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Dasmahapatra AK, Williams CB, Myla A, Tiwary SK, Tchounwou PB. A systematic review of the evaluation of endocrine-disrupting chemicals in the Japanese medaka ( Oryzias latipes) fish. FRONTIERS IN TOXICOLOGY 2023; 5:1272368. [PMID: 38090358 PMCID: PMC10711633 DOI: 10.3389/ftox.2023.1272368] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Grants] [Track Full Text] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 08/04/2023] [Accepted: 10/10/2023] [Indexed: 02/01/2024] Open
Abstract
Japanese medaka (Oryzias latipes) is an acceptable small laboratory fish model for the evaluation and assessment of endocrine-disrupting chemicals (EDCs) found in the environment. In this research, we used this fish as a potential tool for the identification of EDCs that have a significant impact on human health. We conducted an electronic search in PubMed (http://www.ncbi.nlm.nih.gov/pubmed) and Google Scholar (https://scholar.google.com/) using the search terms, Japanese medaka, Oryzias latipes, and endocrine disruptions, and sorted 205 articles consisting of 128 chemicals that showed potential effects on estrogen-androgen-thyroid-steroidogenesis (EATS) pathways of Japanese medaka. From these chemicals, 14 compounds, namely, 17β-estradiol (E2), ethinylestradiol (EE2), tamoxifen (TAM), 11-ketotestosterone (11-KT), 17β-trenbolone (TRB), flutamide (FLU), vinclozolin (VIN), triiodothyronine (T3), perfluorooctanoic acid (PFOA), tetrabromobisphenol A (TBBPA), terephthalic acid (TPA), trifloxystrobin (TRF), ketoconazole (KTC), and prochloraz (PCZ), were selected as references and used for the identification of apical endpoints within the EATS modalities. Among these endpoints, during classification, priorities are given to sex reversal (masculinization of females and feminization of males), gonad histology (testis-ova or ovotestis), secondary sex characteristics (anal fin papillae of males), plasma and liver vitellogenin (VTG) contents in males, swim bladder inflation during larval development, hepatic vitellogenin (vtg) and choriogenin (chg) genes in the liver of males, and several genes, including estrogen-androgen-thyroid receptors in the hypothalamus-pituitary-gonad/thyroid axis (HPG/T). After reviewing 205 articles, we identified 108 (52.68%), 46 (22.43%), 19 (9.26%), 22 (17.18%), and 26 (12.68%) papers that represented studies on estrogen endocrine disruptors (EEDs), androgen endocrine disruptors (AEDs), thyroid endocrine disruptors (TEDs), and/or steroidogenesis modulators (MOS), respectively. Most importantly, among 128 EDCs, 32 (25%), 22 (17.18%), 15 (11.8%), and 14 (10.93%) chemicals were classified as EEDs, AEDs, TEDs, and MOS, respectively. We also identified 43 (33.59%) chemicals as high-priority candidates for tier 2 tests, and 13 chemicals (10.15%) show enough potential to be considered EDCs without any further tier-based studies. Although our literature search was unable to identify the EATS targets of 45 chemicals (35%) studied in 60 (29.26%) of the 205 articles, our approach has sufficient potential to further move the laboratory-based research data on Japanese medaka for applications in regulatory risk assessments in humans.
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Affiliation(s)
- Asok K. Dasmahapatra
- RCMI Center for Environmental Health, Jackson State University, Jackson, MS, United States
- Department of BioMolecular Sciences, School of Pharmacy, University of Mississippi, University, MS, United States
| | - Charmonix B. Williams
- RCMI Center for Environmental Health, Jackson State University, Jackson, MS, United States
| | - Anitha Myla
- RCMI Center for Environmental Health, Jackson State University, Jackson, MS, United States
| | - Sanjay K. Tiwary
- RCMI Center for Environmental Health, Jackson State University, Jackson, MS, United States
| | - Paul. B. Tchounwou
- RCMI Center for Environmental Health, Jackson State University, Jackson, MS, United States
- RCMI Center for Urban Health Disparities Research and Innovation, Morgan State University, Baltimore, MD, United States
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Américo-Pinheiro JHP, Salomão GR, Moreno Paschoa CV, Cruz IA, Isique WD, Romanholo Ferreira LF, Torres NH, Bilal M, Iqbal HMN, Sillanpää M, Nadda AK. Effective adsorption of diclofenac and naproxen from water using fixed-bed column loaded with composite of heavy sugarcane ash and polyethylene terephthalate. ENVIRONMENTAL RESEARCH 2022; 211:112971. [PMID: 35276188 DOI: 10.1016/j.envres.2022.112971] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/11/2021] [Revised: 02/08/2022] [Accepted: 02/15/2022] [Indexed: 02/05/2023]
Abstract
The contamination of water by pharmaceutical pollutants is a major issue these days due to excessive use of these ingredients in modern life. This study evaluated the adsorption and effectiveness of a low-cost composite prepared from heavy sugarcane ash (HSA) fused with polyethylene terephthalate (PET) and functionalized with iron (Fe3+) in a dynamic system through a fixed-bed column. The solution of synthetic drugs was prepared and placed in a reservoir, using a peristaltic pump the solution is run onto the fixed bed column at a flow rate of 2 mL min-1. Saturation time and adsorption capacity were evaluated by centrifugation and extraction after a regular interval of 2 h from the adsorption column. The samples were analyzed using high-performance liquid chromatography (HPLC) and the data was modeled for quantification. For DIC removal, an adsorption capacity of 324.34 μg. g-1 and a saturation time of 22 h were observed, while the adsorption capacity of NAP was 956.49 μg. g-1, with a saturation time of 8 h. Thus, the PETSCA/Fe3+ adsorbent proved to be quite efficient for removing the pharmaceutical pollutants, with a longer period of operation for DIC removal. These findings suggested that a highly efficient bed column made from a less expensive waste material and could be used to remove hazardous pharmaceutical contaminants.
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Affiliation(s)
- Juliana Heloisa Pinê Américo-Pinheiro
- Post-graduate Program in Environmental Sciences, Brazil University, Street Carolina Fonseca, 584, 08230-030, São Paulo, SP, Brazil; Post-graduate Program in Civil Engineering, School of Engineering, São Paulo State University (UNESP), Ave. Brasil Sul, 56, Centro, 15385-000, Ilha Solteira, SP, Brazil.
| | - Gledson Renan Salomão
- Post-graduate Program in Civil Engineering, School of Engineering, São Paulo State University (UNESP), Ave. Brasil Sul, 56, Centro, 15385-000, Ilha Solteira, SP, Brazil
| | - Claudomiro Vinicius Moreno Paschoa
- Post-graduate Program in Civil Engineering, School of Engineering, São Paulo State University (UNESP), Ave. Brasil Sul, 56, Centro, 15385-000, Ilha Solteira, SP, Brazil
| | - Ianny Andrade Cruz
- Graduate Program in Process Engineering, Tiradentes University, Ave. Murilo Dantas, 300, Farolândia, 49032-490, Aracaju, SE, Brazil
| | - William Deodato Isique
- Post-graduate Program in Civil Engineering, School of Engineering, São Paulo State University (UNESP), Ave. Brasil Sul, 56, Centro, 15385-000, Ilha Solteira, SP, Brazil
| | - Luiz Fernando Romanholo Ferreira
- Graduate Program in Process Engineering, Tiradentes University, Ave. Murilo Dantas, 300, Farolândia, 49032-490, Aracaju, SE, Brazil; Institute of Technology and Research, Ave. Murilo Dantas, 300, Farolândia, 49032-490, Aracaju, SE, Brazil
| | - Nádia Hortense Torres
- Graduate Program in Process Engineering, Tiradentes University, Ave. Murilo Dantas, 300, Farolândia, 49032-490, Aracaju, SE, Brazil
| | - Muhammad Bilal
- School of Life Science and Food Engineering, Huaiyin Institute of Technology, Huaian, 223003, China
| | - Hafiz M N Iqbal
- Tecnologico de Monterrey, School of Engineering and Sciences, Campus Monterrey, Ave. Eugenio Garza Sada 2501, Monterrey, N.L., CP 64849, Mexico
| | - Mika Sillanpää
- Department of Chemical Engineering, School of Mining, Metallurgy and Chemical Engineering, University of Johannesburg, P. O. Box 17011, Doornfontein, 2028, South Africa; Chemistry Department, College of Science, King Saud University, Riyadh, 11451, Saudi Arabia
| | - Ashok Kumar Nadda
- Department of Biotechnology and Bioinformatics, Jaypee University of Information Technology, Waknaghat, Solan, 173 234, India.
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González-González RB, Sharma P, Singh SP, Américo-Pinheiro JHP, Parra-Saldívar R, Bilal M, Iqbal HMN. Persistence, environmental hazards, and mitigation of pharmaceutically active residual contaminants from water matrices. THE SCIENCE OF THE TOTAL ENVIRONMENT 2022; 821:153329. [PMID: 35093347 DOI: 10.1016/j.scitotenv.2022.153329] [Citation(s) in RCA: 26] [Impact Index Per Article: 13.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 10/16/2021] [Revised: 12/30/2021] [Accepted: 01/18/2022] [Indexed: 02/07/2023]
Abstract
Pharmaceutical compounds are designed to elicit a biological reaction in specific organisms. However, they may also elicit a biological response in non-specific organisms when exposed to ambient quantities. Therefore, the potential human health hazards and environmental effects associated with pharmaceutically active compounds presented in aquatic environments are being studied by researchers all over the world. Owing to their broad-spectrum occurrence in various environmental matrices, direct or indirect environmental hazardous impacts, and human-health related consequences, several pharmaceutically active compounds have been categorized as emerging contaminants (ECs) of top concern. ECs are often recalcitrant and resistant to abate from water matrices. In this review, we have examined the classification, occurrence, and environmental hazards of pharmaceutically active compounds. Moreover, because of their toxicity and the inefficiency of wastewater treatment plants to remove pharmaceutical pollutants, novel wastewater remediation technologies are urgently required. Thus, we have also analyzed the recent advances in microbes-assisted bioremediation as a suitable, cost-effective, and eco-friendly alternative for the decontamination of pharmaceutical pollutants. Finally, the most important factors to reach optimal bioremediation are discussed.
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Affiliation(s)
| | - Pooja Sharma
- Department of Environmental Microbiology, School for Environmental Sciences, Babasaheb Bhimrao Ambedkar (A Central) University, Lucknow 226 025, Uttar Pradesh, India
| | - Surendra Pratap Singh
- Plant Molecular Biology Laboratory, Department of Botany, Dayanand Anglo-Vedic (PG) College, Chhatrapati Shahu Ji Maharaj University, Kanpur-208 001, India
| | | | | | - Muhammad Bilal
- School of Life Science and Food Engineering, Huaiyin Institute of Technology, Huaian 223003, China
| | - Hafiz M N Iqbal
- Tecnologico de Monterrey, School of Engineering and Sciences, Monterrey, 64849, Mexico.
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Shin YJ, Kim B, Kim H, Kim K, Park K, Kim J, Kim HJ, Kim P. 1,2,3-benzotriazole adversely affects early-life stage of Oryzias latipes. THE SCIENCE OF THE TOTAL ENVIRONMENT 2022; 815:152846. [PMID: 34995609 DOI: 10.1016/j.scitotenv.2021.152846] [Citation(s) in RCA: 4] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/28/2021] [Revised: 12/15/2021] [Accepted: 12/28/2021] [Indexed: 06/14/2023]
Abstract
1,2,3-benzotriazole (BT) is used in large amounts around the world and is one of the substances derived from household chemicals that are of concern for risk when discharged to aquatic environments. Therefore, several studies have been conducted on the aquatic toxicity effects of BT, but the chronic impact assessment studies to evaluate the developmental effects on the early-life stage of fish are insufficient. In this study, the acute toxicity test and subchronic toxicity test (fish, early-life stage toxicity test, ELS test) using embryos of Japanese medaka (Oryzias latipes) were performed to evaluate the acute toxicity, developmental toxicity, growth (indicated by total length and weight at the end of the test), and histopathological effect of BT. In the short-term toxicity test on embryo and sac-fry stage, toxicity value was calculated to be 41 mg/L (NOEC). Based on this value, the exposure concentration of the ELS test was determined as 0.04, 0.4, 4 and 40 mg/L, and total exposure duration was 42 days. At the highest concentration group (40 mg/L), failure of swim bladder inflation and decrease of survival and size (total length and weight) were observed. Moreover, in the histopathological analysis, abnormal findings were detected in swim bladders from the 40 mg/L group such as inflammation and tumor changes. On the other hands, condition index (weight-length relationships, CI) was statistically significantly lower in all exposed groups compared to the control group. NOEC for the survival of BT was calculated to be 4 mg/L. LOEC for CI was 0.04 mg/L, which means BT inhibited weight gain relative to its length on larvae of medaka.
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Affiliation(s)
- Yu-Jin Shin
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea; Department of Environmental Health Science, Konkuk University, Seoul 05029, Republic of Korea.
| | - Bokyung Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Hokyun Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Kyungtae Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Kyunghwa Park
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Jieun Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Hee-Jung Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
| | - Pilje Kim
- Risk Assessment Division, Environmental Health Research Department, National Institute of Environmental Research, Incheon 22689, Republic of Korea
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Synthetic Progestins in Waste and Surface Waters: Concentrations, Impacts and Ecological Risk. TOXICS 2022; 10:toxics10040163. [PMID: 35448424 PMCID: PMC9026682 DOI: 10.3390/toxics10040163] [Citation(s) in RCA: 5] [Impact Index Per Article: 2.5] [Reference Citation Analysis] [Abstract] [Track Full Text] [Download PDF] [Figures] [Subscribe] [Scholar Register] [Received: 12/28/2021] [Revised: 03/22/2022] [Accepted: 03/23/2022] [Indexed: 02/01/2023]
Abstract
Synthetic progestins (PGs) are a large family of hormones used in continuously growing amounts in human and animal contraception and medicinal therapies. Because wastewater treatment plants (WWTPs) are unable to eradicate PGs after excretion, they are discharged into aquatic systems, where they can also be regenerated from conjugated PG metabolites. This review summarises the concentrations of 12 PGs in waters from 2015 to 2021. The selected PGs were considered of particular interest due to their wide use, activity, and hormonal derivation (from testosterone, progesterone, and spirolactone). We concluded that PGs had been analysed in WWTPs influents and effluents and, to a lesser extent, in other matrices, including surface waters, where their concentrations range from ng/L to a few µg/L. Because of their high affinity for cell hormone receptors, PGs are endocrine disruptor compounds that may alter the reproductive fitness and development of biota. This review focused on their biological effects in fish, which are the most used aquatic model organisms to qualify the impacts of PGs, highlighting the risks that environmental concentrations pose to their health, fecundity, and fertility. It is concluded that PGs research should be expanded because of the still limited data on their environmental concentrations and effects.
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Asala TE, Dasmahapatra AK, Myla A, Tchounwou PB. Histological and Histochemical Evaluation of the Effects of Graphene Oxide on Thyroid Follicles and Gas Gland of Japanese Medaka (Oryzias latipes) Larvae. CHEMOSPHERE 2022; 286:131719. [PMID: 34426126 PMCID: PMC8595807 DOI: 10.1016/j.chemosphere.2021.131719] [Citation(s) in RCA: 7] [Impact Index Per Article: 3.5] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 06/20/2021] [Revised: 07/26/2021] [Accepted: 07/28/2021] [Indexed: 05/13/2023]
Abstract
Graphene oxide (GO) has become a topic of increasing concern for its environmental and health risks. However, studies on the potential toxic effects of GO, especially as an endocrine disrupting chemical (EDC), are very limited. In the present study we have used Japanese medaka fish as a model to assess the endocrine disruption potential of GO by evaluating its toxic and histopathologic effects on thyroid follicles and the gas gland (GG) of medaka larvae. One day post-hatch (dph) starved medaka fries were exposed to GO (2.5, 5.0, 10.0, and 20 mg/L) for 96 h, followed by 6 weeks depuration in a GO-free environment with feeding. Larvae were sacrificed and histopathological evaluation of thyroid follicles and the GG cells were done microscopically. Different sizes of spherical/oval shape thyroid follicles containing PAS positive colloids, surrounded by single-layered squamous/cuboidal epithelium, were found to be scattered predominantly throughout the pharyngeal region near the ventral aorta. We have apparently observed a sex-specific difference in the follicular size and thyrocytes height and a non-linear effect of GO exposure on the larvae on 47th day post hatch (dph). The GG is composed of large uniform epithelial cells with eosinophilic cytoplasm. Like thyroids, our studies on GG cells indicate a sex-specific difference and GO exposure non-linearly reduced the GG cell numbers in males and females as well as in XY and XX genotypes. Our data further confirm that sex effect should be carefully considered while assessing the toxicity of EDCs on the thyroid gland.
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Affiliation(s)
- Tolulope E Asala
- RCMI Center for Environmental Health, Jackson State University, 1400 JR Lynch Street, Jackson, MS, 39217, USA
| | - Asok K Dasmahapatra
- RCMI Center for Environmental Health, Jackson State University, 1400 JR Lynch Street, Jackson, MS, 39217, USA; Department of BioMolecular Sciences, Environmental Toxicology Division, University of Mississippi, University, MS, 38677, USA
| | - Anitha Myla
- RCMI Center for Environmental Health, Jackson State University, 1400 JR Lynch Street, Jackson, MS, 39217, USA
| | - Paul B Tchounwou
- RCMI Center for Environmental Health, Jackson State University, 1400 JR Lynch Street, Jackson, MS, 39217, USA.
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FURUKAWA S, MACHIDA Y, TAKEUCHI K, HOSHIKAWA Y, IRIE K. Failure to gulp surface air induces swim bladder adenomas in Japanese medaka (<i>Oryzias latipes</i>). J Toxicol Pathol 2022; 35:237-246. [PMID: 35832900 PMCID: PMC9255999 DOI: 10.1293/tox.2022-0030] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 02/28/2022] [Accepted: 03/29/2022] [Indexed: 11/19/2022] Open
Affiliation(s)
- Satoshi FURUKAWA
- Biological Research Laboratories, Nissan Chemical Corporation, 1470 Shiraoka, Shiraoka-shi, Saitama 349-0294, Japan
| | - Yuichiro MACHIDA
- Biological Research Laboratories, Nissan Chemical Corporation, 1470 Shiraoka, Shiraoka-shi, Saitama 349-0294, Japan
| | - Kazuya TAKEUCHI
- Biological Research Laboratories, Nissan Chemical Corporation, 1470 Shiraoka, Shiraoka-shi, Saitama 349-0294, Japan
| | - Yumiko HOSHIKAWA
- Biological Research Laboratories, Nissan Chemical Corporation, 1470 Shiraoka, Shiraoka-shi, Saitama 349-0294, Japan
| | - Kota IRIE
- Biological Research Laboratories, Nissan Chemical Corporation, 1470 Shiraoka, Shiraoka-shi, Saitama 349-0294, Japan
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