Masanori Terasaki

Acetylcholinesterase inhibitory activity and chemical composition of commercial essential oils.

Commercially available essential oils extracted from Artemisia dracunculus L., Inula graveolens L., Lavandula officinalis Chaix, and Ocimum sanctum L. and the components of these oils were screened by the microplate assay method for determining their acetylcholinesterase (AChE) inhibitory activity. The composition profiles of the oils were characterized by gas chromatography-mass spectrometry (GC-MS) analysis, and the relationships between the oil components and the AChE inhibitory activity of the oils were outlined. The results showed that all of the oils, except that of A. dracunculus from Hungary, exhibited AChE inhibitory activity, and the A. dracunculus oil from France showed the most potent inhibitory activity [50% inhibition concentration (IC(50)) = 0.058 mg/mL]. The AChE inhibitory activity of I. graveolens oil has not been reported to date, and this study is the first to reveal this activity in the oil. Among the essential oil components, five components, namely, 1,8-cineole, α-pinene, eugenol, α-terpineol, and terpinen-4-ol, showed AChE inhibitory activity, with IC(50) values of 0.015, 0.022, 0.48, 1.3, and 3.2 mg/mL, respectively. Eugenol, in particular, was found to be a potent AChE inhibitor along with determination of the IC(50) value, a finding that has been reported for the first time in this study. However, the ratio of the contribution of the active components, including a novel AChE inhibitor, to the observed AChE inhibitory activity of the essential oils was not very high. The results of this study raise concerns about the AChE inhibitory activity of widely produced and readily accessible commercial essential oils.

Acute toxicity of parabens and their chlorinated by-products with Daphnia magna and Vibrio fischeri bioassays.

The acute toxicity of 21 parabens and their chlorinated derivatives was investigated by means of two toxicity bioassays: Daphnia magna immobilization test and the inhibition of bioluminescence of Vibrio fischeri. The median effective concentration (EC50) values of the tested parabens ranged from 2.2 to 62 mg l−1 in the D. magna test and from 0.0038 to 5.9 mg l−1 in the V. fischeri test at 15 min after exposure. The toxicity of dichlorinated methyl‐ and n‐propylparaben, the most commonly used preservatives in cosmetics, toward D. magna was 3.9‐ and 2.8‐fold that of their corresponding parent compounds. Toxicity toward D. magna showed a linear relationship with log P, indicating that toxicity increases with increasing hydrophobicity. On the other hand, the correlations of toxicity toward V. fischeri with hydrophobicity and with the degree of chlorination were poor. In addition, the results of the present study indicated that the V. fischeri test was more sensitive than the D. magna test for the determination of the acute toxicity of parabens. A complete assessment of the ecological and toxicological risks of parabens may require the examination of chlorinated parabens as well as the parent pollutants, as described in the present study. Copyright

Determination of chlorinated by-products of parabens in swimming pool water

We describe the determination of trace amounts of chlorinated parabens, i.e. disinfection by-products, in swimming pool water, using gas chromatography-mass spectrometry with selected ion monitoring (GC-MS-SIM). A dichlorinated by-product of isopropylparaben was detected at levels of up to 25 ng L−1. Further, a dichlorinated by-product of methylparaben and a monochlorinated by-product of benzylparaben were present in concentrations lower than the limit of quantification. Benzylparaben, the parent compound, was also detected at concentrations of up to 28 ng L−1. Thus, in this study, chlorinated parabens were detected and quantified for the first time as disinfection by-products in swimming pool water. The results of this study have raised concerns regarding the chlorinated by-products of active ingredients used in personal care products.

Paraben-chlorinated derivatives in river waters

This article reports the first identification of paraben-chlorinated derivatives in river water. Parabens are widely used as preservatives in pharmaceuticals and personal care products. Parabens can be easily chlorinated by chlorinated tap water. The resulting chlorinated derivatives might pose a higher potential risk to humans and ecosystems than the corresponding parent parabens. However, the occurrence of such derivatives in rivers remains unknown so far. We studied 23 parabens and their chlorinated derivatives from rivers receiving effluents from sewage treatment plants in Shizuoka city, in the central Pacific region of Japan. The compounds were extracted by solid-phase extraction with a styrene polymer sorbent, trimethylsilyl-derivatized, and then identified by gas chromatography–mass spectrometry. Six chlorinated parabens and their primary degradation products, two chlorinated hydroxybenzoic acids, were found for the first time in river water. Moreover, in river water, chlorinated derivatives preferentially partition into the suspended-solid phase.

Evaluation of estrogenic activity of parabens and their chlorinated derivatives by using the yeast two‐hybrid assay and the enzyme‐linked immunosorbent assay

We assessed the estrogen agonist activities of 21 parabens and their chlorinated derivatives by using yeast two-hybrid assays incorporating either the human or medaka (Oryzias latipes) estrogen receptor alpha (hERalpha and medERalpha, respectively), and by using hERalpha competitive enzyme-linked immunosorbent assay (ER-ELISA). In the two-hybrid assay with hERalpha, five parabens and three chlorinated derivatives exhibited estrogenic activity, and their relative activity (17beta-estradiol [E2] = 1) ranged from 2.0 x 10(-5) to 2.0 x 10(-4), with the highest activity observed in i-butylparaben. In the medERalpha assay, six parabens and six chlorinated derivatives exhibited estrogenic activity and their relative activity ranged from 2.7 x 10(-5) to 3.5 x 10(-3), with the highest activity observed in benzylparaben, its monochlorinated derivative, i-butylparaben, and n-butylparaben. Although medERalpha demonstrated an activity to E2 that was three times lower than that demonstrated by hERalpha, medERalpha has a higher sensitivity to parabens than hERa (1.3-8.9 times). Five parabens and two chlorinated derivatives exhibited a binding affinity to ERa in the ER-ELISA; of the parabens, i-butylparaben exhibited the strongest binding affinity. The yeast two-hybrid assay and the ER-ELISA also revealed that many of the assayed chlorinated parabens were much weaker than the parent compound. In addition, the results mainly showed that parabens with a bulk substituent (e.g., i-butyl and benzyl groups) had a higher activity than those with a sterically small substituent. It is considered that derivatization masks the apparent estrogenic activity of parabens, but the resulting chlorinated compounds may represent a potential hazard and therefore other toxicity tests should be performed to determine the toxicity of the chlorinated derivatives.

Rat hyperactivity by bisphenol A, but not by its derivatives, 3-hydroxybisphenol A or bisphenol A 3,4-quinone

Detoxification in the central nervous system is largely unknown. The mechanism of neurotoxicity of bisphenol A, a toxic environmental chemical remains obscure. We examined the effects of bisphenol A, and its derivatives, 3-hydroxybisphenol A and bisphenol A 3,4-quinone on rat behavior as possible metabolites of bisphenol A. A single intracisternal administration of bisphenol A (20 μg equivalent to 87 nmol) into 5-day-old male Wistar rats caused significant hyperactivity at 4-5 weeks of age. It was about 1.3 fold more active in the nocturnal phase than control rats. However, neither 3-hydroxybisphenol A nor bisphenol A 3,4-quinone at the same amount (87 nmol) increased the spontaneous motor activity. Gas chromatographic-mass spectrometric (GC-MS) analyses of the treated brain revealed that 7% of the parent chemical resided in the brain at 8 weeks of age, but its derivatives were not found. This suggested a difference in metabolic turnover of these compounds or a difference in their stabilities. We conclude that bisphenol A per se caused hyperactivity in the rat, eliminating the possibility that possible metabolic forms of bisphenol A, 3-hydroxybisphenol A and bisphenol A 3,4-quinone have the ability to elicit rat hyperactivity, probably because of longer-lasting residence of the parent compound in the brain.

Chronic toxicity of parabens and their chlorinated by-products in Ceriodaphnia dubia.

The chronic toxicity of 12 compounds of parabens and their chlorinated by‐products was investigated using 7‐day Ceriodaphnia dubia test under static renewal condition in order to generate information on how to disinfect by‐products of preservatives that are discharged in aquatic systems. The mortality and inhibition of reproduction tended to increase with increasing hydrophobicity and decreased with the degree of chlorination of parabens. The EC50 values for mortality, offspring number, and first brood production ranged between 0.30–3.1, 0.047–12, and 1.3–6.3 mg L−1, respectively. For the number of neonates, the most sensitive endpoint, the no‐observed‐effect concentration (NOEC) and lowest‐observed‐effect concentration (LOEC) values ranged from 0.63 to 10 mg L−1 and from 1.2 to 19 mg L−1, respectively. Methylparaben (MP), benzylparaben (BnP), and dichlorinated BnP (Cl2BnP) elicited a significant decrease in offspring numbers even at their lowest concentration tested; the NOEC for these compounds was determined to be less than the lowest test concentration (1.3, 0.04, and 0.63 mg L−1 for MP, BnP, and Cl2BnP, respectively). Propylparaben (PP), chlorinated PP, isopropylparaben (iPP), and chlorinated iPP exhibited nonmonotonic concentration‐dependent response; their NOEC and LOEC values could not be determined. The multivariate approach involving principal component analysis and hierarchical cluster analysis revealed four groups that corresponded to the toxicological profiles of parabens. Our results suggested that disinfection of parabens by chlorination could reduce aquatic toxicity of original compounds. The findings obtained in our study together with the data available on paraben concentrations in aquatic systems can be used to perform preliminary risk assessment by comparing the predicted environmental concentration (PEC) with the predicted no‐effect concentration (PNEC) for the marine aquatic environment. The calculated PEC/PNEC ratios ranged from 0.0012 to 0.2, with the highest value observed in MP. This suggested that there are negligible environmental risks for aquatic organisms at current use levels.

Development and validation of chemical and biological analyses to determine the antiestrogenic potency of resin acids in paper mill effluents.

This study combined chemical analysis and bioassays of paper mill effluents and their components in order to determine their antiestrogenic activity. The bioassay comprised a yeast two-hybrid assay incorporating the estrogen receptor alpha (hERalpha) and an hERalpha competitive enzyme-linked immunosorbent assay (ELISA). Samples were fractionated by solid phase extraction (SPE) with a C18 disk and a Florisil cartridge to obtain four fractions. The final fraction, eluted with methanol from the Florisil cartridge after pre-extraction by the C18 disk, was the most active in the two-hybrid assay, and its antiestrogenic potency, expressed as the equivalent concentration to 4-hydroxytamoxifen (OHT), was 277 nM. Seven resin acids had antiestrogenic activity in the active fraction as determined by gas chromatography/mass spectrometry (GC/MS), and their concentration levels ranged from 0.11 to 12 microg/L. All the resin acids exhibited greater activity than OHT; their activity relative to OHT ranged from 2.8- to 4.0-fold in the yeast two-hybrid assay. Based on the chemical analysis data and relative potency of resin acids from the yeast two-hybrid assay, the contribution ratio of resin acids accounted for 72% of the observed antiestrogenic activity of the extract. Furthermore, no resin acid showed any affinity for the estrogen receptor in the ELISA. This study showed that analysis combining the SPE method and the yeast two-hybrid assay is likely to be effective for the comprehensive monitoring of resin acids in paper mill industrial discharge areas.

Identification and accumulation of aromatic sensitizers in fish from paper recycling in Japan

Aromatic sensitizers and related compounds (SRCs) originating from thermal recording material as impurities in waste paper have been detected in aquatic environments near cities where the paper industry is flourishing. In the present study, the levels of exposure to such SRCs and the stable isotope ratios (δ(13)C and δ(15)N) in different fish species (Konosirus punctatus, Takifugu niphobles, and Tribolodon hakonensis) were analyzed. These fish species were collected from the vicinity of waste paper recycling plants in Japan. Eleven SRCs were identified in fish muscle at total concentration levels (ΣSRCs) of 64 to 818 ng/g wet weight (mean 181 ng/L wet wt). The dominant SRCs in the fish samples were 1,1-di(4-methylphenyl)ethane, 1,2-bis(3-methylphenoxy)ethane, and 1,4-dibenzyloxybenzene. Stable isotope ratios showed that, although three species feed on the same trophic level, K. punctatus and T. niphobles live in waters farther offshore than those in which T. hakonensis live. The contributions of various factors to the accumulation were also assessed. The lipid content (r(2) = 0.512, p < 0.001) was found to be the significant factor that influenced accumulation of SRCs in fish. The results also revealed significant positive correlation between the accumulation patterns and SRC components in water (r(2) = 0.512-0.658, all p values <0.05), but they showed negative correlations between the SRCs in fish and log K(OW) values. This suggests that the aqueous route is the predominant route for the accumulation of SRCs in fish. This is the first study on the accumulation of aromatic sensitizers in aquatic biota.

The feasibility of using mosquitofish (Gambusia affinis) for detecting endocrine‐disrupting chemicals in the freshwater environment

We evaluated the utility of gene-transcriptional responses in the liver of mosquitofish (Gambusia affinis), a species introduced to many countries and therefore widely available, for detecting endocrine-disrupting activity in water. Exposure to β-naphthoflavone, an aryl hydrocarbon receptor (AhR) agonist, significantly increased the transcript of the cytochrome P4501A gene (cyp1a), peaking at 24 h, in both sexes at concentrations of 10 µg/L or more. 17β-Estradiol (E(2) ) at 500 ng/L increased the number of males showing gene transcription of precursors of yolk protein, vitellogenin (Vtga, Vtgb, and Vtgc), at 24, 48, and 72 h. Exposure for 48 h to bisphenol A (BPA), an estrogen mimic, also increased vtg-positive males at 1 mg/L or more. Leachate from a Japanese stable-type landfill significantly increased vtg-positive males after 48 h exposure, and the in vitro activity of the leachate against the estrogen receptor (ER) was estimated as an E(2) equivalent of 240 ng/L by yeast transfected with the ER. Chemical analysis showed that major contributors to the ER activation were BPA and 4-tert-octylphenol. This leachate and drainage water from a control-type landfill had AhR activities, estimated by yeast with the AhR, but had no significant effect on cyp1a transcription. These results showed that mosquitofish are suitable for detecting in vivo AhR and ER effects, but are insensitive to E(2).