Gas chromatographic–mass spectrometric determination of 4-nonylphenols and 4-tert-octylphenol in biological samples

A simple and rapid method is described for the GC–MS determination of 4-nonylphenols (NOs) and 4-tert-octylphenol (OC) in biological samples. The NOs and OC in the sample are extracted with acetonitrile and the lipid in the sample extract is eliminated by partitioning between hexane and acetonitrile. After Florisil PR column clean-up, the sample extract is analyzed by GC–MS in the selected ion monitoring (SIM) mode. Average recoveries in pale chub (fish) and corbicula (shellfish) are 86.0 and 93.4% for NOs, and 95.8 and 96.4% for OC, respectively, spiked at the levels of 1.0 μg of NOs and 0.1 μg of OC per 5 g of fish and shellfish samples. The detection limits are 20 ng/g for NOs and 2 ng/g for OC.     

Stir bar sorptive extraction with in situ derivatization and thermal desorption-gas chromatography--mass spectrometry for measurement of phenolic xenoestrogens in human urine samples

A high-sensitivity analytical method that uses stir bar sorptive extraction (SBSE) with in situ derivatization and thermal desorption (TD)-gas chromatography-mass spectrometry (GC-MS) for the simultaneous measurement of trace amounts of phenolic xenoestrogens (PXs), such as 2,4-dichlorophenol (DCP), 4-tert-butylphenol (BP), 4-tert-octylphenol (OP), 4-nonylphenol technical isomers (NP), pentachlorophenol (PCP) and bisphenol A (BPA), in human urine samples was developed. The urine sample (1 ml) was de-conjugated by adding beta-glucuronidase and sulfatase. Then, protein precipitation was performed by the addition of acetonitrile. After centrifugation, the supernatant was diluted with purified water and subjected to SBSE with in situ derivatization and TD-GC-MS. The detection limits of DCP, BP, OP, NP, PCP and BPA in the urine samples were 20, 10, 10, 50, 20 and 20 pg ml-1 (ppt), respectively. The calibration curves for PXs were linear and had correlation coefficients higher than 0.99. The average recoveries of those analytes in the urine samples were higher than 95% (RSD: <10%, n=6) with correction using the added surrogate standards. This simple, accurate, sensitive and selective method can be used in the determination of PXs in human urine samples.     

Metabolic pathway of xenoestrogenic short ethoxy chain-nonylphenol to nonylphenol by aerobic bacteria, Ensifer sp. strain AS08 and Pseudomonas sp. strain AS90

Ensifer sp. strain AS08 and Pseudomonas sp. strain AS90 degrading short ethoxy (EO) chain-nonylphenol (NP) [NPEO_av2.0 containing NP mono- ∼ tetraethoxylates (NP1EO ∼ NP4EO); average 2.0 EO units] were isolated by enrichment cultures. Both strains grew on NP but not on octyl- and nonylphenol polyethoxylates (NPEOs) (average 10 EO units). Growth and degradation of NPEO_av2.0 was increased with increased concentrations of yeast extract (0.02–0.5%) in a culture medium. Culture supernatants of both strains grown on NPEO_av2.0 were analyzed by high-performance liquid chromatography, showing degradation of NP4EO–NP1EO. The metabolites from nonylphenol diethoxylate (NP2EO) by resting cells of both strains were identified by gas chromatography–mass spectrometry as nonylphenoxyethoxyacetic acid, NP1EO, nonylphenoxyacetic acid (NP1EC), and NP, while those from NP1EO were identified as NP1EC and NP. Cell-free extracts from strain AS08 grown on NPEO_av2.0 dehydrogenated NPEOs, NPEO_av2.0, NP2EO, NP1EO, and PEG 400, but the extracts were inactive toward di- ∼ tetraethylene glycol. Aldehydes were formed in the reaction mixture of each substrate with cell-free extracts. From these results, the aerobic metabolic pathway for short EO chain-NP is proposed: A terminal alcohol group of the EO chain is oxidized to a carboxylic acid via an aldehyde, and then one EO unit is removed. This process is repeated until NP is produced.English edition: The paper was edited by a native speaker through KN international ()     

Studies on octylphenoxy surfactants: X. Effect of oxyethylene chain length on ethylene production by cowpea and mung bean and comparison with linear alcohol hydrophobes

The effects of ethoxy (EO) chain length on surfactant-induced ethylene production for selected octylphenoxy (OP) and linear alcohol (LA) surfactants were established using primary leaves of cowpea (Vigna unguiculata (L.) Walp. subsp. unguiculata Dixielee) seedlings. OP surfactant-induced ethylene production was concentration dependent and decreased log linearly with increasing EO content. C_12–15 LA-induced ethylene production decreased log linearly with increasing EO content at 0.1%; however, at 1.0% the relationship was curvilinear with maximum response at 7 EO. Relationships for the C_9–11 and C₉ LA series were nonlinear with greatest biological activity at intermediate (8–12) EO content. Short EO chain length OP surfactants were only slightly water soluble, and induced low levels of ethylene production and phytotoxicity. Addition of OP+1EO to a long chain, water soluble, non-ethylene inducing surfactant (OP+40EO) solution significantly increased ethylene production by OP+1EO in cowpea. A similar response was found for surfactant-induced phytotoxicity and EO chain length as between ethylene production and EO content. Similar EO chain length and ethylene production relationships were found for germinating mung bean (Vigna radiata (L.) R. Wilcz) seeds as for ethylene production and phytotoxicity in cowpea. Radicle growth was markedly inhibited by OP surfactants with an EO chain length of 10 or less and, in some cases, radicles were irreversibly damaged by ethylene inducing surfactants.     

Application of the OECD 301F respirometric test for the biodegradability assessment of various potential endocrine disrupting chemicals

The biodegradability of several potential endocrine disrupting compounds, namely 4-n-nonylphenol (4-n-NP), nonylphenol monoethoxylate (NP1EO), nonylphenol diethoxylate (NP2EO), bisphenol A (BPA), triclosan (TCS), di-(2-ethylhexyl)-phthalate (DEHP), perfluorooctanoate (PFOA) and perfluorononanoate (PFNA) was evaluated in this study, using OECD method 301F (manometric respirometry test) and activated sludge as inoculum. According to the results, 4-n-NP and BPA meet the strict definition of ready biodegradability and they are not expected to be persistent during the activated sludge process. Partial biodegradation was observed for DEHP (58.7+/-5.7%, n=3), TCS (52.1+/-8.5%, n=3) and NP1EO (25.9+/-8.1%, n=3), indicating their possible biodegradation in wastewater treatment systems, while no biodegradation was observed for NP2EO, PFOA and PFNA. Experiments in the co-presence of a readily biodegradable compound showed the absence of co-metabolic phenomena during 4-n-NP, BPA and TCS biodegradation. Using first order kinetics to describe biodegradation of the target compounds, half-lives of 4.3+/-0.6, 1.3+/-0.2, 1.8+/-0.5, 6.9+/-2.6 days were calculated for 4-n-NP, BPA, TCS and DEHP, respectively. Toxicity tests using marine bacterium Vibrio fischeri showed that biodegradation of 4-n-NP, NP1EO, BPA and TCS is a simultaneous detoxification process, while possible abiotic or biotic transformations of NP2EO, DEHP, PFOA and PFNA during respirometric test resulted to significant increase of their toxicities.     

Measurement of Phenolic Environmental Estrogens in Women with Uterine Leiomyoma

Objectives

To investigate the effect of phenolic environmental estrogens on uterine leiomyoma from the perspective of clinical epidemiology.

Methods

Urine and blood samples were collected from Han women with uterine leiomyoma and women without uterine leiomyoma, living in Nanjing, China, between September 2011 and February 2013. A total of 156 urine samples and 214 blood samples were collected from the uterine leiomyoma group and 106 urine samples and 126 blood plasma samples from the control group. Bisphenol A (BPA), nonylphenol (NP) and octylphenol (OP) concentrations were determined by solid-phase extraction (SPE) coupled with liquid chromatography-tandem mass spectrometry (HPLC-MS/MS).

Results

Phenolic environmental estrogens in the uterine leiomyoma and control groups were compared based on: gravida>3 and gravida ≤ 3. In participants with gravida>3, urine OP concentration was significantly (P<0.05) higher in the uterine leiomyoma group than in the control group. In participants with gravida ≤ 3, urine NP concentration was significantly (P<0.05) higher in the uterine leiomyoma group compared to controls. Despite obstetric history, urine BPA mean exposure concentration was significantly (P<0.05) different between uterine leiomyoma group and control group. The urine BPA concentration was not significantly (P>0.05) different between gravida>3 and gravida ≤ 3 patients. There was no significant (P>0.05) difference in plasma concentrations of BPA, OP and NP between the leiomyoma group and control group. Mean exposure concentration and range of distribution of BPA, OP and NP plasma concentration differed between the uterine leiomyoma and control group.

Conclusion

Exposure level of phenolic environmental estrogens in human was related with leiomyoma tumorigenesis.     

Genotoxic effects of environmental estrogen-like compounds in CHO-K1 cells

Some environmental estrogen-like compounds, such as bisphenol A (BPA), 4-nonylphenol (NP), 4-octylphenol (OP), propyl p-hydroxybenzoate (P-PHBA), and butyl p-hydroxybenzoate (B-PHBA), synthetic estrogen, diethylstilbestrol (DES), and natural estrogen, 17beta-estradiol (E2), were studied for their genotoxicity in CHO-K1 cells using sister-chromatid exchange (SCE), chromosome aberration (CA), and DNA strand break (comet) assays. Six of the chemicals, excluding E2, caused DNA migration in the comet assay and induced SCEs at one or more of the highest doses. Among the chemicals, OP produced an especially high incidence of SCEs. Structural CA was induced by five of the chemicals, excluding OP and NP, and BPA, E2, and DES also induced aneuploid cells. E2 and DES particularly increased the rate of polyploidy at high doses. The incidence of colchicine-mitosis-like (c-mitotic) figures suggesting spindle disrupting effects was also detected with five of the chemicals, excluding OP and NP, and six of the chemicals, excluding E2, caused endoreduplication (ERD), a form of nuclear polyploidization induced by block of cell cycle at G2 phase, at one or more high doses. Our present results suggest that OP and NP cause repairable DNA damage, including SCEs, and do not result in CA, while the damage caused by DES, BPA, P-PHBA, and B-PHBA results in the induction of CAs together with SCEs probably because of imperfect repair. We are unable to explain the observation that the DNA damage caused by E2 resulted in CA induction but not DNA migration or SCE induction, except for speculating that the DNA damage is different from that caused by DES and the estrogen-like chemicals. Our findings also suggest that E2, DES and BPA have aneuploidogenic properties, and that the former two of chemicals also are polyploidy-inducing agents.     

Biosorption of nonylphenol on dead biomass of Rhizopus arrhizus encapsulated in chitosan beads

The nonylphenol (NP) biosorption and desorption potential for fungal biomass used under batch conditions was investigated using kinetics and isotherm models. Fungal biomass of Rhizopus arrhizus TISTR 3610 exhibited preferential uptake of NP, an endocrine disrupting chemicals. Sporangiospores, asexual spores, were immobilised in chitosan beads. The biosorption data of NP on the moist heat inactivated R. arrhizus–chitosan beads were analyzed using four popular adsorption isotherms and, by using non-linear least-regression with the solver add-in in Microsoft Excel, correlated in order with the Fritz–Schluender > Redlich–Peterson > Freundlich > Langmuir isotherms. The pseudo first-order kinetics was found to have the best fit with the experimental data. The diffusivity of NP in the R. arrhizus–chitosan beads was calculated using the shrinking core model, and the diffusivity values were in the ranges of 2.3736 × 10⁻⁴–1.8950 × 10⁻⁴ cm² s⁻¹. Desorption to recover the adsorbed NP from the beads was performed in methanol and was best described using a pseudo second-order kinetic model.     

Continuous acetonitrile degradation in a packed-bed bioreactor

A 20-l packed-bed reactor filled with foamed glass beads was tested for the treatment of acetonitrile HPLC wastes. Aeration was provided by recirculating a portion of the reactor liquid phase through an aeration tank, where the dissolved oxygen concentration was kept at 6 mg/l. At a feeding rate of 0.77 g acetonitrile l^–1 reactor day^–1, 99% of the acetonitrile was removed; and 86% of the nitrogen present in acetonitrile was released as NH₃, confirming that acetonitrile volatilization was not significant. Increasing the acetonitrile loading resulted in lower removal efficiencies, but a maximum removal capacity of 1.0 g acetonitrile l^–1 reactor day^–1 was achieved at a feeding rate of 1.6 g acetonitrile l^–1 reactor day^–1. The removal capacity of the system was well correlated with the oxygenation capacity, showing that acetonitrile removal was likely to be limited by oxygen supply. Microbial characterization of the biofilm resulted in the isolation of a Comamonas sp. able to mineralize acetonitrile as sole carbon, nitrogen and energy source. This organism was closely related to C. testosteroni (91.2%) and might represent a new species in the Comamonas genus. This study confirms the potential of packed-bed reactors for the treatment of a concentrated mixture of volatile pollutants.     

High-performance liquid chromatographic analysis of bisphenol A and 4-nonylphenol in serum, liver and testis tissues after oral administration to rats and its application to toxicokinetic study

A sensitive and simple method based on solid-phase extraction (SPE) and HPLC with fluorescence detection for the determination of bisphenol A (BPA) and 4-nonylphenol (4-NP) in rat serum, liver and testis tissues has been developed. The chromatographic conditions consisted of a C18 column and mobile phase composition of acetonitrile and water with flow rate of 1.0 ml/min. The fluorescence detection was performed at excitation and emission wavelengths of 227 nm and 313 nm, respectively. Under these conditions, BPA and 4-NP were well separated and showed good linearities in the ranges of 0.01-50.0 microg/ml for BPA and 0.15-150.0 microg/ml for 4-NP with correlation coefficients greater than 0.999. The detection limits of serum and tissue samples were 2.8 ng/ml and 1.4 ng/g for BPA and 5.6 ng/ml and 2.8 ng/g for 4-NP at a signal-to-noise ratio (S/N) of 3. The intra-assay and the inter-assay precisions were better than 11.4%. Recoveries of BPA and 4-NP were 78.6-95.0% and 80.2-93.4%, respectively. The proposed method was applied to a toxicokinetic study of BPA and 4-NP including individual and combined oral administration to rats. The results showed that 4-NP remarkably altered the toxicokinetic parameters of BPA in testis, while parameters of BPA were not obviously altered in serum and liver under the experimental conditions investigated. On the other hand, there was no significant difference in the toxicokinetics of 4-NP when administered with BPA.     

Synthesis and antiperoxidant activity of new phenolic O-glycosides

We describe the synthesis of some 3-tert-butyl-4-hydroxyphenyl -glycopyranosides by reaction of tert-butylhydroquinone with β- -pentaacetyl-glucose, β- -pentaacetyl-galactose, 2-acetamido- and 3,4,6-tri-O-acetyl-2-butanamido-2-deoxy-β- -glucopyranosyl chlorides as well as the formation of anomeric 3-tert-butyl-4-hydroxyphenyl 4,6-di-O-acetyl-2,3-dideoxy- -erythro-hex-2-eno-pyranosides by reaction between tert-butylhydroquinone and 3,4,6-tri-O-acetyl- -glucal. All compounds, except 3-tert-butyl-4-hydroxyphenyl α- and β- -glucopyranosides, inhibited lipid peroxidation with a degree of potency comparable to that of tert-butyl hydroxyanisole.     

Degradation of bisphenol A and nonylphenol by nitrifying activated sludge

Nitrifier-enriched activated sludge was used in batch degradation of bisphenol A (BPA) and nonylphenol (NP) to verify if ammonium-oxidizing activity within nitrifiers is responsible for the biodegradation of those compounds. Decreases in both BPA and NP concentrations occurred simultaneously with ammonium (NH₄⁺) oxidation into nitrate (NO₃⁻) by nitrifying sludge. However, when ammonium was replaced by nitrite (NO₂⁻) in the medium, an acclimation period was required prior onset of significant degradation of BPA and NP. In the presence of inhibitors such as allylthiourea or Hg₂SO₄, BPA and/or NP reduction decreased significantly, implying that removal of BPA and NP was mostly mediated by biological activity rather than by physicochemical adsorption onto sludge flocs.     

Unique transglycosylation potential of extracellular α-d-galactosidase from Talaromyces flavus

The transglycosylation potential of the extracellular α-d-galactosidase from the filamentous fungus Talaromyces flavus CCF 2686, chosen as the best enzyme from the screening, was investigated using a series of sterically hindered alcohols (primary, secondary and tertiary) as galactosyl acceptors. Nine alkyl α-d-galactopyranosides derived from the following alcohols – tert-butyl alcohol, 2-methyl-2-butyl alcohol, 2-methyl-1-propyl alcohol, 2,2,2-trifluoroethyl alcohol, 2-propyn-1-ol, n-pentyl alcohol, 3,5-dihydroxybenzyl alcohol, 1-phenylethyl alcohol and 1,4-dithio-dl-threitol – were prepared on a semi-preparative scale. This demonstrates a broad synthetic potential of the T. flavus α-d-galactosidase that has not been observed with another enzyme tested. Moreover, this enzyme exhibits good transglycosylation yields (6–34%). The enzymatic synthesis of tert-butyl α-d-galactopyranoside by transglycosylation was studied in detail.     

Stir bar sorptive extraction and thermal desorption-gas chromatography-mass spectrometry for the measurement of 4-nonylphenol and 4-tert-octylphenol in human biological samples

Alkylphenols, 4-nonylphenol (NP) and 4-tert-octylphenol (OP), in human urine and plasma samples were analyzed using stir bar sorptive extraction (SBSE) in combination with thermal desorption-gas chromatography-mass spectrometry (TD-GC-MS). The method involved correction by stable isotopically labeled surrogate standards, 4-(1-methyl)octylphenol-d5 (m-OP-d5) and deuterium 4-tert-octylphenol (OP-d). A biological sample was extracted for 60 min at room temperature (25 degrees C) using a stir bar coated with a 500 microm thick polydimethylsiloxane (PDMS) layer. Then, the stir bar was analyzed by TD-GC-MS in the selected ion monitoring (SIM) mode without any derivatization step. The average recoveries in human urine and plasma samples spiked with NP and OP at levels of 0.5 and 10 ng ml-1 were between 95.8 and 99.8% with correction using the added surrogate standards. The limits of quantitation were 0.2 ng ml-1 for NP and 0.02 ng ml-1 for OP. We measured the background levels of NP and OP in five human urine and three human plasma samples from healthy volunteers. NP and OP were not detected in all human urine samples (N.D. < 0.2 ng ml-1 for NP, and N.D. < 0.02 ng ml-1 for OP). However, 0.2-0.3 ng ml-1 for NP and 0.1-0.2 ng ml-1 for OP in human plasma samples were observed by this method.     

Biotransformation of [ring-U-14C]4-n-nonylphenol by Agrostemma githago cell culture in a two-liquid-phase system

The biotransformation of [¹⁴C]4-n-nonylphenol (5 mg l^–1; 10 mg l^–1) by Agrostemma githago cell suspensions was studied using a batch two-liquid-phase system (medium/n-hexadecane 200:1, v/v). The highly lipophilic 4-n-nonylphenol was applied via n-hexadecane phase. After 7 d of incubation, more than 85% of applied 4-n-nonylphenol was absorbed by the cells, and 40% was transformed to 10 side-chain monohydroxylated metabolites (two with additional double bond at side-chain). The primary metabolites were analyzed by GC-EIMS. In the cells, the monohydroxylated products and residual 4-n-nonylphenol were present as glycosides. The method proved to be suitable for the production of primary metabolites of 4-n-nonylphenol on a larger scale for identification purposes and for metabolic profiling of the compound.     

Combined carbon and nitrogen removal from acetonitrile using algal–bacterial bioreactors

When compared with Chlorella vulgaris, Scenedesmus obliquus and Selenastrum capricornutum, C. sorokiniana presented the highest tolerance to acetonitrile and the highest O₂ production capacity. It also supported the fastest acetonitrile biodegradation when mixed with a suitable acetonitrile-degrading bacterial consortium. Consequently, this microalga was tested in symbiosis with the bacterial culture for the continuous biodegradation of acetonitrile at 2 g l^–1 in a stirred tank photobioreactor and in a column photobioreactor under continuous illumination (250 E m^–2 s^–1). Acetonitrile removal rates of up to 2.3 g l^–1 day^–1 and 1.9 g l^–1 day^–1 were achieved in the column photobioreactor and the stirred-tank photobioreactor, respectively, when operated at the shortest retention times tested (0.4 days, 0.6 days, respectively). In addition, when the stirred-tank photobioreactor was operated with a retention time of 3.5 days, the microbial culture was capable of assimilating up to 71% and nitrifying up to 12% of the NH₄⁺ theoretically released through the biodegradation of acetonitrile, thus reducing the need for subsequent nitrogen removal. This study suggests that complete removal of N-organics can be combined with a significant removal of nitrogen by using algal–bacterial systems and that further residual biomass digestion could pay-back part of the operation costs of the treatment plant.     

High-performance liquid chromatographic determination of trimebutine and its major metabolite, N-monodesmethyl trimebutine, in rat and human plasma

A rapid, selective and very sensitive ion-pairing reversed-phase HPLC method was developed for the simultaneous determination of trimebutine (TMB) and its major metabolite, N-monodesmethyltrimebutine (NDTMB), in rat and human plasma. Heptanesulfonate was employed as the ion-pairing agent and verapamil was used as the internal standard. The method involved the extraction with a n-hexane–isopropylalcohol (IPA) mixture (99:1, v/v) followed by back-extraction into 0.1 M hydrochloric acid and evaporation to dryness. HPLC analysis was carried out using a 4-μm particle size, C₁₈-bonded silica column and water–sodium acetate–heptanesulfonate–acetonitrile as the mobile phase and UV detection at 267 nm. The chromatograms showed good resolution and sensitivity and no interference of plasma. The mean recoveries for human plasma were 95.4±3.1% for TMB and 89.4±4.1% for NDTMB. The detection limits of TMB and its metabolite, NDTMB, in human plasma were 1 and 5 ng/ml, respectively. The calibration curves were linear over the concentration range 10–5000 ng/ml for TMB and 25–25000 ng/ml for NDTMB with correlation coefficients greater than 0.999 and with within-day or between-day coefficients of variation not exceeding 9.4%. This assay procedure was applied to the study of metabolite pharmacokinetics of TMB in rat and the human.     

Accumulation of ACE Inhibitory Tripeptides,Val-Pro-Pro and Ile-Pro-Pro,in Vascular Endothelial Cells

Topsoil samples were collected from 36 different paddy fields in West Japan. Each soil sample was incubated with a basal salt-medium containing 0.2% OPPEO. Twelve samples possessed OPPEO-degrading activity, from which twelve cultures of OPPEO-degrading bacteria were isolated. The isolated bacteria grew on a medium containing 0.2% OPPEO as the sole carbon source, and OP2EO and OP3EO were accumulated in the medium under aerobic conditions. OP1EO and octylphenol, which have often been identified in surface water together with OP2EO, were not observed in this experiment. The bacterial isolates were gram negative and tentatively identified as Pseudomonas putida (10 isolates) and Burkholderia cepacia (one isolate) by BIOLOG and 16S rDNA RFLP analyses.