Environmental polycyclic aromatic hydrocarbon (PAH) exposure and DNA damage in Mexican children.

Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous pollutants presenting a public health risk, particularly to children, a vulnerable population. PAHs have genotoxic and carcinogenic properties, which depend on their metabolism. Many enzymes involved in PAH metabolism, including CYP1A1, CYP1B1, GSTM and GSTT are polymorphic, which may modulate the activation/deactivation of these compounds. We evaluated PAH exposure and DNA damage in children living in the vicinity of the main petrochemical complex located in the Gulf of Mexico, and explored the modulation by genetic polymorphisms of PAH excretion and related DNA damage. The participants (n=82) were children aged 6-10y attending schools near the industrial area. Urinary 1-hydroxypyrene (1-OHP; a biomarker of PAH exposure) was determined by reverse-phase-HPLC; DNA damage by the comet assay (Olive Tail Moment (OTM) parameter); CYP1A1*2C and CYP1B1*3 polymorphisms by real time-PCR; and GSTM1*0 and GSTT1*0 by multiplex PCR. The median value of 1-OHP was 0.37µmol/mol creatinine; 59% of children had higher 1-OHP concentrations than those reported in environmentally exposed adults (0.24µmol/mol creatinine). A stratified analysis showed increased DNA damage in children with 1-OHP concentrations greater than the median value. We observed higher 1-OHP concentrations in children with CYP1A1*2C or GSTM1*0 polymorphisms, and a positive influence of CYP1A1*2C on OTM values in children with the highest PAH exposure. The data indicate that children living in the surroundings of petrochemical industrial areas are exposed to high PAH levels, contributing to DNA damage and suggesting an increased health risk; furthermore, data suggest that polymorphisms affecting activation enzymes may modulate PAH metabolism and toxicity.

Increased micronucleus frequencies in reticulocytes of children exposed to industrial pollution: oxidative stress and the OGG1 S326C polymorphism.

We examined possible early-effect biomarkers and polymorphisms of susceptibility in primary school children living near the Atoyac River in central México, which receives waste from multiple industries. We observed a significant increase in micronucleated reticulocytes associated with the oxidative stress index (OSI) and the OGG1 GG (S326C) genotype, and a significant decrease of reticulocytes carrying the transferrin receptor, inversely correlated with OSI.

Babesia bigemina sexual stages are induced in vitro and are specifically recognized by antibodies in the midgut of infected Boophilus microplus ticks.

Babesia bigemina, a causative agent of bovine babesiosis, is transmitted from one bovine to another only by infected ticks. The life cycle of B. bigemina includes a sexual phase in the tick host; however, molecules from sexual stages of any Babesia species have not been characterized. This is the first report of the induction of sexual stages of any Babesia species in vitro, free of tick antigens. Intraerythrocytic parasites were cultured in vitro for 20h using an induction medium. Extraerythrocytic parasites were first seen 3h post induction; elongated stages with long projections appeared at 6h post induction and by 9h they paired and fused to form larger stages. Round zygotes appeared 20h post induction. Moreover, by using Percoll gradients, sexual stages were purified free of contaminating intraerythrocytic stages. Purified parasites were used to generate polyclonal antibodies, which specifically bound to antigens expressed in sexual stages induced in vitro, but not to antigens expressed in intraerythrocytic stages. Importantly, these antibodies specifically identified sexual stages from midguts of female Boophilus microplus ticks fed on infected cattle.

Hepatic CYP1A, 2B, 2C, 2E and 3A regulation by methoxychlor in male and female rats.

The effect on liver cytochrome P450 (CYP) by i.p. injections of methoxychlor (MXC) in corn oil at 0, 100, 150, 200 or 250 mg/kg twice daily for 3 days was investigated in adult male and female Wistar rats. The MXC injection (100 mg/kg b.w.) caused a similar increase of total CYP content in males and females as compared with controls who received the vehicle only. In males, this increase continued up to 250 mg/kg. As to the induction of specific CYP activities, the effect of MXC was found to be sex dependent with three different patterns. Males showed the greatest increases of ethoxy- and methoxyresorufin-O-dealkylase (EROD and MROD, respectively), two CYP1A1/1A2-related activities. On the contrary, females were more responsive than males for pentoxyresorufin-O-dealkylase (PROD) and benzyloxyresorufin-O-dearylase (BROD), two CYP2B-related activities. Finally, p-nitrophenol hydroxylase (PNPH), a CYP2E1-related activity, showed a similar small, although statistically significant, increase for both sexes. As to CYP apoprotein levels, CYP1A1 and CYP2B1/2B2 showed greater increases in females than in males; whereas, interestingly, CYP2E1 induction was higher in males than in females. These results indicate overall that gender modulates CYP expression after MXC injection both qualitatively and quantitatively, and, therefore, this pesticide is not a pure PB inducer. Moreover, the statistically significant increase of CYP3A2 apoprotein expression observed in females and also, to a lower extent, in males, and the decrease of CYP2C11 apoprotein found in males, two sex-related enzymes, may explain the reported endocrine disrupting effect of MXC. The relevance of the different patterns of rat liver CYP induction observed after MXC treatment, in relationship to the speculated endocrine disrupting potential of MXC in humans potentially exposed to this pesticide, needs further investigation.

Trifluoroacetylated adducts in spermatozoa, testes, liver and plasma and CYP2E1 induction in rats after subchronic inhalatory exposure to halothane.

The induction of cytochrome P450 (CYP) 2E1 in testes and liver and the presence of trifluoroacetylated (TFA) adducts in spermatozoa, testes, liver and plasma were investigated in rats subchronically exposed by inhalation to halothane (15 ppm/4 h/day/5 days/week/9 weeks). After halothane exposure, p-nitrophenol hydroxylase (p-NPH) activity increased 3.2-fold and CYP2E1 apo-protein content 7-fold in testes, whereas in liver, p-NPH increased 2.3-fold and CYP2E1 apoprotein content 1.4-fold. These results suggest a differential inductive effect of halothane on CYP2E1 in these tissues. Moreover, TFA adducts were present in microsomes of testis and liver and in plasma of halothane-treated rats. The immunoblot analysis of testicular microsomes showed two intense TFA protein bands of 63 and 59 kDa, whereas in liver three intense bands of 100, 76 and 63 kDa were observed. Bands of similar molecular weights to those observed in liver were detected in the plasma of halothane-treated animals. In addition, TFA adducts were detected by immunofluorescence in spermatozoa, probably in the acrosome and/or perinuclear theca region, and in the distal tail of spermatozoa. The increase in CYP2E1 apoprotein and p-NPH activity observed in testis and liver microsomes suggests that halothane induces its own biotransformation both hepatically and extrahepatically and in addition, that the nature of the TFA adducts will depend on the proteins present in each tissue. Also, the presence of TFA adducts in spermatozoa may result from the activation of halothane in the reproductive tract. The detailed mechanism of TFA adduct formation and its consequences on the spermatozoa function remain to be fully clarified.

Inhibitory action of halothane on rat masculine sexual behavior and sperm motility.

Adult male rats were exposed to inhale halothane in the following regime: 15 ppm/4 h/5 days/week/9 weeks. Sexual behavior observations and sperm motility test were made before halothane exposure (0 days) and at 15, 30, 45 and 60 days of exposure. Fifteen days after halothane exposure, this anesthetic inhibited the proportion of animals displaying ejaculation. In those animals ejaculating, halothane produced an inhibition of masculine sexual behavior reflected as an increase in the intromission latency, number of mounts and postejaculatory interval. At 30 days after exposure, only an increase in the intromission latency was observed. At 45 and 60 days, the inhibitory effect of halothane on sexual behavior disappeared. Similarly, at 15 and 30 days, but not at 45 or 60 days of halothane exposure, a reduced sperm motility was observed. Such transient effects of halothane suggest the development of tolerance to the inhibitory actions of this anesthetic on sexual behavior and sperm motility. These halothane effects are in line with an inhibition of masculine sexual behavior after stimulation of the GABAergic system.