estrone-sulfate and estradiol-3-sulfate

The occurrence of free and conjugated estrogens was examined in a survey of eleven sewage treatment plants (STPs) and their discharge water in the United Kingdom using grab sampling. The STPs included trickling filter with and without tertiary treatment, and activated sludge with tertiary treatment. For three activated sludge plants both influent and effluent samples were compared. For a further 8STPs only the effluent was examined. The estrone-3-sulphate, estradiol-3-sulphate and estriol-3-sulphate concentrations (up to 20 ng L(-1)) were typically 5-fold that of the respective free estrogen concentration in the effluents. This represents a substantial additional 'potential' estrogen load arriving in the receiving waters. Estrone-3-glucuronide was found at 9 ng L(-1), estradiol-3-glucuronide at 7 ng L(-1), and estriol-3-glucuronide at 32 ng L(-1) in sewage influent. Except on one occasion, no glucuronide conjugates could be found in the effluent. The results suggest in most cases glucuronide conjugates will be completely transformed in sewage treatment whilst sulphate conjugates will only be partially removed.

Topics: Environmental Monitoring; Estradiol; Estriol; Estrogens; Estrone; Rivers; Sewage; United Kingdom; Waste Disposal, Fluid; Water Pollutants, Chemical; Water Pollution, Chemical

Estrogens-sulphates such as 17beta-estradiol-3-sulphate and estrone-3-sulphate are excreted by livestock in the urine. These conjugates are precursors to the free counterparts 17beta-estradiol and estrone, which are endocrine disrupting chemicals. In this study microcosm laboratory experiments were conducted in three pasture soils from New Zealand to study the aerobic degradation and metabolite formation kinetics of 17beta-estradiol-3-sulphate at three different incubation temperatures. The degradation of 17beta-estradiol-3-sulphate followed a first-order kinetic and the temperature dependence of the rate constants was sufficiently described by the Arrhenius equation. Degradation was different between the three investigated soils and the rate constants across the soils were significantly correlated to the arylsulphatase activity at 7.5 and 15 degrees C. Estrone-3-sulphate and 17beta-estradiol were identified as primary metabolites and estrone as a secondary metabolite. Results suggest arylsulphatase activity originating from soil microbial biomass is the main driver for the degradation of 17beta-estradiol-3-sulphate.

Topics: Aerobiosis; Arylsulfatases; Estradiol; Estrone; Kinetics; New Zealand; Soil; Soil Microbiology; Soil Pollutants; Temperature

In this study we present a pressurized liquid extraction/liquid chromatography-tandem mass spectrometry (PLE/LC-MS-MS) method to determine a group of estrogens and conjugated estrogens in sewage sludge. Parameters that affect the extraction step such as extraction solvent, temperature, pressure, static extraction time, number of cycles, purge time and flush volume have been optimized. In the LC-MS-MS system, electrospray ionization and a triple quadrupole analyzer have been used, and the multiple reaction monitoring mode has enabled low levels of target analytes to be detected. All recoveries were higher than 81% except for estrone 3-glucoronide and estradiol 17-glucoronide which were not extracted and consequently, they were not considered in the present study. The repeatability and reproducibility between days expressed as %RSD (n=3), were lower than 6% and 9%, respectively. The method developed allowed the target analytes to be quantified at low levels of microg/kg. The limits of detection were lower than 26 microg/kg of dry weight (d.w.) of sewage sludge, except for 17 alpha-estradiol, 17beta-estradiol, 17 alpha-ethinylestradiol and estradiol 17-acetate whose values were between 150 and 175 microg/kg (d.w.). The method was applied to determine these compounds in sewage sludge from two domestic sewage treatment plants. Estrone 3-sulfate, estradiol 3-sulfate, diethylstilbestrol, estrone and estriol were determined in some samples and estriol showed the highest value (406 microg/kg d.w.).

Topics: Chemical Fractionation; Chromatography, High Pressure Liquid; Environmental Monitoring; Estradiol; Estradiol Congeners; Estriol; Estrogens; Estrogens, Conjugated (USP); Estrone; Sewage; Tandem Mass Spectrometry; Water Pollutants, Chemical

Multidrug resistance protein 1 (MRP1) is an ATP-binding cassette (ABC) transporter that transports a range of hydrophobic xenobiotics, as well as relatively hydrophilic organic anion conjugates. The protein is present at high levels in testicular Leydig and Sertoli cells. Studies with knockout mice suggest that MRP1 may protect germ cells from exposure to some cytotoxic xenobiotics, but potential endobiotic substrates in this organ have not been identified. Previously, we have shown certain D-ring, but not A-ring, estrogen glucuronides can act as competitive inhibitors of MRP1 mediated transport, suggesting that they are potential substrates for the protein. In the case of 17 beta-estradiol-17 beta-d-glucuronide, this has been confirmed by direct transport studies. The Leydig cell is the major site of estrogen conjugation in the testis. However, the principal products of conjugation are A-ring estrogen sulfates, which are then effluxed from the cell by an unknown transporter. To determine whether MRP1/mrp1 could fulfill this function, we used membrane vesicles from MRP1-transfected HeLa cells to assess this possibility. We found that estradiol and estrone 3-sulfate alone were poor competitors of MRP1-mediated transport of the cysteinyl leukotriene, leukotriene C(4). However, in the presence of reduced glutathione (GSH), their inhibitory potency was markedly increased. Direct transport studies using [(3)H]estrone 3-sulfate confirmed that the conjugated estrogen could be efficiently transported (K(m) = 0.73 microm, V(max) = 440 pmol mg(-)1 protein min(-)1), but only in the presence of either GSH or the nonreducing alkyl derivative, S-methyl GSH. In contrast to previous studies using vincristine as a substrate, we detected no reciprocal increase in MRP1-mediated GSH transport. These results provide the first example of GSH-stimulated, MRP1-mediated transport of a potential endogenous substrate and expand the range of MRP1 substrates whose transport is stimulated by GSH to include certain hydrophilic conjugated endobiotics, in addition to previously identified hydrophobic xenobiotics.

Topics: ATP-Binding Cassette Transporters; Biological Transport; Estradiol; Estrone; Glutathione; HeLa Cells; Humans; Leukotriene C4; Multidrug Resistance-Associated Proteins

The binding of estrone-3-sulfate (E1-3-S) and estradiol-3-sulfate (E2-3-S) to adult stallion plasma was determined and compared with the binding to equine serum albumin (ESA). On the ESA molecule, two binding sites for E1-3-S with an association constant of 1.3 x 10(5) M-1 and several sites of weaker affinity were found; the data for E2-3-S showed the existence of four binding sites of moderate affinity (1 x 10(5) M-1) and several sites of weaker affinity. The removal of albumin from the stallion plasma resulted in the absence of binding of E1-3-S or E2-3-S, whereas the removal of glycoproteins resulted in binding parameters similar to those obtained with whole plasma. These results indicate that ESA is the only estrogen sulfate binder in horse plasma. Under physiological conditions, 95% of E1-3-S was bound to ESA.

Topics: Animals; Blood Proteins; Estradiol; Estrone; Glycoproteins; Horses; Male; Protein Binding; Serum Albumin

We isolated 12 strictly anaerobic steroid-3-sulfate-desulfating strains from the intestinal floras of rats and humans. Two strains (S1 and S2) of the same atypical Clostridium species and an atypical Lactobacillus strain (termed R9) were obtained from rats. The human isolates were identified as Eubacterium cylindroides (two strains, H1 and H2), Peptococcus niger (two strains, H4 and H89), and Clostridium clostridiiforme. We also isolated, from different human fecal samples, four strains of phenotypically similar asaccharolytic Bacteroides strains, H6.2a, H6.2b, H65, and H175. Aryl steroid sulfatase activity for estrogen sulfates was present in all isolates. Alkyl steroid sulfatase activity for both 3 alpha- and 3 beta-sulfates was found only in P. niger H4. The same P. niger strain and Clostridium strains S1 and S2 also possessed bile acid sulfatase activity.

Topics: Animals; Arylsulfatases; Bacteria, Anaerobic; Bacteroides; Clostridium; Estradiol; Estrone; Eubacterium; Feces; Humans; Intestines; Lactobacillus; Peptococcus; Rats; Steroids; Steryl-Sulfatase; Substrate Specificity; Sulfatases

The metabolism, in vitro, of [6,7-3H]-oestrone-3-sulfate and [6,7-3H]-oestradiol-17beta-3-sulfate by the uteri of pregnant female Guinea-Pigs has been studied using 900 g supernatants. A hydrolysis of the sulfate moiety was observed: 35% of the radioactivity was recovered in the unconjugated fractions after 1 hr. of incubation. Gluruconide oestrogens were also recovered but the rate of synthesis was very low (3.6% after 1 hr.). OEstrone and oestradiol-17beta have been identified in unconjugated, glucuro and sulfo-conjugated fractions after incubation with the tritiated oestrogen sulfates.

Topics: Animals; Estradiol; Estrogens, Conjugated (USP); Estrone; Female; Guinea Pigs; Hydrolysis; Kinetics; Pregnancy; Pregnancy, Animal; Tritium; Uterus

Topics: Animals; Estradiol; Estrogens, Conjugated (USP); Estrone; Female; Fetus; Guinea Pigs; In Vitro Techniques; Kidney; Pregnancy; Subcellular Fractions

Topics: Androstenedione; Chorionic Gonadotropin; Clomiphene; Cresols; Cyclofenil; Estradiol; Estrone; Female; Humans; In Vitro Techniques; Menotropins; Ovary; Perfusion; Steroids; Sulfuric Acid Esters; Sulfuric Acids; Testosterone