Effect of petroleum wastewater treated with gravity separation and magnetite nanoparticles adsorption methods on the blood biochemical response of mrigal fish (Cirrhinus cirrhosus)

Hamidi, Sakineh; Banaee, Mahdi; Pourkhabbaz, Hamid Reza; Sureda, Antoni; Khodadoust, Saeid; Pourkhabbaz, Alireza

doi:10.1007/s11356-021-15106-8

Cited by 18 publications

(7 citation statements)

References 89 publications

Supporting

Mentioning

Contrasting

Order By: Relevance

“…Along with this liver’s activity, the increase in adrenocorticotrophic and glucagon hormones, coupled with decreased insulin levels, may also contribute to liver glycogen’s enhanced breakdown (Alkaladi et al 2020 ). Chronic exposure to distillery effluent was found to result in increased blood sugar levels in C. carpio (Ramakritinan et al 2005 ) and petroleum effluent in Cirrhinus cirhossus (Hamidi et al 2021 ).…”

Section: Discussionmentioning

confidence: 99%

Effects of 2,4,6-Trichlorophenol on Clarias batrachus: a biomarkers approach

Mukherjee¹,

Ferreira

Saha

2022

Environ Sci Pollut Res

View full text Add to dashboard Cite

Abstract2,4,6-Trichlorophenol (2,4,6-TCP) is a common waste among the resulting chlorophenols generated in the production of common products classified as an extremely toxic, mutagenic, carcinogenic and highly persistent xenobiotic in the environment. To evaluate the impact of 2,4,6-TCP in aquatic systems, the catfish species Clarias batrachus has been selected to test its toxicity due to its high market value and consumption in India. Here is presented the impact of this compound on different physiological parameters of fish: haematological parameters (haemoglobin, total erythrocyte count, total leucocyte count and mean corpuscular haemoglobin), biochemical parameters (total serum protein and total serum glucose), growth and reproductive parameters (condition factor, hepatosomatic index, maturity index, specific growth rate, growth hormone, 17β-estradiol and testosterone), exposed to two concentrations of 2,4,6-TCP (0.5 mg/L and 1 mg/L — 1/10th and 1/20th of the LC50) for a period of 15, 30 and 45 days. The results showed that C. batrachus even when exposed to the lower concentration (0.5 mg/L) for the shortest time (15 days) negatively impacted the organism in all the assessed parameters. This was highlighted by the Integrated Biomarker Response index (IBR), showing worse scores for the treatments (up to 20 × worse than the control). This work highlights the importance of continued research on the impact of 2,4,6-TCP, on an important commercial, supported by the high environmental persistence of this compound that can reach the same range of tested concentrations.

show abstract

Section: Discussionmentioning

confidence: 99%

Effects of 2,4,6-Trichlorophenol on Clarias batrachus: a biomarkers approach

Mukherjee¹,

Ferreira

Saha

2022

Environ Sci Pollut Res

View full text Add to dashboard Cite

show abstract

“…In S. schlegeli, total protein and albumin concentrations were reduced after exposure to dimethylbenz (a) anthracene at 2.4 and 4.8 mg/kg for 8 weeks [106]. In a similar manner, the total protein and albumin levels of the mrigal carp (Cirrhinus cirrhosis) fish were dramatically reduced after being exposed to 1% water-soluble fractions of crude oil [107]. On the contrary, the total protein and albumin indices were significantly increased in African catfish (Clarias gariepinus) exposed to 10% aqueous extract of Nigerian crude oil for 30 days [108].…”

Section: Blood Biochemistry Test Indicates Whatmentioning

confidence: 77%

Polycyclic Aromatic Aydrocarbons (PAHs) Pollution Approaches in Aquatic Ecosystems: Perils and Remedies Using Green Technologies

El-Bouhy,

Reda,

Mohamed

et al. 2024

Zagazig Veterinary Journal

View full text Add to dashboard Cite

One of the most persistent environmental pollutants known as polycyclic aromatic hydrocarbons (PAHs), are pervasive throughout the world. Polycyclic aromatic hydrocarbons pose a serious health threat to a variety of life forms because of their mutagenic, teratogenic, immunotoxicogenic, and/or carcinogenic properties. The majority of PAHs production comes from both natural and human sources, such as forest fires, volcanic emissions, coal, oil, and petroleumbased goods like gasoline. Because PAHs show very high persistence, aquatic and non-aquatic animal species can easily acquire their residues in the environment, either directly from the water or indirectly through their food. Because of this, the current review focuses on the main PAHs emission sources, transformations, occurrences in ecosystems, and harmful effects on aquatic animals, with an emphasis on fish. Also, eco-friendly biological treatment methods for PAHs remediation are thoroughly discussed. These methods include microbial remediation (bacterialremediation, myco-remediation, and vermi-remediation) and Phyto-remediation techniques (active carbons, rhizo-remediation, and medicinal plants).

show abstract

“…[11][12][13] For oil spills in aqueous environments, the most commonly used oil-water separation methods can be divided into three major classes: biological treatment, chemical treatment and physical/mechanical treatment. 14,15 Specifically, examples include bio-oxidation separation, enzyme treatment; [16][17][18][19][20] coagulant treatment, 21,22 electrical separation, 23 in situ combustion; 24,25 gravity separation, [26][27][28] skimmers, 29,30 filtration separation, 31 centrifugal separation, 32 adsorption separation and so on. However, chemical methods and biological methods can also cause secondary pollution and have high requirements for water intake, professional maintenance, and high infrastructure costs.…”

Section: Introductionmentioning

confidence: 99%