The concentration of polycyclic aromatic hydrocarbons (PAHs) in Fish (Mullet fish-Mugil cephalus) and Shellfish (Tiger prawn-Penaeus Monodon and crab-Uca tangeri) samples from fishing areas in Amariaria Community, downstream of Bonny River, Southern Nigeria, were assessed to determine possible human health risk associated with consumption. Mean levels (mg/kg) of total PAHs ranged from 0.059 to 0.126 in fish, 0.015 to 0.106 in prawn and 0.057 to 0.063 in crab. A considerable predominance of the 3 and 4-rings PAHs in all the matrices was observed with benzo (a) anthracene dominating in all three species. Estimated daily intake (EDI) of PAHs through consumption of fish ranged from 0 to 0.0005 mg/kg/day, for prawn, 0 to 0.0002 mg/kg/day and for crab, 0 to 0.0002 mg/kg/day. EDI values were, however, lower than the reference dose (RfD) indicating low risk from consumption. Results of the estimated excess cancer risk (ECR) for Benzo (a) anthracene in fish, however, suggests that lifetime exposure to Benzo (a) anthracene through fish consumption would result in cancer risk.
Ecotoxicological effects of industrial chemicals (Rig wash, Oil eater, Nalco, Glycol™) and pesticides (Propoxur, Deltamethrin, Atrazine, Furadan) on Tilapia guineensis (fish) and Aporrectodea longa (earthworms) were tested using the Organisation for Economic Cooperation and Development (OECD) # 203 and 207 protocols. The water and soil ratings indicate that the test chemicals were toxic to the organisms. The estimated 96 hour lethal concentration LC 50 values for Rig wash, Oil eater, Nalco EC1304A/COT 505, Glycol, Propoxur, and Deltamethrin were 26.34±0.46, 6.02±0.30, 3.07±0.14, 1.31±0.01, 20.91±0 and 0.01±0 mg/l respectively. In the earthworm bioassay, the estimated 14-day LC 50 values for Rigwash, Oil eater, Nalco EC1304A/COT 505, Glycol, Atrazine and Furadan were 80.05±3.5, 151.55±10.7, 172.63±14.2, 63.72±2.43, 4.97±0 and 0.29±0 mg/kg respectively. Safety factors are arbitrarily built in around the LC 50 values in order to arrive at environmentally tolerable concentrations. The concentration of a chemical in the receiving environment should not exceed 10% of the LC 50 . The organisms exposed to the test chemicals showed significant difference when compared with the levels measured in the control group. The observed sensitivity of the test organisms to the chemicals indicates that adherence to standard safety limits/measures should be maintained during use and disposal of hazardous chemicals. This would ensure that the biotic components of the Nigerian Niger Delta ecosystem are prudently protected.
Concentrations of Persistent organics (Polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), metalloid (As) and heavy metals (Fe, Zn, Mn, Cu, Ni, Cd. V, Cr, Pb, Hg) were measured in fish (Clarias gariepinus) samples collected from selected stations (S1, S2 and S3) along the stretch of Ovia River, Southern Nigeria, to assess the potential risks to humans consuming fish from the river. Acenaphthylene (AcPY), PCB 18 and iron (Fe) were the most dominant residues with mean concentrations ranging from 0.002 to 0.128, 0.001 to 0.003 and 175.97 to 255.52 mg/kg respectively. The most carcinogenic PAH, Benzo(a)pyrene (BaP) in S3, all the PCB congeners, cadmium (Cd), and lead (Pb) concentrations in the three stations were observed to be above EU recommended guideline values for food safety. Concentrations of dioxin-like PCB congeners, 77, 105, 114 and the sum of carcinogenic PAHs also contributed to the toxic burden of these contaminants in fish. The estimated cumulative THQ for the assessed metalloid and heavy metals indicates health risks from exposure to metalloid and Heavy metals through fish consumption.
The formulation of glyphosate composed of Isopropylamine salt (41 % wt) is widely used as herbicide both in the terrestrial and aquatic environment. This study examined the toxicity of the surfactant Isopropylamine salt of glyphosate herbicide to post juvenile African catfish (Clarias gariepinus).. This experimental design was based on the standard Total Residual Chlorine (TRC) method with interval time of 24, 48, 72 and 96 hrs. Gulping of air, restlessness, surface to bottom movement, sudden quick movement and excessive resting at the bottom were abnormal behaviour observed in the exposed fish. Mortality of C. gariepinus increased (p<0.05) with an increase in glyphosate concentration. The results showed that the 96h LC50 value of glyphosate was 300 mg/L while the maximum allowable concentration (MAC) of this toxicant is 30.0 mg/L. The effect of the toxicant on C. gariepinus was both time and concentration-dependent.
Acetaminophen is one of the most commonly detected Analgesics and pain killer drug in freshwater environments. This study evaluated the possible multi-toxic effects of environmentally relevant concentrations (15.5, 25.5, 35.5 and 45.5µg/L) of acetaminophen in Clarias gariepinus fish exposed for 28 days using multiple biomarkers. Hepatosomatic index (HIS) and condition factor (K) of acetaminophen–exposed group were not different from the control. The superoxide dismutase (SOD) activity increased significantly at 15.5 and 35.5µg/L and Catalase (CAT) activity in all acetaminophen-exposed groups barely showed an upward trend. The concentration of glutathione S-transferase (GST) activities was not different from the control. Glutathione peroxidase (GPx) activities increased at all concentrations when compared to the control group. There were general inhibitions of Acetylcholinesterase (AChE) activities in all exposed groups including the control. Total antioxidant capacity (TAC) increased significantly at 25.5 and 45.5µg/L and Interluekin-6 (IL-6) showed non-significant increases in all exposed concentrations. Acetaminophen exposure caused non-significant increases in the activities of C reactive protein (CRP). White blood cells (WBC) and lymphocytes (LYM counts) were significant reduced. Acetaminophen induced significant changes in hormones of the hypothalamic-pituitary-gonad (HPG) axis (17β-Estradiol and Testosterone) and vitellogenin (Vtg) synthesis at 45.5µg/L. Histopathological alterations in the liver was evident of apoptotic hyperplasia, sinusoidal congestion and necrosis of the hepatocytes and was concentration dependent. Acetaminophen exposure to the fish gills enhanced the fusion and shortening of some filaments, hyperplasia of the epithelia gills cells, aneurism, congestion and epithelia rupture of the gills. Gonad examination showed acetaminophen exposure triggered the occurrence of intersex in 25.5, 35.5 and 45.5µg/L. The collaborative biomarkers used in this study showed the multiple impacts of acetaminophen on the physiology of C. gariepinus. Multivariate statistical analysis indicated that fish in the control groups exhibited a distinctly response from the acetaminophen-exposed fish and that over 95% of the biomarkers significantly contribute to discriminate between the acetaminophen-exposed fish and the control group. Our research provides evidence supporting the use of multiple-biomarker approach to evaluate the health status of C. gariepinus in future studies.
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