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      Fate and Uptake of Pharmaceuticals in Soil–Earthworm Systems

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          Abstract

          Pharmaceuticals present a potential threat to soil organisms, yet our understanding of their fate and uptake in soil systems is limited. This study therefore investigated the fate and uptake of 14C-labeled carbamazepine, diclofenac, fluoxetine, and orlistat in soil–earthworm systems. Sorption coefficients increased in the order of carbamazepine < diclofenac < fluoxetine < orlistat. Dissipation of 14C varied by compound, and for orlistat, there was evidence of formation of nonextractable residues. Uptake of 14C was seen for all compounds. Depuration studies showed complete elimination of 14C for carbamazepine and fluoxetine treatments and partial elimination for orlistat and diclofenac, with greater than 30% of the 14C remaining in the tissue at the end of the experiment. Pore-water-based bioconcentration factors (BCFs), based on uptake and elimination of 14C, increased in the order carbamazepine < diclofenac < fluoxetine and orlistat. Liquid chromatography–tandem mass spectrometry and liquid chromatography–Fourier transform mass spectrometry indicated that the observed uptake in the fluoxetine and carbamazepine treatments was due to the parent compounds but that diclofenac was degraded in the test system so uptake was due to unidentifiable transformation products. Comparison of our data with outputs of quantitative structure−activity relationships for estimating BCFs in worms showed that these models tend to overestimate pharmaceutical BCFs so new models are needed.

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          Sorption of veterinary pharmaceuticals in soils: a review.

          Veterinary pharmaceuticals (VPs) are used in large amounts in modern husbandry. Due to their use pattern, they possess a potential for reaching the soil environment. To assess their mobility in soil, the literature on sorption of chemicals used as VPs is reviewed and put into perspective of their physicochemical properties. The compilation of sorption coefficients to soil solids (Kd,solid) demonstrates that these chemicals display a wide range of mobility (0.2 < Kd,solid < 6,000 L/kg). Partition coefficients for association of tetracycline and quinolone carboxylic acid VPs to dissolved organic matter (Kd,DOM) vary between 100 and 50,000 L/kg. The variation in Kd,solid for a given compound in different soils can be significant. For most of the compounds, the variation is not considerably lower for the organic carbon-normalized sorption coefficient Koc. In addition, prediction of log Koc by log Kow leads to significant underestimation of log Koc and log Kd,DOM values. This suggests that mechanisms other than hydrophobic partitioning play a significant role in sorption of VPs. A number of hydrophobicity-independent mechanisms such as cation exchange, cation bridging at clay surfaces, surface complexation, and hydrogen bonding appear to be involved. These processes are not accounted for by organic carbon normalization, suggesting that this data treatment is conceptually inappropriate and fails to describe the sorption behavior. Moreover, prediction of log Koc based on the hydrophobicity parameter log Kow is not successful.
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            Toxic effects of the non-steroidal anti-inflammatory drug diclofenac. Part I: histopathological alterations and bioaccumulation in rainbow trout.

            Human and veterinary pharmaceuticals have been shown to occur in considerably high amounts in sewage treatment plant (STP) effluents and surface waters. The non-steroidal inflammatory drug diclofenac represents one of the most commonly detected compounds. Information concerning possible ecotoxicological risks of the substance are rather scarce. So far there are no data available on its possible effects in fish after prolonged exposure. In order to evaluate sublethal toxic effects of diclofenac in fish, rainbow trout (Oncorhynchus mykiss) exposed to diclofenac concentrations ranging from 1 microg/L to 500 microg/L over a 28 day period were investigated by histopathological methods. In addition, diclofenac residues in various organs were analyzed by means of gas chromatography/mass spectrometry (GC/MS). The histopathological examinations of diclofenac-exposed fish revealed alterations of the kidney such as an hyaline droplet degeneration of the tubular epithelial cells and the occurrence of an interstitial nephritis. In the gills, the predominant finding consisted in a necrosis of pillar cells leading to damage of the capillary wall within the secondary lamellae. The lowest observed effect concentration (LOEC) at which both renal lesions and alterations of the gills occurred was 5 microg/L. In contrast, the light microscopical examination of the liver, the gastro-intestinal tract, and the spleen did not reveal any histopathological alterations neither in diclofenac-exposed fish nor in solvent controls or control individuals. Chemical analysis showed a concentration-related accumulation of diclofenac in all organs examined. The highest amounts could be detected in the liver, followed by the kidney, the gills and the muscle tissue. Dependent on the diclofenac concentration used, the bioconcentration factors (BCF) were 12-2732 in the liver, 5-971 in the kidney, 3-763 in the gills, and 0.3-69 in the muscle respectively. From the present findings it can be assumed, that prolonged exposure in environmentally relevant concentrations of diclofenac leads to an impairment of the general health condition of fish.
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              The environmental side effects of medication.

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                Author and article information

                Journal
                Environ Sci Technol
                Environ. Sci. Technol
                es
                esthag
                Environmental Science & Technology
                American Chemical Society
                0013-936X
                1520-5851
                24 April 2014
                20 May 2014
                : 48
                : 10
                : 5955-5963
                Affiliations
                [1] Environment Department, §Department of Biology, Bioscience Technology Facility and Centre of Excellence in Mass Spectrometry, and Department of Chemistry and Centre of Excellence in Mass Spectrometry, University of York , Heslington, York YO10 5DD, United Kingdom
                []EHS Technical CoE, GlaxoSmithKline, Ware SG12 0DP, United Kingdom
                Author notes
                [* ]Phone: +44 (0)1904 434791; fax: +44 (0)1904 432998; e-mail: alistair.boxall@ 123456york.ac.uk .
                Article
                10.1021/es500567w
                4041664
                24762061
                ab1dd3bf-ea4a-485e-b37d-40d396cece9b
                Copyright © 2014 American Chemical Society

                Terms of Use CC-BY

                History
                : 01 February 2014
                : 24 April 2014
                : 23 April 2014
                Categories
                Article
                Custom metadata
                es500567w
                es-2014-00567w

                General environmental science
                General environmental science

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