction of pesticides with each other (or with other chemicals) will benefit from using a systems toxicology approach. The identification of core features of pesticide mixtures at molecular level, such as gene expression profiles, could be helpful to assess or predict the occurrence of interactive effects giving rise to unpredicted responses.
TL;DR: Oxidative Stress is the key mechanism involved in Lead, Mercury, Cadmium and Arsenic-induced kidney toxicity and possible effectiveness of plants and plants derived compound against heavy metals is due to their antioxidant activity.
Abstract: Environmental pollution has become a concerning matter to human beings. Flint water crisis in the USA pointed out that pollution by heavy metal is getting worse day by day, predominantly by Lead, Cadmium, Mercury and Arsenic. Despite of not having any biological role in flora and fauna, they exhibit detrimental effect following exposure (acute or chronic). Even at low dose, they affect brain, kidney and heart. Oxidative stress has been termed as cause and effect in heavy metal-induced kidney toxicity. In treatment strategy, different chelating agent, vitamins and minerals are included, though chelating agents has been showed different fatal drawbacks. Interestingly, plants and plants derived compounds had shown possible effectiveness against heavy metals induced kidney toxicity. This review will provide detail information on toxicodynamics of Pb, Cd, Hg and As, treatment strategy along with the possible beneficiary role of plant derived compound to protect kidney.
TL;DR: Studies with permethrin, cypermethrin and fenvalerate have established that rates of metabolism and elimination in rainbow trout are significantly lower than those reported for birds and mammals, and variations in toxicodynamics are also crucial in evaluating pyrethroid selectivity.
Abstract: The pyrethroid insecticides are extremely toxic to fish, with 96—h LC50 values generally below 10 μg/L and i.p. and i.v. LD50 values below 20 mg/kg. Corresponding LD50 values in mammals and birds are in the range of several hundred to several thousand milligrams per kilogram. This review examines pyrethroid toxicokinetics and toxicodynamics in fish as critical factors associated with species selectivity. Studies with permethrin, cypermethrin and fenvalerate have established that rates of metabolism and elimination in rainbow trout are significantly lower than those reported for birds and mammals. Comparatively low lethal brain pyrethroid concentrations and nonneural aspects of pyrethroid intoxication in fish suggest that variations in toxicodynamics are also crucial in evaluating pyrethroid selectivity.
TL;DR: The results support the view that the membrane is the primary target site for acute toxicity of substituted phenols in aquatic organisms and the classification into baseline toxicants and uncouplers based upon the criteria derived from the mechanistic test system is correct.
Abstract: Mechanistic studies on membrane toxicity are reviewed and linked to effects observed in-vivo. Time-resolved spectroscopy on energy-transducing membranes is an in-vitro test method that provides information on the toxicodynamics of membrane toxicity, namely baseline toxicity and uncoupling. Without blurring effects of the toxicokinetic phase, the intrinsic potency of membrane toxicants can directly be determined thus allowing the development of a classification system to distinguish between baseline toxicity and uncoupling. Toxicity data of known baseline toxicants and of substituted phenols from literature are reevaluated in light of the information obtained from the mechanistic test system. Exposure-based effect data (aqueous effect concentrations) of substituted phenols (baseline toxicants and uncouplers) from various aquatic organisms (bacteria, protozoa, algae, daphnids, fish) are compared to the corresponding effect concentrations expected from baseline toxicity. The results of the comparison support the view that the membrane is the primary target site for acute toxicity of substituted phenols in aquatic organisms. The classification into baseline toxicants and uncouplers based upon the criteria derived from the mechanistic test system is correct. Nevertheless, the acute toxicity in-vivo cannot be correlated quantitatively to the mechanistic data presumably because bioaccumulation is not directly proportional to intrinsic toxicity and the metabolic transformation is variable within the test set of substituted phenols. The pH-dependence of acute toxicity is mainly determined by the pH-dependence of bioccumulation, the internal effect concentrations are virtually independent on external pH. The internal effect concentrations, also called lethal body burdens or critical body residues, which are taken from the literature or calculated from aqueous effect concentrations and bioconcentration factors, are related to membrane concentrations using a simple three-compartment equilibrium partitioning model. The modeled membrane concentrations of non-polar and polar narcotics turn out to be statistically indistinguishable, which is consistent with the findings from the mechanistic test system. The toxic ratios, i.e., the excess toxicity of uncouplers in relation to their baseline toxicity, agree for most compounds upon comparison of the mechanistic test system with the aquatic organisms thus confirming that uncoupling is the dominant mode of action responsible for lethality.
TL;DR: The influence of speciation on metal toxicokinetics and toxicodynamics in mammals, and therefore the adverse effects of metals, is reviewed to illustrate how the physicochemical characteristics of metals and their handling in the body (toxicokinetics) can influence toxicity (t toxicodynamics).
Abstract: Chemical form (i.e., species) can influence metal toxicokinetics and toxicodynamics and should be considered to improve human health risk assessment. Factors that influence metal speciation (and examples) include: (1) carrier-mediated processes for specific metal species (arsenic, chromium, lead and manganese), (2) valence state (arsenic, chromium, manganese and mercury), (3) particle size (lead and manganese), (4) the nature of metal binding ligands (aluminum, arsenic, chromium, lead, and manganese), (5) whether the metal is an organic versus inorganic species (arsenic, lead, and mercury), and (6) biotransformation of metal species (aluminum, arsenic, chromium, lead, manganese and mercury). The influence of speciation on metal toxicokinetics and toxicodynamics in mammals, and therefore the adverse effects of metals, is reviewed to illustrate how the physicochemical characteristics of metals and their handling in the body (toxicokinetics) can influence toxicity (toxicodynamics). Generalizing from mercury,...