Radiolytic decomposition of pesticide carbendazim in waters and wastes for environmental protection.

The radiolytic degradation of widely used fungicide, carbendazim, in synthetic aqueous solutions and industrial wastewater was investigated employing γ-irradiation. The effect of the absorbed dose, initial concentration and pH of irradiated solution on the effectiveness of carbendazim decomposition were investigated. Decomposition of carbendazim in 100 µM concentration in synthetic aqueous solutions required irradiation with 600 Gy dose. The aqueous solutions of carbendazim have been irradiated in different conditions, where particular active radical species from water radiolysis predominate. The obtained data have been compared with the kinetic modeling. The reversed-phase high-performance liquid chromatography was used for the determination of carbendazim and its radiolytic decomposition products in irradiated solutions. The changes of toxicity of irradiated solutions were examined with different test organisms and human leukemia cells.

Investigating the biodegradability of perfluorooctanoic acid.

Perfluorooctanoic acid (PFOA) is an industrial chemical that has become disseminated globally in aquatic and terrestrial habitats, humans, and wildlife. Understanding PFOA's biodegradability (susceptibility to microbial metabolic attack) is a crucial element in developing an informed strategy for predicting and managing this compound's environmental fate. Reasoning that PFOA might be susceptible to reductive defluorination by anaerobic microbial communities, we embarked on a 2-phase experimental approach examining the potential of five different microbial communities (from a municipal waste-water treatment plant, industrial site sediment, an agricultural soil, and soils from two fire training areas) to alter PFOA's molecular structure. A series of primarily anaerobic incubations (up to 259d in duration) were established with acetate, lactate, ethanol, and/or hydrogen gas as electron donors and PFOA (at concentrations of 100 ppm and 100 ppb) as the electron acceptor. Cometabolism of PFOA during reductive dechlorination of trichloroethene (TCE) and during reduction of nitrate, iron, sulfate, and methanogenesis were also examined. Endpoints of potential PFOA transformation included release of fluoride and detection of potential transformation products by LC/Orbitrap MS and LC/accurate radioisotope counting in a (14)C radiotracer study. The strongest indication of PFOA transformation occurred during its potential cometabolism at the 100 ppb concentration during reductive dechlorination of TCE. Despite an extensive search for transformation products to corroborate potential cometabolism of PFOA, we were unable to document any alteration of PFOA's chemical structure. We conclude that, under conditions examined, PFOA is microbiologically inert, hence environmentally persistent.

Penetration of ammonium perfluorooctanoate through rat and human skin in vitro.

Rat and human epidermal membranes were mounted onto in vitro diffusion cells with an exposure area of 0.64 cm2, and skin integrity was confirmed using electrical impedance. Following membrane selection, Fluorad FC-118, a 20% aqueous solution of ammonium perfluorooctanoate (AFPO), was applied to the epidermal surface of each skin replicate at approximately 150 microL/cm2 and the donor chamber opening occluded with Parafilm. Serial receptor fluid samples were collected hourly from 1 to 6 h and at 12, 24, 30, and 48 h and analyzed by liquid chromatography-mass spectrometry (LC-MS) for APFO anion (PFO-). For rat skin, the time to steady-state penetration (6500+/-3000 ng APFO x cm(-2) x h(-1)) occurred in less than 12 h, which was sustained until termination (48 h). Based on the concentration of the applied test material, the permeability coefficient (Kp) for APFO in rat skin was calculated to be 3.25+/-1.51 x 10(-5) cm/h. By end of the 48-h exposure period, only a small portion of the total APFO applied (1.44+/-1.13%) had penetrated through rat skin. For human skin, steady-state penetration of APFO (190+/-57 ng APFO x cm(-2) x h(-1)) was reached by 12 h. Based on the concentration of the applied test material, the permeability coefficient for APFO in human skin was calculated to be 9.49+/-2.86 x 10(-7) cm/h. By the end of the 48-h exposure period, only a negligible amount of the total APFO applied (0.048+/-0.01%) had penetrated through human skin. Thus, under infinite dose and occlusive conditions, the steady-state penetration of APFO from a 20% solution was approximately 34-fold faster through rat skin than human skin.

Time- and concentration-dependent increases in cell proliferation in rats and mice administered vinyl acetate in drinking water.

Chronic administration of vinyl acetate (VA) in drinking water to rats and mice has produced upper digestive tract neoplasms. These tumors were believed to arise from the intracellular metabolism of VA by carboxylesterases to cytotoxic and genotoxic compounds. We hypothesized that prolonged VA exposure at high concentrations would induce cytotoxicity and a restorative cell proliferation (CP). These endpoints were measured in F-344 rats and BDF1 mice administered drinking water containing 0, 1000, 5000, 10,000, or 24,000 ppm VA for 92 days. On test days, Days 1, 8, 29, and 92, upper digestive tract histopathology and oral cavity CP (pulsed 5-bromodeoxyuridine [BrdU] to measure S-phase DNA synthesis) were evaluated. Analysis of test solutions showed that VA spontaneously hydrolyzed, slowly releasing acetic acid and thereby lowering pH. Statistically significant, concentration-related increases in CP occurred in basal cells of the mandibular oral cavity mucosa of mice at 10,000 and 24,000 ppm but only after 92 days. CP increases were approximately 2.4- and 3.4-fold above controls and were considered to be toxicologically significant. Some statistically significant increases in CP were also measured in the oral cavity mucosa of rats; however, these changes were considered to be of equivocal biological relevance. No histopathological evidence of mucosal injury was seen in either species. The absence of cytotoxicity in the upper digestive tract mucosa suggests that the increased CP at high administered VA concentrations may be due to a mitogenic response, ostensibly from the loss of cell growth controls in oral cavity mucosa.

Determination of organoarsenicals in the environment by solid-phase microextraction-gas chromatography-mass spectrometry.

The development of a method for the analysis of organoarsenic compounds that combines dithiol derivatization with solid-phase microextraction (SPME) sample preparation and gas chromatography-mass spectrometry (GC-MS) is described. Optimization focused on a SPME-GC-MS procedure for determination of 2-chlorovinylarsonous acid (CVAA), the primary decomposition product of the chemical warfare agent known as Lewisite. Two other organoarsenic compounds of environmental interest, dimethylarsinic acid and phenylarsonic acid, were also studied. A series of dithiol compounds was examined for derivatization of the arsenicals, and the best results were obtained either with 1,3-propanedithiol or 1,2-ethanedithiol. The derivatization procedure, fiber type, and extraction time were optimized. For CVAA, calibration curves were linear over three orders of magnitude and limits-of-detection were < 6.10(-9) M in solution, the latter a more than 400 x improvement compared to conventional solvent extraction GC-MS methods. A precision of < 10% R.S.D. was typical for the SPME-GC-MS procedure. The method was applied to a series of water samples and soil/sediment extracts, as well as to aged soil samples that had been contaminated with Lewisite.

Coupling condensation nucleation light scattering detection with capillary electrophoresis using electrospray.

An improved method for coupling capillary electrophoresis (CE) with condensation nucleation light scattering detection (CNLSD) is described. The method employs an electrospray aerosol source followed by aerosol particle neutralization within a weak plasma established by a polonium-210 alpha emitter. Sensitive, universal detection of underivatized proteins, peptides, and amino acids is demonstrated. The system performance was significantly affected by the operational mode of the electrospray source, characterized by the physical appearance of the droplet at the end of the electrospray capillary. With a so-called pulsating mode, relatively low backgrounds were obtained with 10 mM ammonium acetate or 10 mM ammonium acetate/10 mM ammonia CE buffers using one diffusion screen, allowing detection of proteins at single microgram per milliliter levels and amino acids and peptides at submicrogram per milliliter levels. Linearity of response, expressed as peak height or peak area; mass limits of detection (LODs) for proteins, peptides, and amino acids at the picogram level, corresponding to femtomole levels of peptides and amino acids or subfemtomole levels of proteins; and better detectability compared to UV absorbance at 214 and 200 nm were demonstrated. The separation efficiencies obtained with the CE-electrospray-CNLSD system are much higher than those obtained for a previously reported pneumatic nebulizer-based system and in the range of approximately 20,000-160,000 plates/m using the pulsating electrospray mode. With careful adjustment of the electrospray voltage, a different operating mode, called the silver bullet mode, could be established for which higher signals, lower background and background noise, and higher separation efficiencies were observed compared to the pulsating mode. The lower background levels observed with the silver bullet mode eliminated the need for the use of a diffusion screen for background control with the buffer employed. With the silver bullet mode without a diffusion screen, linear response and LODs at the 15 ng/mL level, corresponding to subpicogram or 1-2 fmol levels of underivatized peptides and amino acids, and plate numbers in the range of 65,000-220,000 plates/m were estimated.

Condensation nucleation light scattering detection for capillary electrophoresis.

We describe two means for interfacing condensation nucleation light scattering detection to capillary electrophoresis (CE). With the first method, a fused-silica capillary was used for the separation and the CE was grounded through a Nafion membrane that also connected the system to a microconcentric pneumatic nebulizer. Limits of detection (LODs) for underivatized amino acids were at the low microgram per milliliter level, and separation efficiencies were ∼9 times lower than the optimum predicted for these species based on the injection plug width and axial dispersion by diffusion. LODs were limited by background nonvolatiles resulting from dissolution of fused silica at the high pHs used for the separations. An alternate system employed PEEK capillaries which acted as the separation capillary and also as the inner nebulizer capillary. In this case, the exit end of the capillary was coated with conductive paint which extended to the tip of the nebulizer, was in contact with the CE buffer, and was grounded to complete the CE circuit. Response was nonlinear and the separation efficiency of this system was somewhat lower than that for the Nafion membrane system. Response as peak heights for all of the amino acids and peptides studied was nearly identical on a mass basis. With this system, much lower background signals were obtained, and as a result, LODs for underivatized amino acids and peptides were below the 1 µg/mL level, corresponding to less than 10 pg or less than 100 fmol injected. Both systems were fairly simple, effective means to generate aerosols with the low flows of CE and should be applicable to interfacing of other aerosol-based detectors with CE.

Oxidative removal of interferences in flow-injection potentiometric determination of chloride.

Direct potentiometric determination of chloride in a flow-injection system can be performed in the presence of excess bromide, iodide, sulphide and cyanide, when potassium bromate in nitric acid is used as the carrier solution. The hydrodynamics and temperature of such a system have been examined and various oxidants and indicating electrodes investigated. The analysis can be performed at a maximum rate of 120 samples per hour.