Dean E. Hammermeister

Characterization of dansylated glutathione, glutathione disulfide, cysteine and cystine by narrow bore liquid chromatography/electrospray ionization mass spectrometry

A method using reversed phase high performance liquid chromatography/electrospray ionization-mass spectrometry (RP-LC/ESI-MS) has been developed to confirm the identity of dansylated derivatives of cysteine (C) and glutathione (GSH), and their respective dimers, cystine (CSSC) and glutathione disulfide (GSSG). Cysteine, GSH, CSSC and GSSG are present at low concentrations in rainbow trout (Oncorhynchus mykiss) liver cells. Initially, hepatic cells were sampled from a suspension culture and disrupted upon addition of 10% perchloric acid. The reduced thiols present in the cell extracts were acetylated to prevent dimerization and then the C and GSH species were derivatized with dansyl chloride for fluorescence detection. An LC system using a weak anion exchange column (AE) with fluorescence detection (FLD) was used for sensitive routine analysis; however, it produced peaks of unknown origin in addition to the expected analytes. Analytes were then separated on a C18 RP-LC system using a water/acetonitrile gradient with 0.2% formic acid, and detected using LC/ESI-MS at 3.5 KV which produced an intense ion with a minimum limit of detection of less than 0.5 pmole injected (>10:1 signal-to-noise (S/N). Subsequently, fractions of effluent from the AE-LC/FLD system were analyzed by LC/ESI-MS to confirm the presence of the target analytes in routine cell extracts. Monodansylated GSSG was identified as a product that could possibly affect the quantification of GSH and GSSG.

A comparison of the lethal and sublethal toxicity of organic chemical mixtures to the fathead minnow (Pimephales promelas)

The joint toxic effects of known binary and multiple organic chemical mixtures to the fathead minnow (Pimephales promelas) were defined at both the 96-h 50% lethal effect concentration (LC50) and sublethal (32-d growth) response levels for toxicants with a narcosis I, narcosis II, or uncoupler of oxidative phosphoralation mode of toxic action. Experiments were designed to define the degree of additive joint toxicity for mixtures of specific xenobiotics that are believed to act through a similar or different primary mode of toxic action. Our results support the general conclusion that concentration addition is expected for the joint toxicity of similarly acting toxicants. When chemicals were thought to act by a dissimilar mechanism, the combined effects we observed at both of the response levels tested were less than predicted by concentration addition, but usually more toxic than that predicted by the independent action/response addition model. It was demonstrated in multichemical mixtures that several toxicants can act together in a nearly additive fashion to produce effects even when they are present at concentrations below their individual no-observed-effect concentration. Concentration-response relationships for test chemicals at both the lethal and sublethal responses were defined for each of the three modes of toxic action studied. When normalized for potency, it was observed that one relationship could be defined to predict lethality to juvenile fathead minnows when exposed to individual chemicals with either a narcosis I, narcosis II, or uncoupler mode of toxic action. These sublethal relationships were similar for the narcosis I and narcosis II test chemicals, but a steeper response was observed for tests conducted with uncouplers.

Saturation units for use in aquatic bioassays.

Methods were developed for preparing liquid/liquid and glass wool column saturators for generating chemical stock solutions for conducting aquatic bioassays. Exposures have been conducted using several species of fish, invertebrate, and mollusks in static and flow-through conditions using these methods. Stock solutions for 82 organic chemicals were prepared using these saturation units. The primary purpose of stock generation was to provide a continuous and consistent amount of toxicant laden solution at a measured analytical level which would be available to test organisms for the test duration. In the present study, the glass wool column and liquid/liquid saturators were used to provide consistent stock concentrations, at times approaching saturation, for fathead minnow (Pimephales promelas) acute exposures. Attempts were made to achieve the maximum solubility of these compounds for comparison purposes to water solubility values available in the literature. Literature solubility values from a database by Yalkowsky et al. [1] provided information on temperatures and data quality which allowed comparison to values obtained from the present study. Twenty four compounds were identified and analyzed for the comparison of maximum obtainable solubility levels. Maximum saturator stock water concentrations were generally lower (R = 0.98) but were in close agreement with published water solubility values.

In Vivo Microdialysis Sampling of Phenol and Phenyl Glucuronide in the Blood of Unanesthetized Rainbow Trout: Implications for Toxicokinetic Studies

Microdialysis (MD) is a sampling method that allows continuous in vivo collection of free, unbound chemicals in blood and interstitial fluids. In the present study we describe a surgical method for placement of a MD probe in the dorsal aorta of 600- to 900-g rainbow trout (Onchorhynchus mykiss). A specially designed probe guide was inserted into the dorsal aorta via the mouth. A PE-50 polyethylene cannula was then inserted into the probe guide and used to further position and maintain the probe guide in the dorsal aorta. Once proper placement of the probe guide was ascertained, the cannula was removed and a CMA-10 MD probe (4-mm tip) was inserted. The animal was then placed into a respirometer-metabolism chamber and allowed to recover from anesthesia. The placement and functionality of the probe were evaluated by examining the in vivo toxicokinetics of phenol (PH) and phenyl glucuronide (PG) in the blood of an unanesthetized rainbow trout exposed to water-borne PH (7.0 mg/liter). Prior to and following the introduction of PH into the metabolism chamber, MD samples (150 microliters) were collected at 30-min intervals and analyzed for free plasma PH and PG by HPLC. Total PH in exposure water and blood was also monitored every 30 min. Free PH and total PH in plasma accumulated rapidly and reached apparent steady-state levels of 54 and 142 pmol/microliters, respectively, in about 60 min. A blood:water partition coefficient of 2.0-2.6 was determined from these data, while bound and free plasma PH were 60 and 40%, respectively. PG was not detected until approximately 90 min of PH exposure.(ABSTRACT TRUNCATED AT 250 WORDS)

Kinetics and effects of dichloroacetic acid in rainbow trout.

Halogenated acetic acids (HAAs) produced by chlorine disinfection of municipal drinking water represent a potentially important class of environmental contaminants. Little is known, however, about their potential to adversely impact fish and other aquatic life. In this study we examined the kinetics and effects of dichloroacetic acid (DCA) in rainbow trout. Branchial uptake was measured in fish confined to respirometer-metabolism chambers. Branchial uptake efficiency was <5%, suggesting passive diffusion through aqueous channels in the gill epithelium. DCA concentrations in tissues following prolonged (72, 168, or 336 h) waterborne exposures were expressed as tissue:plasma concentration ratios. Concentration ratios for the kidney and muscle at 168 and 336 h were consistent with the suggestion that DCA distributes primarily to tissue water. Reduced concentration ratios for the liver, particularly at 72 h, indicated that DCA was highly metabolized by this tissue. Routes and rates of elimination were characterized by injecting chambered animals with a high (5.0mg/kg) or low (50 microg/kg) bolus dose. DCA was rapidly cleared by naïve animals resulting in elimination half-lives (t(1/2)) of less than 4h. Waterborne pre-treatment of fish with DCA increased the persistence of a subsequently injected dose. In high dose animals, pre-treatment caused a 4-fold decrease in whole-body clearance (CL(B)) and corresponding increases in the area under the plasma concentration-time curve (extrapolated to infinity; AUC(0-->infinity)) and t(1/2). Qualitatively similar results were obtained in low dose fish, although the magnitude of the pre-treatment effect ( approximately 2.5-fold) was reduced. Renal and branchial clearance contributed little (combined, <3% of CL(B)) to the elimination of DCA. Biliary elimination of DCA was also negligible. The steady-state volume of distribution (V(SS)) did not vary among treatment groups and was consistent with results of the tissue distribution study. DCA had no apparent effects on respiratory physiology or acid-base balance; however, the concentration of blood lactate declined progressively during continuous waterborne exposures. A transient effect on blood lactate was also observed in bolus injection experiments. The results of this study suggest that clearance of DCA is due almost entirely to metabolism. The pathway responsible for this activity exhibits characteristics in common with those of mammalian glutathione S-transferase zeta (GSTzeta), including non-linear kinetics and apparent suicide inactivation by DCA. Observed effects on blood lactate are probably due to the inhibition of pyruvate dehydrogenase kinase in aerobic tissues and may require the participation of a monocarboxylase transport protein to move DCA across cell membranes.