scholarly journals Phytotoxicity, Bioaccumulation, and Degradation of Nonylphenol in Different Microalgal Species without Bacterial Influences

2020 ◽  
Vol 21 (4) ◽  
pp. 1338
Author(s):  
Ning He ◽  
Zhiwei Liu ◽  
Xian Sun ◽  
Shuangyao Wang ◽  
Weijie Liu ◽  
...  
Keyword(s):  
Scenedesmus Obliquus ◽  
Sewage Treatment ◽  
Aquatic Organisms ◽  
Freshwater Microalgae ◽  
Associated Bacteria ◽  
Antioxidant Responses ◽  
Negative Impacts ◽  
Species Specific ◽  
Suitable Scope ◽  
Antioxidant Reactions

Nonylphenol (NP) is a contaminant that has negative impacts on aquatic organisms. To investigate its phytotoxicity, bioaccumulation, and degradation in algae without associated bacteria, six freshwater microalgae—Ankistrodesmus acicularis, Chlorella vulgaris, Chroococcus minutus, Scenedesmus obliquus, Scenedesmus quadricauda, and Selenastrum bibraianum—in bacteria-free cultures were studied. When exposed to 0.5–3.0 mg L−1 NP for 4 days, cell growth and photosynthesis, including maximal photochemistry (Fv/Fm), were suppressed progressively. The antioxidant responses of superoxide dismutase (SOD), catalase (CAT), and peroxidase (POD) showed species differences. While the antioxidant enzymes in C. vulgaris and S. obliquus were more active with the increase of NP (0–3 mg L−1), they dropped in the other four algae at concentrations of 1 and 1.5 mg L−1. Therefore, C. vulgaris and S. obliquus were designated as NP-tolerant species and showed more conspicuous and faster changes of antioxidant reactions compared with the four NP-sensitive species. All six species degraded NP, but A. acicularis was more reactive at low NP concentrations (<1 mg L−1), suggesting its possible application in sewage treatment for its potential for effective NP removal from water bodies in a suitable scope. Therefore, the conclusion is that biodegradation of NP by algae is species specific.

Acute and chronic effect of cyaniade on survival rate, behavior, and reproduction of Daphnia sp.

2013 ◽  
Vol 1 (1) ◽  
pp. 52 ◽  
Author(s):  
Melky R Pattiwael ◽  
Remy E. P Mangindaan ◽  
Rudi Prabowo ◽  
Inneke F. M Rumengan
Keyword(s):  
Government Regulation ◽  
Aquatic Organisms ◽  
Standard Test ◽  
Toxicity Tests ◽  
Zooplankton Organism ◽  
Rate Behavior ◽  
Negative Impacts ◽  
Reproduction Pattern ◽  
Acute And Chronic Effects ◽  
Ministerial Decree

Cyanide (CN) through leaching process in the gold processing could produce tailings that have negative impacts on the aquatic environment. To determine the acute and chronic effects of cyanide on aquatic organisms, toxicity tests have been conducted in the laboratory using Daphnia sp.This zooplankton organism is recommended by APHA as standard test animals. In this study the test concentrations refer to the Ministerial Decree No. 202 of 2004 and Government Regulation No. 82 of 2001. Cyanide was analyzed as free CN and WADS CN. The result of acute toxicity test using cyanide solution showed that Daphnia could survive a maximum concentration of 0.2 ppm. LC50 values for 24 and 72 hours were 0,59 mg/L and 0,10 mg/l, respectively. The LT50 was found at 42 hours. Daphnia sp. produced different numbers of offspring at different CN concentrations, and changed their reproduction pattern from parthenogenesis to sexual reproduction after exposure to a cyanide concentration of 0.1 ppm for 24 hours©  Sianida (CN) melalui proses leaching dalam proses pengolahan emas menghasilkan limbah yang dapat memberi dampak negatif bagi lingkungan perairan. Untuk mengetahui sampai seberapa jauh CN dapat memberi efek akut dan kronis terhadap biota air, telah dilakukan uji toksisitas di laboratorium dengan menggunakan Daphnia sp. Zooplankton ini direkomendasikan oleh APHA sebagai salah satu hewan uji standar. Dalam penelitian ini konsentrasi uji yang dipakai mengacu pada peraturan yang berlaku, yaitu Keputusan Menteri No. 202, Tahun 2004, dan Peraturan Pemerintah No. 82, Tahun 2001. Analisis sianida yang dihitung adalah nilai free CN dan WADS CN. Hasil penelitian uji toksisitas akut dengan menggunakan larutan sianida didapati Daphnia mampu bertahan hidup sampai pada konsentrasi 0,2 ppm dan nilai LC50 berada pada konsentarsi 0,1 ppm serta LT50 pada jam ke 42. Hasil uji efek kronis, Daphnia sp. menghasilkan jumlah anakan yang berbeda pada konsentrasi CN yang berlainan, dan mengalami perubahan pola reproduksi dari partenogenesis menjadi seksual setelah dipaparkan pada kosentrasi sianida 0,1 ppm selama 24 jam©

scholarly journals Heavy Metals in Wastewater and Sewage Sludge from Selected Municipal Treatment Plants in Eastern Cape Province, South Africa

Water ◽  
2020 ◽  
Vol 12 (10) ◽  
pp. 2746 ◽  
Author(s):  
Mojeed A. Agoro ◽  
Abiodun O. Adeniji ◽  
Martins A. Adefisoye ◽  
Omobola O. Okoh
Keyword(s):  
Heavy Metals ◽  
South Africa ◽  
Sewage Treatment ◽  
Treatment Plant ◽  
Aquatic Organisms ◽  
Absorption Spectrometry ◽  
Eastern Cape Province ◽  
Eastern Cape ◽  
Removal Capacity ◽  
Treatment Facilities

This study assessed the distribution of five heavy metals (Cd, Pb, Cu, Zn, and Fe) across the various stages of treatment in three selected sewage treatment facilities and their receiving waterbodies in the Eastern Cape Province, South Africa. Aqueous and solid (sludge) samples were collected monthly from September 2015 to February 2016. Quantitation was achieved by atomic absorption spectrometry after necessary sample preparations. Concentrations of heavy metal cations in the sludge generally varied from <DL (below detection limit) to 1.17 mg kg−1, <DL to 0.14 mg kg−1, 27.588 to 69.789 mg kg−1, and <DL to 0.099 mg kg−1 for Cu, Cd, Fe and Pb; while Zn was below detection all through. Similarly, the levels of Cu, Cd, and Fe in the influents, effluents, upstream and downstream across the three plants ranged from <DL–6.588 mg L−1, <DL–0.636 mg L−1, <DL–0.878 mg L−1 and <DL–0.711 mg L−1, respectively; Zn and Pb were less than DL in all the matrices and study locations. All the contaminants were below hazardous levels in all the sludge and aqueous samples except Cd which was higher in effluents and surface waters across the board. Wastewater Treatment Plant (WWTP)-A exhibited better removal capacity for Fe (86.6%), compared to WWTP-B (34.7%) and WWTP-C (56.9%). However, the removal of Cu and Zn was very poor in all the treatment facilities studied. Carcinogenic and non-carcinogenic risks evaluated were sufficiently low. This suggests that the levels of contamination, even with respect to Cd, was minimal. Nevertheless, efforts should be made to keep the concentrations of these contaminants at levels safe for humans and aquatic organisms. Furthermore, the use of the effluents from these facilities for irrigation should be discouraged to prevent unnecessary build-up of metals in the soil and plants grown with such, as well as subsequent bioaccumulation and biomagnification in the food chain.

scholarly journals Fluorides in Wastewater Discharges: Toxic Challenges to the St. Lawrence River Biological Community

1996 ◽  
Vol 31 (4) ◽  
pp. 809-838 ◽  
Author(s):  
Peggy Wallis ◽  
Ronald Gehr ◽  
Perry Anderson
Keyword(s):  
Waste Water Treatment ◽  
Sewage Treatment ◽  
Treatment Plant ◽  
Aquatic Organisms ◽  
Water Treatment Plant ◽  
Aquatic Systems ◽  
Waste Water Treatment Plant ◽  
Biological Community ◽  
Fingernail Clams ◽  
St Lawrence River

Abstract This literature review examines the risk to fluvial organisms of fluoride released to the St. Lawrence River by the Montréal Urban Community waste-water treatment plant. The following key points are presented regarding the behaviour of fluoride in aquatic systems: fluoride is not removed by primary sewage treatment methods; fluoride from the treatment plant is rapidly diluted to background levels; aquatic plants do not accumulate significant levels of fluoride; fluoride is generally sequestered in the shell/exoskeleton/skeleton and skin of animals and released via the urinary system; fluoride ion is not very toxic in aquatic systems; there is rarely a large difference between acute and chronic (or lethal and sublethal) threshold levels of fluoride in aquatic systems; the most sensitive aquatic organisms are trout and fingernail clams; finally, the only significant evidence of synergistic action is with aluminium. It is concluded that fluoridation of the city of Montréal’s drinking water would not pose any significant additional risk to the biological community in the receiving waters of the St. Lawrence River.

scholarly journals Fundamental Research on Effect of Sewage Treatment Process on Biological Impacts against Aquatic Organisms by Sewage Water

2015 ◽  
Vol 51 (4) ◽  
pp. 95-103 ◽  
Author(s):  
FUMIHIKO TAKEDA ◽  
HIROYUKI MANO ◽  
TOMOKAZU KITAMURA ◽  
KOYA KOMORI ◽  
SEIICHIRO OKAMOTO
Keyword(s):  
Treatment Process ◽  
Sewage Treatment ◽  
Aquatic Organisms ◽  
Sewage Water ◽  
Biological Impacts ◽  
Fundamental Research

Humic acid alleviates the ecotoxicity of graphene-family materials on the freshwater microalgae Scenedesmus obliquus

Chemosphere ◽  
2018 ◽  
Vol 197 ◽  
pp. 749-758 ◽  
Author(s):  
Ying Zhang ◽  
Tiantian Meng ◽  
Xi Guo ◽  
Ruixin Yang ◽  
Xiaohui Si ◽  
...  
Keyword(s):  
Humic Acid ◽  
Scenedesmus Obliquus ◽  
Freshwater Microalgae ◽  
Graphene Family Materials

scholarly journals Occurrence and risks of antibiotics in an urban river in northeastern Tibetan Plateau

2020 ◽  
Vol 10 (1) ◽  
Author(s):  
Yuzhu Kuang ◽  
Xiaoyu Guo ◽  
Jingrun Hu ◽  
Si Li ◽  
Ruijie Zhang ◽  
...  
Keyword(s):  
Antibiotic Resistance ◽  
Tibetan Plateau ◽  
River Water ◽  
Sewage Treatment ◽  
Antibiotic Resistance Genes ◽  
Aquatic Organisms ◽  
Urban River ◽  
Resistance Evolution ◽  
Northeastern Tibetan Plateau ◽  
Plateau Area

AbstractThere is a dearth of information on the occurrence and risks of antibiotics in the urban rivers from plateau areas. This study investigated 83 antibiotics in water and sediments of an urban river and effluents of sewage treatment plants (E-STPs) in Xining, Qinghai (northeastern Tibetan Plateau). Fifty-three antibiotics were detected, and the concentrations of individual antibiotics varied in the range of undetected (ND)-552 ng/L in water, ND-164 ng/g in sediments, and ND-3821 ng/L in E-STPs. Seasonal differences of antibiotic concentrations were significant for water samples (p < 0.05) but insignificant for sediments (p > 0.05). In urban area, E-STP is the main source of antibiotics in the river, while runoff from manured cropland contributes partially to antibiotics in the river in the suburban area. The antibiotic compositions in water were different from those in sediments, but were similar to those in E-STPs. Notably, because of strong solar radiation and long sunshine hours in the plateau area, low levels of quinolones, which are sensitive to photolysis, were observed in river water. Moreover, norfloxacin and enrofloxacin, observed in urban river from other regions of China, were not detected in the Huangshui River water. The occurrence of ofloxacin, erythromycin, roxithromycin, clarithromycin, and trimethoprim in E-STPs may induce a possible risk to antibiotic resistance evolution. Trimethoprim, anhydroerythromycin, sulfamethoxazole, sulfapyridine, and clindamycin in river water could pose low to medium risks to aquatic organisms. Further investigation on the occurrence and distribution of antibiotic resistance genes in the Huangshui River is urgently needed.

Protecting aquatic organisms from chemicals: the harsh realities

2009 ◽  
Vol 367 (1904) ◽  
pp. 3877-3894 ◽  
Author(s):  
John P. Sumpter
Keyword(s):  
Sewage Treatment ◽  
Sewage Treatment Plant ◽  
Treatment Plant ◽  
Regulatory System ◽  
Aquatic Organisms ◽  
Transformation Products ◽  
Developed Countries ◽  
Agricultural Runoff ◽  
Freshwater Environment ◽  
Freshwater Organisms

Tens of thousands of man-made chemicals are in everyday use in developed countries. A high proportion of these, or their transformation products, probably reach the aquatic environment. A considerable amount is known about the environmental concentrations of some of these chemicals (such as metals), especially the regulated ones, but little or nothing is known about the majority. In densely populated countries, most or all rivers will receive both diffuse (e.g. agricultural runoff) and point source (e.g. sewage treatment plant effluent) inputs, and hence be contaminated with complex, ill-defined mixtures of chemicals. Most freshwater organisms will be exposed, to varying degrees, to this contamination. The number of species exposed is in the thousands, and quite possibly tens of thousands. Little is known about whether or not these species are adversely affected by the chemicals present in their environment. Often it is not even known what species are present, let alone whether they are affected by the chemicals present. In a few high-profile cases (e.g. tributyl tin causing imposex in molluscs and oestrogens ‘feminizing’ male fish), chemicals have undoubtedly adversely affected aquatic species, occasionally leading to population crashes. Whether or not other chemicals are affecting less visible species (such as most invertebrates) is largely unknown. It is possible that only very few chemicals in the freshwater environment are adversely affecting wildlife, but it is equally possible that some effects of chemicals are, as yet, undiscovered (and may remain so). Nor it is clear which chemicals may pose the greatest risk to aquatic organisms. All these uncertainties leave much to chance, yet designing a regulatory system that would better protect aquatic organisms from chemicals is difficult. A more flexible and intelligent strategy may improve the current situation. Finally, the risk due to chemicals is put into context with the many other threats, such as alien species and new diseases that undoubtedly can pose significant risks to aquatic ecosystems.

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