Diquat causes caspase-independent cell death in SH-SY5Y cells by production of ROS independently of mitochondria.

Evidence indicates that Parkinson's disease (PD), in addition to having a genetic aetiology, has an environmental component that contributes to disease onset and progression. The exact nature of any environmental agent contributing to PD is unknown in most cases. Given its similarity to paraquat, an agrochemical removed from registration in the EU for its suspected potential to cause PD, we have investigated the in vitro capacity of the related herbicide Diquat to cause PD-like cell death. Diquat showed greater toxicity towards SH-SY5Y neuroblastoma cells and human midbrain neural cells than paraquat and also MPTP, which was independent of dopamine transporter-mediated uptake. Diquat caused cell death independently of caspase activation, potentially via RIP1 kinase, with only a minor contribution from apoptosis, which was accompanied by enhanced reactive oxygen species production in the absence of major inhibition of complex I of the mitochondrial respiratory chain. No changes in α-synuclein expression were observed following 24-h or 4-week exposure. Diquat may, therefore, kill neural tissue by programmed necrosis rather than apoptosis, reflecting the pathological changes seen following high-level exposure, although its ability to promote PD is unclear.

Trichloroethylene and its metabolite TaClo lead to degeneration of substantia nigra dopaminergic neurones: Effects in wild type and human A30P mutant α-synuclein mice.

Parkinson's disease (PD) is characterised pathologically by degeneration of the dopaminergic (DA) neurones of the substantia nigra pars compacta (SNpc) and the presence of α-synuclein containing Lewy body inclusions. Trichloroethylene (TCE) has been suggested as a potential environmental chemical that may contribute to the development of PD, via conversion to the neurotoxin, 1-Trichloromethyl-1,2,3,4-tetrahydro-ß-carboline (TaClo). We investigated the effect of an 8 week exposure to TCE or TaClo on wild type and, as an experimental model of PD, A30P mutant α-synuclein overexpressing mice using a combination of behaviour and pathology. TCE or TaClo exposure caused significant DA neuronal loss within the SNpc in both wild type and transgenic mice. Cell numbers were lower in A30P animals than wild type, however, no additive effect of TCE or TaClo exposure and A30P overexpression was found. TCE or TaClo did not appear to lead to acceleration of motor or cognitive deficits in either wild type or A30P mutant mice, potentially because of the modest reductions of DA neuronal number in the SNpc. Our results do however suggest that TCE exposure could be a possible factor in development of PD like changes following exposure.

Clinical management of casualties exposed to lung damaging agents: a critical review.

There is no specific antidote for the treatment of casualties exposed to chlorine, phosgene, or mustards; therefore, management is largely supportive. Corticosteroid treatment has been given to casualties accidentally exposed to chlorine. Clinical data on efficacy are inconclusive as the numbers given steroids have been small and the indications for administration unclear. There have been no clinical controlled studies. There is a stronger evidence base from animal studies, particularly from porcine and rodent models. Lung injury induced by phosgene and mustard appears to be mediated by glutathione depletion, lipid peroxidation, free radical generation, and subsequent cellular toxicity. There is limited evidence to suggest that repletion of glutathione reduces and/or prevents lung damage by these agents. This may provide an opportunity for therapeutic intervention.

Esterase activity in rat hepatocytes.

Hydrolysis of acetylsalicylate, benorylate, phenetsal, fluazifop butyl and paraoxon has been studied with freshly isolated rat hepatocytes maintained as a monolayer. Acetylsalicylate and paraoxon were the poorest substrates for hydrolysis whereas benorylate was hydrolysed one hundred times faster. Phenetsal and fluazifop butyl were both hydrolysed at one-tenth of the rate of benorylate. Inhibitor studies with paraoxon, BNPP and physostigmine indicated the involvement of different carboxylesterase isozymes. Studies with acetylsalicylate indicated that uptake of the substrate into the hepatocyte may influence the rate of formation of the hydrolysis product. Studies of hydrolysis in hepatocytes more closely reflect in vivo hepatic hydrolysis than subcellular fractions as cytosolic and microsomal esterases can act in parallel.

Human xenobiotic metabolizing esterases in liver and blood.

Esterases in human liver microsomes hydrolysed fluazifop-butyl (Vmax 9.8 +/- 1.6 mumol/min/g tissue), paraoxon (Vmax 47.4 +/- 7.5 nmol/min/g tissue) and phenylacetate (Vmax 57 +/- 8 mumol/min/g tissue), whereas esterases found in the human liver cytosol hydrolysed fluazifop-butyl (Vmax 10.0 +/- 0.5 mumol/min/g tissue) and phenylacetate (Vmax 37 +/- 2.9 mumol/min/g tissue) but not paraoxon. Human plasma esterase hydrolysed fluazifop-butyl (Vmax 0.09 +/- 0.006 mumol/min/mL), paraoxon (Vmax 210 +/- 14 nmol/min/mL) and phenylacetate (Vmax 250 +/- 17 mumol/min/mL). Inhibitory studies using paraoxon, bis-nitrophenol phosphate and mercuric chloride indicated fluazifop-butyl hydrolysis involved carboxylesterase in liver microsomes and cytosol, and cholinesterase and carboxylesterase in plasma. Phenylacetate hydrolysis involved arylesterase in plasma, both arylesterase and carboxylesterase in liver microsomes and carboxylesterase in liver cytosol. Plasma hydrolysis is less important and overall esterase activity is lower in humans than in the rat which is therefore a poor model.

Nature and role of xenobiotic metabolizing esterases in rat liver, lung, skin and blood.

In the present study, the distribution and nature of esterases in the rat which hydrolysed fluazifop-butyl, carbaryl, paraoxon and phenylacetate were investigated. Vmax and Km values for the hydrolysis reactions were determined. Fluazifop-butyl was hydrolysed to fluazifop by rat liver (Vmax mumol/min/g microsomes 6.2 +/- 0.4; cytosol 6.84 +/- 0.85), lung (Vmax microsomes 0.38 +/- 0.1; cytosol 1.5 +/- 0.32) and skin (Vmax microsomes 0.02 +/- 0.0015; cytosol 0.4 +/- 0.06) and by plasma (Vmax mumol/min/mL 5.8 +/- 0.48) and red blood cells (Vmax 0.03 +/- 0.015). Significant inhibition by paraoxon and bismitrophenol phosphate indicated the involvement of carboxylesterases. Carbaryl was hydrolysed by liver, lung and skin at a lower rate by microsomal fractions (Vmax nmol/min/g 2.1 +/- 0.25, 1.6 +/- 0.25, 0.2 +/- 0.035, respectively) compared to cytosolic fractions (Vmax 6.7 +/- 0.75, 1.4 +/- 0.36, 0.5 +/- 0.12) and plasma (Vmax nmol/min/mL 3.0 +/- 0.25). Hydrolysis involved carboxylesterases. Paraoxon was hydrolysed by paraoxonases/arylesterases only in the plasma (Vmax nmol/min/mL 246 +/- 12) and microsomal fractions from liver (Vmax 330 nmol/min/g +/- 25) and lung (Vmax 2 +/- 0.25). Phenylacetate was hydrolysed by both microsomal and cytosolic fractions from all tissues studied. Hydrolysis involved arylesterases in the microsomes and carboxylesterases in the cytosol. Extrahepatic hydrolysis may be important following some routes of exposure to xenobiotic esters.

Paraoxonase distribution in Caucasian males.

Mean plasma paraoxonase activity was lower in a population of all males than in a mixed sex population with no evidence of the higher activity group. It is suggested that sex differences in plasma lipid may contribute to the observed differences, and that factors other than genetics may influence observed plasma paraoxonase levels.

Peripheral esterases in the rat: effects of classical inducers.

Liver microsomal paraoxonase, aryl esterase and fluazifop butyl esterase (carboxylesterase) were induced by pretreatment of rat with phenobarbitone but not by beta-naphthoflavone or clofibric acid. In the extrahepatic tissues lung cytosolicfluazifop butyl and phenylacetate esterase were induced.

The role of metabolism in determining susceptibility to parathion toxicity in man.

Human liver microsomes (n = 16) activated parathion (O, O, diethyl O-p-nitrophenyl phosphorothioate, 20 and 200 microM) to paraoxon at a rate of 23.3-199.3 and 18.7-310.3 pmol/min per mg protein, respectively. p-Nitrophenol, was also formed, at 321.1-769.2 and 406.2-778.3 pmol/min per mg protein. This represented a 16-fold and 2-fold range in capacity to activate and detoxify parathion, respectively. Parathion was activated with an apparent Km of 9-16 microM (n = 3). The activation of parathion (200 microM) was positively correlated with nifedipine oxidation, indicating the involvement of CYP3A. Correlations were not significant with ethoxyresorufin-O-dealkylation (CYP1A1/2), pentoxyresorufin-O-dealkylation (CYP2B6), p-nitrophenol hydroxylation (CYP2E1), paraoxon hydrolysis (A-esterase) or phenylvalerate hydrolysis (B-esterase). Paraoxon formation from parathion was markedly reduced by CYP3A inhibitors. Experiments with EDTA indicated that A-esterase was not functionally important at low levels of paraoxon. Human P450s 3A4 and 3A5 expressed microsomes were the most efficient at biotransforming parathion to paraoxon, although P450s 1A1, 2B6 and 2C8 also catalysed the reaction. This study has determined wide interindividual variations in capacity to metabolise parathion, mainly by CYP3A, which may influence its manifest toxicity.

Comparative studies of two organophosphorus compounds in the mouse.

A rodent model, the albino mouse, was used to investigate the in vitro and in vivo capacity of 2 organophosphate (OP) compounds, mipafox and ecothiopate, to inhibit enzymes considered to be involved in the mechanisms of OP toxicity. Mipafox and ecothiopate were chosen as model compounds because the former can produce a delayed neuropathy whereas the latter does not. Mipafox (110 mumol/kg, s.c.) inhibited brain acetylcholinesterase (AChE), neuropathy target esterase (NTE) and phenylvalerate hydrolases by 58, 64 and 65%, while diaphragm AChE and phenylvalerate hydrolases were inhibited by 66 and 80%, respectively. In contrast, ecothiopate (0.5 mumol/kg) had no effect on brain NTE or on brain or diaphragm phenylvalerate hydrolases. At the same time, diaphragm AChE was inhibited by 60% while brain AChE activity had increased by 15% of control. Mipafox was a potent inhibitor of AChE and NTE in vitro. Although ecothiopate was a highly potent anti-ChE in vitro, it had no inhibitory effect on NTE.

Ambient, biological, and biological effect monitoring of exposure to polycyclic aromatic hydrocarbons (PAHs).

A novel strategy was utilised to assess the risk to health from exposure to polycyclic aromatic hydrocarbons (PAHs). Ambient monitoring was carried out by personal sampling. Urinary thioethers (UTh) and urinary 1-hydroxypyrene (1-HP) were utilised for biological monitoring. Urinary d-glucaric acid (UDGA) and sister chromatid exchange (SCE) in peripheral blood lymphocytes were used as biological effect markers. The population was categorised into exposed and control groups according to the external dose of PAHs. The excretion of 1-HP in the controls over the 3-day period showed a relatively stable baseline, while the exposed showed a significant increase over the same period of time. SCE frequency in the exposed population was significantly different from controls.

Cytogenetic response without changes in peripheral cholinesterase enzymes following exposure to a sheep dip containing diazinon in vivo and in vitro.

Occupational exposure to organophosphorus insecticides (OPs), such as diazinon, may be monitored by the measurement of the activity of peripheral cholinesterase enzymes, including erythrocyte acetylcholinesterase (EAChE) and plasma or serum cholinesterase (plasma or serum ChE). Exposures have also been measured by the analysis of dialkyl phosphate metabolites of OPs in urine. The potential health risks associated with exposure, especially those of a neurological nature, may then be estimated, and appropriate measures to reduce or eliminate exposures can be implemented. There is evidence that some OP pesticides may have in vivo genotoxic effects, suggesting a possible link with cancer with long term or repeated heavy exposures. This paper describes work performed in 17 subjects with a single or two exposures to a sheep dip containing diazinon. Urine samples revealed OP metabolites dimethylphosphate (DMP), dimethylthiophosphate (DMTP), diethylphosphate (DEP) and diethylthiophosphate (DETP) in 37% of subjects at low levels which were not elevated after exposure. EAChE and plasma ChE were also unchanged before and after exposure, and were similar to those measured in unexposed control groups. Sister chromatid exchanges (SCE), a marker of chromosome damage, was significantly elevated in peripheral blood lymphocytes after exposure compared with before. SCE were unchanged in a group of non-occupationally exposed workers. In vitro studies with both authentic diazinon (98%) and diazinon in a sheep dip formulation (45%) showed increased SCE and decreased replicative indices, suggesting toxic and genotoxic effects of diazinon.

Percutaneous penetration of 2-phenoxyethanol through rat and human skin.

2-Phenoxyethanol applied in methanol was absorbed (64 +/- 4.4% at 24 hr) through unoccluded rat skin in vitro in the static diffusion cell with ethanol/water as receptor fluid. By comparison (43 +/- 3.7% in 24 hr) was absorbed in the flow-through diffusion system with tissue culture medium as receptor fluid. 2-Phenoxyethanol applied in methanol was absorbed (59.3 +/- 7.0% at 6 hr) through unoccluded human skin in vitro in the flow-through diffusion cell with tissue culture medium. With both unoccluded cells, 2-phenoxyethanol was lost by evaporation but occlusion of the static cell reduced evaporation and increased total absorption to 98.8 +/- 7.0%. Skin, post mitochondrial fraction, metabolized phenoxyethanol to phenoxyacetic acid at 5% of the rate for liver. Metabolism was inhibited by 1 mM pyrazole, suggesting involvement of alcohol dehydrogenase. However, first-pass metabolism of phenoxyethanol to phenoxyacetic acid was not detected during percutaneous penetration through viable rat skin in the flow-through system. First-pass metabolism in the skin does not therefore have an influence on systemic availability of dermally absorbed phenoxyethanol. These measures of phenoxyethanol absorption through rat and human skin in vitro agree well with those obtained previously in vivo.

Interindividual variations in enzymes controlling organophosphate toxicity in man.

1 Interindividual variations in an unexposed population have been defined for five enzymes involved in organophosphate (OP) toxicity. The enzymes measured were: red blood cell acetylcholinesterase (AChE), lymphocyte neuropathy target esterase (NTE), serum cholinesterase (ChE), serum paraoxonase and serum arylesterase. 2 AChE and arylesterase were normally distributed in the population whilst the distribution of NTE, ChE and paraoxonase deviated significantly from normal. 3 Assay precision and intra-individual variability were measured for each of the enzymes; the effect on interindividual variation was assessed. 4 Variations in enzyme activities between individuals could have profound effects on susceptibility to OP toxicity. Prior determination of these enzymes may be predictive of susceptibility. 5 Lymphocyte NTE has some limitations as an indicator of exposure to neurotoxic OPs.

Metabolism of n-hexane by rat liver and extrahepatic tissues and the effect of cytochrome P-450 inducers.

1. The in vitro metabolism of n-hexane was studied in rat liver, lung, brain and skeletal muscle microsomes and in microsomes prepared from cell lines expressing human cytochrome P-450 2E1 or 2B6. The hydroxylated metabolites of n-hexane were quantified by gas chromatography-mass spectometry. 2. Rat liver and extensor digitorum longus (EDL, fast-twitch skeletal muscle) microsomes and the CYP 2B6 microsomes produced the pre-neurotoxic metabolite of n-hexane, 2-hexanol as a major metabolite in contrast to the other rat tissues examined. 3. Inhibition of 2- and 3-hexanol production from n-hexane by rat lung microsomes using metyrapone, an inhibitor of cytochrome P-450 2B1 activity, resulted in almost complete inhibition of lung microsomal activity. 4. Production of all three hexanols was significantly increased with phenobarbital-induced rat liver microsomes, with a 10-fold increase in 2- and 3-hexanol production. A slight increase in 2-hexanol production with phenobarbital-induced rat EDL and brain microsomes was observed. No increase in n-hexane metabolism was noted following induction with beta-naphthoflavone or with ethanol.

An investigation into the role of rat skeletal muscle as a site for xenobiotic metabolism using microsomes and isolated cells.

1. The role of skeletal muscle microsomes as a site of extrahepatic xenobiotic metabolism using n-hexane as a model substrate was investigated. The observed cytochrome P450-dependent metabolism was compared with that found with liver, and brain microsomal fractions. 2. Rat skeletal muscle microsomes metabolised n-hexane to 1-, 2- and 3-hexanol at rates 40-300 times lower than observed with rat liver microsomes. 3. Fast-twitch extensor digitorum longus muscle (EDL) microsomes had twice as much n-hexane hydroxylase activity as the slow-twitch soleus and furthermore the EDL microsomes produced 2-hexanol, a bioactivation product of n-hexane, as a major metabolite. 4. Metabolism of hexane to 1-, 2- and 3-hexanol and 2-hexanon was demonstrated in cultured rat myoblasts. 5. Ethoxyresorufin and pentoxyresorufin O-dealkylation were not detected in either muscle microsomes or myoblasts although immunocytochemical localisation studies were suggestive of the presence of cytochrome P-450. 6. In conclusion, rat skeletal muscle has a low level of xenobiotic metabolism activity. The relevance to neuromuscular toxicity of n-hexane is discussed.

The percutaneous absorption and skin distribution of lindane in man. I. In vivo studies.

1. The absorption and distribution of lindane through skin was examined using human volunteers. Two different preparations were employed, one with acetone as the vehicle and the other, a commercial product, consisting primarily of white spirit as the solvent base. 2. The mean peak plasma concentrations of lindane following exposure to the acetone and white-spirit based applications were 0.91 and 0.47 ng/ml, respectively. The similarity between these levels did not reflect the 40-fold higher dose of lindane in the acetone vehicle. White spirit enhanced the penetration of lindane with respect to the acetone vehicle, highlighting the influence of vehicle upon percutaneous absorption. Low levels of trichlorophenol glucuronide metabolites, but no lindane, were detected in the urine. 3. The exposure site was washed at 6 h to mimic a decontamination procedure at the end of a working day. The proportion of the applied dose unabsorbed by 6 h was 80% and 10% for the acetone and the white spirit-based formulation, respectively. Small areas of the exposed site were tape stripped at 6 and 24 h to assess any lindane that may be associated with the stratum corneum. High levels were observed in the stratum corneum at 6 h exposure (up to 30% of the applied dose for the white spirit based formulation). However, this level had decreased by 24 h (by at least 90% of the amount found at 6 h). A gauze or gauze/shirt combination covering the application site between 6 and 24 h did account for some of this loss of lindane from the stratum corneum attributed to friction and removal of exfoliated cells. The unaccounted proportion was presumed to have been absorbed through the skin into the systemic circulation. This demonstrates the absorption of chemicals can occur from a depot in the stratum corneum even following a wash procedure.

The percutaneous absorption and skin distribution of lindane in man. II. In vitro studies.

1. The absorption of lindane through human skin was assessed in vitro using static diffusion cells with 50% aqueous ethanol as the receptor fluid. Four formulations of lindane were applied, three of which were commercial preparations. The dermal distribution of lindane within the skin was also examined, focusing particularly on any association of lindane to the stratum corneum. The results were then compared with a parellel in vivo study. 2. Two of the formulations contained white spirit as the predominant solvent, and lindane absorption was greatest from these preparations in terms of the percentage of the applied dose (15-25% by 24 h). Absorption was less from an aqueous spray dilution (3% by 24 h), with absorption from acetone being the least (< 1% by 24 h). Similar amounts of lindane penetrated by 24 h for the acetone and white spirit-based applications (approx. 8 micrograms). This supported the in vivo observation that similar plasma lindane levels were recorded following exposure to the acetone solution and the white spirit-based formulation A, although the lindane concentration in acetone was 40-fold higher. 3. For the acetone and water-based preparations, a soap/water swab of the skin surface at 6 h contained the majority of the applied dose (around 75%). Substantial amounts of lindane were recovered in tape-strippings taken at 6 h (representative of stratum corneum content) which were significantly greater than lindane in the remainder of the skin, for the acetone solution and formulation A. This provided a strong indication that lindane had accumulated in the stratum corneum, a property that has been linked with other lipophilic chemicals.

The effect of sulphur mustard on glutathione levels in rat lung slices and the influence of treatment with arylthiols and cysteine esters.

1. Sulphur mustard reacts directly with benzenethiols and cysteine esters in aqueous medium. 2. Benzenethiols diffuse into lung slices in short term culture. 3. Treatment of lung slices in short term culture with benzenethiols does not protect cellular glutathione from conjugation with sulphur mustard. 4. Following uptake of cysteine ester into lung slices cysteine is elevated but this does not protect cellular glutathione from sulphur mustard.