Effect of alachlor on hepatic cytochrome P450 enzymes in rats

Comparative phytotoxicity of Rac-metolachlor and S-metolachlor on rice seedlings

The toxicity of Rac-metolachlor and S-metolachlor on rice (IIYou92, Oryza sativa L.) seedlings was determined and compared in a hydroponics experiment. The elongation of shoot, main root, and the number of lateral roots were inhibited in both Rac- and S-metolachlor treatments. The 96 h- IC50 of Rac- and S-metolachlor were 12.32 and 9.44 μM for shoot, and 4.69 and 1.75 μM for root, respectively. The content of chlorophyll a, chlorophyll b and total chlorophyll of leaf treated by Rac-metolachlor was higher than that treated by S-metolachlor. The activities of superoxide dismutase, peroxidase, cytochrome P450 2E1, glutathione S-transferase, and the content of glutathione increased after herbicide exposure, and the activities or the content was higher in the S-metolachlor treatment than in the exposure to Rac-metolachlor. Ultrastructural studies revealed that Rac- and S-metolachlor had adverse effects on leaf cells, and S-metolachlor treatment caused higher damage.

Effect of zinc and paraquat co-exposure on neurodegeneration: Modulation of oxidative stress and expression of metallothioneins, toxicant responsive and transporter genes in rats

Oxidative stress is implicated in Parkinson's disease (PD). Metallothioneins (MT), cytochrome P450 IIE1 (CYP2E1) and glutathione S-transferases alpha4-4 (GSTA4-4) are involved in oxidative stress-mediated damage. Altered dopamine transporter (DAT) and vesicular monoamine transporter-2 (VMAT-2) are also documented in PD. The present study was undertaken to investigate the effect of Zn and PQ co-exposure on neurodegeneration in rats. A significant reduction was observed in spontaneous locomotor activity (SLA), striatal dopamine (DA) levels, tyrosine hydroxylase (TH) immunoreactivity, glutathione reductase (GR) and catalase activity along with increased lipid peroxidation (LPO) and glutathione peroxidase (GPx) activity after Zn and/or PQ exposure. Zn and/or PQ exposure increased gene expression of DAT, CYP2E1, GSTA4-4, MT-I and MT-II, but reduced the expression of VMAT-2. Protein expression analysis of TH, VMAT-2 and DAT showed results similar to those obtained with gene expression study. Zn and PQ co-exposure caused a more pronounced effect than that of individual exposure. The results obtained in this study suggest that, similar to PQ, Zn induced neurodegeneration via alterations in oxidative stress and expression of the above-mentioned genes. However, the effect of Zn+PQ was only slightly higher than that of alone, indicating that probably Zn and PQ follow some different molecular events leading to neurodegeneration.

Simultaneous toxic action of zinc and alachlor resulted in enhancement of zinc uptake by the filamentous fungus Paecilomyces marquandii

Microbial ability vary when pollutants exist together in the environment in comparison to the presence of single toxic compound. The influence of alachlor and zinc on the growth of the filamentous fungus Paecilomyces marquandii and its ability to eliminate alachlor and zinc has been studied. Their simultaneous presence in the polluted environment is very probable. In liquid cultures the pesticide (50 mg/l) was removed with the efficiency of 85% within 7 days. Beginning from the third day of culturing two derivatives of alachlor were found: N-(2',6'-diethylphenyl)-N-metoxymethyl-acetamide and unstable 2-chloro-N-(2',6'-diethylphenyl)-N-hydroxymethyl-acetamide, the first time detected as product of alachlor metabolisation by filamentous fungus. The herbicide elimination was not inhibited by zinc up to 1.0 mM of the metal content in the culture medium, 5.0-7.5 mM of the metal limited alachlor depletion by 30-50%, whereas a higher zinc concentration stopped this process. Zinc content in P. marquandii mycelium during the incubation in growth medium reached 10-20 mg/g of dry weight and was increased up to 99 mg/g by alachlor, however due to its presence a strong inhibitory effect on growth was observed. It was postulated that the increase in zinc binding by the growing mycelium of P. marquandii in the presence of the pesticide was connected with the changes in the wall and membrane composition induced by simultaneous toxic interaction of zinc and alachlor. Only 15-20% of bound zinc was detected in the cell wall of the fungus, whereas the amount of zinc loaded in the wall of mycelium originating from the cultures incubated in the alachlor presence increased to 60%. Additionally, changes in the profile of fatty acids of cultures with pesticide and metal addition were observed. P. marquandii strain seems to be promising for a potential industrial application. It can both effectively bind zinc and remove alachlor from the mixture of pollutants.

Cytotoxicity of chloroacetanilide herbicide alachlor in HepG2 cells independent of CYP3A4 and CYP3A7

Alachlor is cytotoxic to human hepatoblastoma HepG2s, a cell line that expresses constitutive CYP3A7 and dexamethasone (DEX)-inducible CYP3A4 and CYP3A7. CYP3A4 catalyzes alachlor N-dealkylation to 2-chloro-N-(2,6-diethylphenyl)acetamide (CDEPA), precursor of 2,6-diethylbenzoquinoneimine, putative reactive metabolite for rat nasal carcinogenicity. We hypothesized that HepG2 alachlor cytotoxicity would be mediated by CYP3A4/7 and increased with DEX. Here, we report time-dependent alachlor cytotoxicity (EC(50) approximately 500 microM and 264+/-17 microM at 6 and 24h, respectively) as assessed by lactate dehydrogenase leakage. DEX pretreatment (25 microM, 48 h) significantly increased CYP3A7-catalyzed luciferin 6' benzylether O-debenzylation, but had no effect on alachlor toxicity. Further, CYP3A4/7 inhibitor triacetyloleandomycin did not prevent, but rather potentiated, alachlor cytotoxicity. In agreement, CDEPA was less toxic than parent alachlor. HepG2 CYP3A4 activity was unaffected by 48 h DEX pretreatment; therefore, studies were done in DPX-2 cells, a HepG2 derivative engineered to overexpress pregnane-X receptor (PXR) that exhibits rifampicin (RIF)-inducible endogenous CYP3A4. Alachlor cytotoxicity in DPX-2 cells occurred over a concentration range equivalent to that in HepG2. CYP3A4 activity of DPX-2 cells treated with RIF (10 microM, 48 h) was twice that of untreated cells, but RIF did not increase alachlor toxicity. These results demonstrate that neither CYP3A4 nor CYP3A7 initiate a pathway leading to a toxic alachlor metabolite.

Chemopreventive properties of trans - resveratrol against the cytotoxicity of chloroacetanilide herbicides in vitro

The beneficial effect of trans-resveratrol (RESV) on health is well documented. Our aim was to study the putative preventive effect of RESV on the cytotoxicity of frequently used herbicides (alachlor, acetochlor). Estrogen receptor positive (ER+) MCF-7 human mammary carcinoma, HepG2 (ER+) human hepatocellular carcinoma and VERO estrogen receptor negative (ER-) non-transformed monkey fibroblast cell lines were treated with alachlor and acetochlor (2-500 microg/ml) as toxic agents, and RESV (10 microM) as preventive agent. The MTT dye reduction assay was performed to test cytotoxicity, and flow cytometry to test cell proliferation and apoptosis. RESV is not cytotoxic in the concentration range of 1-100 microM on neither cell lines examined after 24 h, but cytotoxic on Vero and MCF-7 cells at 100 microM after 48h, and on all three cell lines after 72 h. On both ER+ cell lines a stimulation of viability occurs in the low concentration range (0.5-12.5 microM) as detected by the MTT assay. Cell cycle analysis of the culture shows a significant increase of S-phase cells at low concentrations of RESV (10-50 microM) and a decrease in the 100-200 microM concentration range. The ratio of apoptotic cells significantly increases after the administration of 50 microM RESV, depending on the incubation time. The cytotoxicity of 20-65 microg/ml alachlor and 10-65 microg/ml acetochlor was significantly decreased by the addition of 10 microM RESV in Vero ER- cells whereas no significant change was detected on ER+ cell lines MCF-7 and HepG2. These results show that RESV protects non-transformed ER- cells, but has no such effect on ER+ tumor cells.

Isolation and characterization of alachlor-degrading actinomycetes from soil

Alachlor (2-cloro-N-(methoxymethyl)-N-(2,6-diethylphenyl)-acetamide) is an extremely toxic and highly mobile herbicide that is widely used for pre-emergence control of grasses and weeds in many commercial crops in Brazil. In order to select soil actinomycetes able to degrade this herbicide, fifty-three actinomycete strains were isolated from soil treated with alachlor using selective conditions and subjected to in vitro degradation assays. Sixteen isolates were shown to be tolerant to high concentrations of the herbicide (up to 720 mg L(-1)), and six of these were able to grow and degrade >/= 50 alachlor (72 mg L(-1)) in mineral salts medium. Morphological and phylogenetic analysis enabled the assignment of the alachlor-degrading strains to the genus Streptomyces. Strain LS151 was related to the type strains of Streptomyces capoamus/Streptomyces galbus, whereas strains LS143 and LS153 were related to Streptomyces bikiniensis. The remaining strains, LS166, LS177 and LS182, were similar in morphological features and recovered in a single cluster based on 16S rDNA sequence analysis, but shown to be distinct on the basis of genomic fingerprint data (rep-PCR). Though a definitive taxonomic assignment of alachlor-degrading strains was not possible, these data indicate that ability to degrade this pesticide was detected in different Streptomyces taxa.

The herbicide metolachlor induces liver cytochrome P450s 2B1/2 and 3A1/2, but not thyroxine-uridine dinucleotide phosphate glucuronosyltransferase and associated thyroid gland activity

Metolachlor (2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl) acetamide) is widely used internationally as a corn and cotton herbicide. The metolachlor effects noted in rats during testing for U.S. pesticide registration include increased liver weight and hepatocarcinogenicity associated with eosinophilic foci. These properties, plus nongenotoxicity, are also characteristic of the prototypical rat liver tumor promoter, phenobarbital. Phenobarbital induces hepatic cytochrome P450s CYP2B1/2 and CYP3A1/2 and thyroxine (T(4))-UDP-glucuronosyltransferase (T(4)-UGT), which enhances thyroxine clearance and thus indirectly increases thyroid gland activity. Because other chloroacetanilide herbicides are known to similarly affect rat thyroid gland, this study tested the hypothesis that metolachlor would have these additional phenobarbital-like effects on liver, especially that of T(4)-UGT induction with consequential stimulation of thyroid gland. Effects of metolachlor, fed to male Sprague-Dawley rats for 14 days at the carcinogenic dose of 3000 ppm, were compared to those of equimolar phenobarbital. Liver microsomal CYP2B1/2 and CYP3A1/2 were probed by immunoblotting and T(4)-UGT was measured enzymatically. Serum T(4), triiodothyronine (T(3)), and thyroid-stimulating hormone (TSH) and thyroid follicular epithelial cell morphology and proliferation were used to assess thyroid gland activity. Metolachlor induced CYP2B1/2 and CYP3A1/2 proteins, but unlike phenobarbital, did not affect T(4)-UGT activity. In agreement, serum T(4), T(3), or TSH were unaffected by metolachlor. Also, no significant effects of metolachlor on thyroid gland morphology or follicular epithelial cell height or proliferation were observed. These data demonstrate that metolachlor is an inducer of hepatic CYP2B1/2 activity. But unlike the prototypical CYP2B1/2 inducer phenobarbital, metolachlor does not cause an increase in T(4)-glucuronidation and thyroid gland activation.