The aim of the study was to investigate the effects of subchronic exposure of zebrafish (Danio rerio) to a fluoroquinolone norfloxacin, using selected oxidative stress parameters as a target. Toxicity tests were performed on zebrafish according to the OECD Guidelines number 203 and number 215. In the Subchronic Toxicity Test, a significant (P < 0.01) increase in the activity of glutathione peroxidase, glutathione S-transferase, and catalase was found. In the test, norfloxacin did not affect lipid peroxidation and catalytic activity of glutathione reductase. From the results, we can conclude that norfloxacin has a negative impact on specific biochemical processes connected with the production of reactive oxygen species in fish tested.
ABSTRACT:In the present study, the effects of sub-lethal sub-chronic doses of ibuprofen, diclofenac, and carbamazepine alone, and in combination (concentration range 0.02-60 µg/l), on the early life stages of tench (Tinca tinca) were investigated. The lower concentrations of pharmaceuticals tested (0.02, 0.2, 2 µg/l) represent the concentration values of these substances commonly present in surface waters or effluents from wastewater treatment plants. Multiple biomarkers of biotransformation, antioxidant defence systems, and lipid peroxidation were determined in fish after 35 days of exposure. The evaluated pharmaceuticals induced oxidative stress in fish both alone and in combination with each other. Generally, 60 µg/l of each single pharmaceutical influenced the activity of antioxidant enzymes significantly (P < 0.05), whereas the same concentration of these pharmaceuticals in combination (1 : 1 : 1) did not have any impact on the activity of these enzymes. However, changes in biotransformation and antioxidant enzymes were apparent if lower concentrations of these pharmaceuticals were administered in the mixture. Significant changes (P < 0.05) in the activities of glutathione reductase, glutathione peroxidase, and glutathione-S-transferase were observed even at environmental concentration ranges. A significant effect (P < 0.05) on lipid peroxidation levels was found only in the experimental group exposed to carbamazepine. Keywords: antioxidant defence system; lipid peroxidationList of abbreviations ANC = acid-neutralising capacity, CAT = catalase, CBZ = carbamazepine, COD Mn = chemical oxygen demand, COX = cyclooxygenase, DCF = diclofenac, DMSO = dimethylsulfoxide, GPx = glutathione peroxidase, GR = glutathione reductase, GSH = reduced active form of glutathione, GSSG = oxidised inactive form of glutathione, GST = glutathione-S-transferase, IBU = ibuprofen, LC = liquid chromatography, LC-MS/MS = liquid chromatography with tandem mass spectrometry, LPO = lipid peroxidation level, NSAIDs = non-steroidal anti-inflammatory drugs, ROS = reactive oxygen species Pharmaceutical mixtures that contaminate water sources are currently a problem worldwide. Ibuprofen (IBU), diclofenac (DCF), and carbamazepine (CBZ) are among the most frequently detected drugs in aquatic ecosystems. Their concentrations in surface water range from ng/l to tens of µg/l. Higher concentrations have been detected in developing countries due to the direct discharge of untreated wastewater from residences and hospitals into surface waters (Tran et al. 2014).
Ubiquitous occurrence of pharmaceuticals in aquatic environment results in concern about potential adverse the effects on nontarget organisms. In water, drugs are present in complex mixtures, in which complicated interactions affect toxicity of single components. The purpose of this study was to examine effect of 35-day-long exposure to mixture of ibuprofen, diclofenac, and carbamazepine on the mortality, growth, early ontogeny, and histopathological changes in tench (Tinca tinca). Early life stage toxicity test was carried out using a modified protocol according to OECD guideline 210. Exposure to mixture of pharmaceuticals at concentration of 60 μg·L−1 for each substance was associated with significant increase in mortality, as well as significant increase in growth and elevated incidence of malformations. Any of the tested concentrations resulted in histopathological changes of liver, kidney, skin, or gill. After fourteen days of exposure there was short-term delay of development related to increased concentrations of pharmaceuticals in the mixture (2, 20, and 60 μg·L−1). Environmentally relevant concentrations (0.02; and 0.2 μg·L−1) used in this experiment did not result in toxic impairment of tench.
ABSTRACT:For the monitoring of distribution and accumulation of phthalic acid esters (PAE) in animal tissues, samples of muscle, mesenteric fat (fat), skin and liver from broiler chicks ROSS 308 were used. The chicks were divided into four groups (50 chicks each). All the chicks were given commercial diets (complete feed, KKS) for broiler chicks (starter -BR1; grower -BR2 and finisher -BR3). The experimental diets were supplemented with vegetable oil (RV) with low (group N) or high (group V) phthalate contents, or animal fat with a high phthalate content (group Z). Neither the control diets (K), nor the grower (BR1) diets contained vegetable oils or animal fat. The N chicks were given the grower (BR2) and finisher (BR3) diets supplemented with 5% and 3% vegetable oil, respectively. The V chicks were given BR2 and BR3 diets with 5% and 3% vegetable oil, respectively. The Z chicks were given BR2 and BR3 diets with 5% and 3% animal fat, respectively. The chicks were fattened till 42 days of age. Dibutyl phthalate (DBP) and di-(2-ethylhexyl) phthalate (DEHP) were found in the tissues of chicks in all the experimental groups. The DBP content in the muscle ranged from 0.03 to 0.55 mg/kg, in the adipose tissue from < 0.20 to 2.56 mg/kg, in the skin from < 0.20 to 1.49 mg/kg , and in the liver from 0.03 to 0.13 mg/kg. The content of DEHP in the muscle ranged from 0.03 to 1.15 mg/kg, in the adipose tissue from 0.25 to 9.85 mg/kg, in the skin from < 0.20 to 4.68 mg/kg, and in the liver from 0.16 to 0.24 mg/kg. The highest concentrations of DBP of 1.28 ± 1.00 mg/kg of fresh sample (an average value from eight chicks) was determined in the adipose tissue of V chicks. The highest concentration of DEHP of 3.27 ± 2.87 mg/kg of fresh sample (mean of eight chicks) was also determined in the V group. The accumulation of DEHP was 3.2; 2.6 and 2.9 times higher than that of DBP in the muscle, adipose tissue and skin, respectively. The V and Z chicks showed higher phthalate contents (the sum of DBP and DEHP) in the adipose tissue, skin and liver than the K and N chicks.
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