ORIGINAL_ARTICLE
Environmental Pollution and Disaggregated Economic Policy Uncertainty: Evidence from Japan
Though, the attention of researchers on exploring the impact of economic policy uncertainty on carbon emissions is on increase, however, the impact of different types of economic policy uncertainty remains unexplored. Thus, this study investigates the impact of different types of economic policy uncertainty on carbon emissions in Japan. A monthly data from 1987M1 to 2019M12 was used, while the FMOLS, DOLS, CCR and ARDL estimators were employed for examining the cointegration among the variables, as well as the long- and short-run relationship between types of economic policy uncertainty and carbon emissions. The study findings revealed a long-run cointegration among energy consumption, per capita income, fiscal, exchange rate, monetary, and trade policy uncertainties and carbon emissions. Moreover, this study found energy consumption, exchange rate, monetary, and trade policy uncertainties to contribute significantly to the increase of carbon emissions in Japan. Finally, this study suggests that environmental policy makers in Japan should take into account the economic policy uncertainty so as to promote robust information for climate policy that will be targeted at ameliorating the carbon emissions in Japan.
https://jpoll.ut.ac.ir/article_84041_1a71b1af44563e917f8784c727c2d6f6.pdf
2021-10-01
749
767
10.22059/poll.2021.321490.1057
Environmental Pollution
Economic policy uncertainty
climate change
Environmental quality
Japan
Jamiu Adetola
Odugbesan
odugbesanadetola@gmail.com
1
Faculty of Economics, Administrative and Social Sciences, Cyprus West University, North Cyprus, Mersin 10, Turkey Faculty of Political and Social Sciences, Onbes Kasim Kibris University, North Cyprus, Mersin 10, Turkey
LEAD_AUTHOR
Sarah
Aghazadeh
saharaghazadeh@gmail.com
2
Faculty of Economics and Administrative Sciences, Final International University, North Cyprus, Mersin 10, Turkey
AUTHOR
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ORIGINAL_ARTICLE
Particulate Matter and Adverse Respiratory Health Outcome: Exposure of Street Vendors in Kolkata city in India
Exposure to airborne particulates is a major occupational hazard especially for outdoor workers who spending time outdoors at ground level getting exposed to traffic fumes and roadside dust. Aim of this study was to assess respiratory health symptoms and determine the change of lung functions of the roadside vendors and its association with traffic-related exposures and their working experience. A cross-sectional study was conducted in key market places of Kolkata – Gariahat (GH), Esplanade-Park Street (EP), Shyambazar-Hatibagan (SH) and Behala (BE). Particulate (PM10 and PM2.5) levels and meteorological parameters (wind speed, temperature and relative humidity) were monitored in the morning, afternoon and night over the period of October 2019 to February 2020. Lung function status (FEV1, FVC, FEV1/FVC ratio and PEF) was measured for 111 purposively selected participants. PM concentration was observed higher in the morning and night peak hours for all sites. At SH area the average occupational exposure level for PM10 and PM2.5 were observed as 1502.22 μg/m3h and 684.01 μg/m3h. Percentage predicted FEV1 (%FEV1) of street vendors was found decreasing with their work experience and the worst-case scenario was observed in the EP area, with the corresponding value being 70.75%, 49.15% and 47.3% for less than 10 years, 10 to 20 years and more than 20 years participation respectively. The higher particulate burden was observed to have declining lung function status of the street vendors. A strong policy framework should be adopted to improve outdoor working environment for outdoor workers.
https://jpoll.ut.ac.ir/article_84064_8328aa8b7279fcb9084c65bc54b1c83c.pdf
2021-10-01
769
785
10.22059/poll.2021.321814.1059
urban environment
Air pollution
Occupational Exposure
Outdoor workers
respiratory symptoms
Nabanita
Ghosh
nabanita199517@gmail.com
1
Global Change Programme - Jadavpur University, Kolkata, India
LEAD_AUTHOR
Biplob
Das
jubiplob@gmail.com
2
Department of Civil Engineering, Jadavpur University, Kolkata, India
AUTHOR
Nandini
Das
nandiinii.das@gmail.com
3
Global Change Programme - Jadavpur University, Kolkata, India
AUTHOR
Souran
Chatterjee
souran.chatterjee@gmail.com
4
Global Change Programme - Jadavpur University, Kolkata, India Department of Environmental Sciences and Policy, Central European University, Nádor utca 9, 1051 Budapest, Hungary
AUTHOR
Anupam
Debsarkar
anupamju1972@gmail.com
5
Global Change Programme - Jadavpur University, Kolkata, India Department of Civil Engineering, Jadavpur University, Kolkata, India
AUTHOR
Amit
Dutta
amittt555@gmail.com
6
Department of Civil Engineering, Jadavpur University, Kolkata, India
AUTHOR
Shibnath
Chakrabarty
sn_chakrabarty@yahoo.com
7
Department of Civil Engineering, Jadavpur University, Kolkata, India
AUTHOR
Joyashree
Roy
joyashreeju@gmail.com
8
Global Change Programme - Jadavpur University, Kolkata, India Asian Institute of Technology, Bangkok, Thailand Department of Economics, Jadavpur University, Kolkata, India
AUTHOR
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Pan, H., Bartolome, C., Gutierrez, E., Princevac, M., Edwards, R., Boarnet, M. G. and Houston, D. (2013). Investigation of roadside fine particulate matter concentration surrounding major arterials in five Southern Californian cities. Journal of the Air and Waste Management Association, 63(4), 482–498.
24
Planning Commission, G. of I. (2010). West Bengal Development Report. In Academic Foundation, New Delhi.
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Prabhu, V., Gupta, S. K., Madhwal, S. and Shridhar, V. (2019). Exposure to atmospheric particulates and associated respirable deposition dose to street vendors at the residential and commercial sites in dehradun city. Safety and Health at Work, 10(2), 237–244.
26
Roy, S. (2014). Emergence of shopping malls and its impact on the hawkers’ market economy: A case study of Kolkata city. Indian Journal of Applied Research, 4(8), 295–298.
27
Ruchirawat, M., Navasumrit, P., Settachan, D., Tuntaviroon, J., Buthbumrung, N. and Sharma, S. (2005). Measurement of genotoxic air pollutant exposures in street vendors and school children in and near Bangkok. Toxicology and Applied Pharmacology, 206(2), 207–214.
28
Sasikumar, S., Maheshkumar, K., Dilara, K. and Padmavathi, R. (2020). Assessment of pulmonary functions among traffic police personnel in Chennai city - A comparative cross-sectional study. Journal of Family Medicine and Primary Care, 9(7), 3356–3360.
29
Sidhu, M. K., Ravindra, K., Mor, S. and John, S. (2017). Household air pollution from various types of rural kitchens and its exposure assessment. Science of the Total Environment, 586, 419–429.
30
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31
Turcotte, R. A., Perrault, H., Marcotte, J. E. and Beland, M. (1992). A test for the measurement of pulmonary diffusion capacity during high-intensity exercise. Journal of Sports Sciences, 10(3), 229–235.
32
ORIGINAL_ARTICLE
Treatment Oilfield Produced Water using Coagulation/Flocculation Process (case study: Alahdab Oilfield)
Produced water is a large amount of water wasted throughout the crude oil extraction process, it's a mixture of the well's deposition water and the water of oil wells extraction water. Produced water contains oil, suspended solids and dissolves solid. This study tested produced water collected from Alahdab oilfield/middle oil company for oil content and suspended solid contamination using chemical precipitation and coagulation-flocculation for reinjection and environmental considerations. Coagulation/flocculation is a common method used as primary purification to oily wastewater treatment due to its usability, performance, and low cost. Coagulant experimental was completed by A jar test device, additives of ferric sulfate and aluminium sulfate were in a range about (10 ـ 40) ppm, as well as polyelectrolyte- (polyacrylamide) as an additional flocculent in the range (1.5-3) ppm. The results show that ferric sulfate was more efficient at removing turbidity than aluminium sulfate under the same conditions, with the best removal of turbidity at dose concentration 30 ppm of Ferric sulfate and a flocculent dose concentration of 2.5 ppm of polyacrylamide, also with oil content decreasing from 396.71 ppm to 53.56 ppm.
https://jpoll.ut.ac.ir/article_84065_e57fc0d6868ec7198bc7963360778aa1.pdf
2021-10-01
787
797
10.22059/poll.2021.322760.1071
Oilfield
Coagulation
Turbidity
oil content
Produced water
Hussein Ali
Jabbar
husseineng89.z@gmail.com
1
Department of Environmental Engineering, College of Engineering, Mustansiriyah University, P.O. Box 14150, Bab Al-Mu'adhem, Baghdad, Iraq
LEAD_AUTHOR
Mohammed jaafar Ali
Alatabe
mohammedjjafer@uomustansiriyah.edu.iq
2
Baghdad, Iraq
AUTHOR
Almojjly, A., Johnson, D., Oatley-Radcliffe, D. L. and Hilal, N. (2018). Removal of oil from oil-water emulsion by hybrid coagulation/sand filter as pre-treatment. Journal of Water Process Engineering, 26, 17–27.
1
Altaher, H., ElQada, E. and Omar, W. (2011). Pretreatment of wastewater streams from petroleum/petrochemical industries using coagulation. Advances in Chemical Engineering and Science, 1(04), 245.
2
Amuda, O. S. and Amoo, I. A. (2007). Coagulation/flocculation process and sludge conditioning in beverage industrial wastewater treatment. Journal of Hazardous Materials, 141(3), 778–783.
3
Bakke, T., Klungsøyr, J. and Sanni, S. (2013). Environmental impacts of produced water and drilling waste discharges from the Norwegian offshore petroleum industry. Marine Environmental Research, Vol. 92, pp. 154–169. https://doi.org/10.1016/j.marenvres.2013.09.012
4
Daud, Z., Awang, H., Nasir, N., Ridzuan, M. B. and Ahmad, Z. (2015). Suspended solid, color, COD and oil and grease removal from biodiesel wastewater by coagulation and flocculation processes. Procedia-Social and Behavioral Sciences, 195, 2407–2411.
5
Daud, Z., Nasir, N., Aziz Abdul Latiff, A., Ridzuan, M. B. and Awang, H. (2016). Treatment of biodiesel wastewater by coagulation-flocculation process using polyaluminium chloride (PAC) and polyelectrolyte anionic. ARPN Journal of Engineering and Applied Sciences, 11(20), 11855–11859.
6
Duan, J. and Gregory, J. (2003). Coagulation by hydrolysing metal salts. Advances in Colloid and Interface Science, 100, 475–502.
7
Farajnezhad, H. and Gharbani, P. (2012). Coagulation treatment of wastewater in petroleum industry using poly aluminum chloride and ferric chloride. International Journal of Research and Reviews in Applied Sciences, 13(1), 306–310.
8
Hadi, H. J., Al-Zobai, K. M. M. and Alatabe, M. J. A. (2020). Oil removal from produced water using Imperata cylindrica as low-cost adsorbent. Current Applied Science and Technology, 20(3), 494–511. https://doi.org/10.14456/cast.2020.33
9
Hassan, M. A. A., Li, T. P. and Noor, Z. Z. (2009). Coagulation and flocculation treatment of wastewater in textile industry using chitosan. Journal of Chemical and Natural Resources Engineering, 4(1), 43–53.
10
Hogg, R. (2005). Flocculation and dewatering of fine-suspension particles. Coagulation and Flocculation, 2nd Ed., CRC Press, Florida, USA.
11
Igunnu, E. T. (2014). Treatment of produced water by simultaneous removal of heavy metals and dissolved polycyclic aromatic hydrocarbons in a photoelectrochemical cell.
12
Jiménez, S., Micó, M. M., Arnaldos, M., Medina, F. and Contreras, S. (2018). State of the art of produced water treatmenJIMÉNEZ, S. et al. State of the art of produced water treatment. Chemosphere v. 192, p. 186–208 , 2018.978-953-51-0928-0. t. Chemosphere, Vol. 192, pp. 186–208.
13
Karbassi, A. and Pazoki, M. (2015). Optimization of coagulation/flocculation for treatment of wastewater. J. Environ. Treatment Tech, 3(2), 170–174.
14
Khalid, M. G. (2014). Treatment of emulsified oil in produced water from oil wells by adsorption on to corn-cob as sorbent. Al-Nahrain Journal for Engineering Sciences, 17(1), 83–90.
15
Lin, L., Jiang, W., Chen, L., Xu, P. and Wang, H. (2020). Treatment of produced water with photocatalysis: Recent advances, affecting factors and future research prospects. Catalysts, Vol. 10. https://doi.org/10.3390/catal10080924
16
Mohammed, T. J. and Abbas, E. R. (2017). Turbidity and Oil Removal from Oilfield Produced Water, by Coagulation-Flocculation Technique.
17
Mohammed, T. J., Hashim, M. and AL-Abideen, E. H. Z. (2007). Treatment of oily wastewater. Engineering and Technology Journal, 25(suppl. of No. 3).
18
Mohammed, T. J. and Shakir, E. (2018). Effect of settling time, velocity gradient, and camp number on turbidity removal for oilfield produced water. Egyptian Journal of Petroleum, 27(1), 31–36.
19
Mousa, K. M. and Al-Hasan, A. A. (2017). Oilfield produced water treatment by coagulation/flocculation processes. Proceedings of the Second Conference of Post Graduate Researches (CPGR’2017) College of Engineering.
20
Mousa, K. M. and Hadi, H. J. (2016). Coagulation/flocculation process for produced water treatment. International Journal of Current Engineering and Technology, 6(2), 551–555.
21
Puszkarewicz, A. (2008). Removal of Petroleum Compounds (Vol. 34, pp. 5–14). Vol. 34, pp. 5–14.
22
Ramavandi, B. (2014). Treatment of water turbidity and bacteria by using a coagulant extracted from Plantago ovata. Water Resources and Industry, 6, 36–50.
23
Sahu, O. and Chaudhari, P. (2013). Review on Chemical treatment of Industrial Waste Water. Journal of Applied Sciences and Environmental Management, Vol. 17. https://doi.org/10.4314/jasem.v17i2.8
24
Santana, C. R., Pereira, D. F., Sousa, S., Cavalcanti, E. B. and Silva, G. F. (2010). Evaluation of the process of coagulation/flocculation of produced water using Moringa oleifera Lam. as natural coagulant. Brazilian Journal of Petroleum and Gas, 4(3).
25
Sawain, A., Taweepreda, W., Puetpaiboon, U. and Suksaroj, C. (2009). The Effect of pH on the Stability of Grease and Oil in Wastewater from Biodiesel Production Process. Renewable Energy, pp. 0–4.
26
Shahriari, T., Karbassi, A. R. and Reyhani, M. (2019). Treatment of oil refinery wastewater by electrocoagulation–flocculation (Case Study: Shazand Oil Refinery of Arak). International Journal of Environmental Science and Technology, 16(8), 4159–4166.
27
Shi, J., Wang, X. and Wang, X. (2014). Optimizing Oily wastewater treatment via Wet Peroxide Oxidation using response surface methodology. Journal of the Korean Chemical Society, Vol. 58, pp. 80–84. https://doi.org/10.5012/jkcs.2014.58.1.80
28
Tzoupanos, N. D. and Zouboulis, a I. (2008). Coagulation-Flocculation Processes in Water / Wastewater Treatment : the Application of New Generation of Chemical Reagents. 6th IASME/WSEAS International Conference on HEAT TRANSFER, THERMAL ENGINEERING and ENVIRONMENT, pp. 309–317.
29
ORIGINAL_ARTICLE
Optimisation of Crystal Violet and Methylene Blue Dye Removal from Aqueous Solution onto Water Hyacinth using RSM
In this study, the adsorptive removal of two dyes (crystal violet (CV) and methylene blue (MB)) with HNO3 pre-treated water hyacinth powder (WHP) adsorbent was analysed. The experiments were designed using response surface methodology (RSM) with variable input parameter pH (2-12), adsorbent dose (0.5-3 g/L), initial dyes concentration (25-200 mg/L) and time (10-180 min). The optimization condition for dye removal were (pH = 7.22, adsorbent dose = 3.0 g/L, initial dye concentration = 195.28 mg/L and time of contact = 99.29 min) for CV with removal of 98.20% and (pH = 9.82, adsorbent dose = 2.96 g/L, initial dye concentration = 199.36 mg/L and contact time = 111.74 min) for MB with removal of 97.843%. The above findings observed that pre-treated water hyacinth powder can be utilised as a cost-effective and efficient adsorbent for dye effluent wastewater treatment.
https://jpoll.ut.ac.ir/article_84066_2f441f9efd9796c86f5e776dff911bd5.pdf
2021-10-01
799
814
10.22059/poll.2021.322778.1072
Adsorption
Central composite design
Dye
Water hyacinth
Rajnikant
Prasad
rajnikantprasad1312@gmail.com
1
A-704, Bhabha Bhavan, SVNIT, Icchhanath, Surat
LEAD_AUTHOR
Kunwar Durg
Yadav
ds17ce005@ced.svnit.ac.in
2
Civil Engineering Department, Sardar Vallabhbhai National Institute of Technology, Surat, Gujarat 395 007, India.
AUTHOR
Ahmad, M.A. and Alrozi, R. (2011). Removal of malachite green dye from aqueous solution using rambutan peel-based activated carbon: Equilibrium, kinetic and thermodynamic studies. Chem. Eng. J. 171, 510–516.
1
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2
Bagheri, A.R., Ghaedi, M., Asfaram, A., Bazrafshan, A.A. and Jannesar, R. (2017).
3
Comparative study on ultrasonic assisted adsorption of dyes from single system onto Fe3O4 magnetite nanoparticles loaded on activated carbon: Experimental design methodology. Ultrason. Sonochem. 34, 294–304.
4
Basaleh, A.A., Al-Malack, M.H. and Saleh, T.A. (2019). Methylene Blue removal using polyamide-vermiculite nanocomposites: Kinetics, equilibrium and thermodynamic study. J. Environ. Chem. Eng. 7, 103107.
5
Bayramoglu, G., Altintas, B. and Arica, M.Y. (2009). Adsorption kinetics and thermodynamic parameters of cationic dyes from aqueous solutions by using a new strong cation-exchange resin. Chem. Eng. J. 152, 339–346.
6
Bulut, Y. and Aydin, H. (2006). A kinetics and thermodynamics study of methylene blue adsorption on wheat shells. Desalination 194, 259–267.
7
Chiou, M.S. and Li, H.Y. (2003). Adsorption behavior of reactive dye in aqueous solution on chemical cross-linked chitosan beads. Chemosphere 50, 1095–1105.
8
Chowdhury, S. and Saha, P. (2010). Sea shell powder as a new adsorbent to remove Basic Green 4 (Malachite Green) from aqueous solutions: Equilibrium, kinetic and thermodynamic studies. Chem. Eng. J. 164, 168–177.
9
Chowdhury, S., Chakraborty, S. and Saha, P. Das (2013). Removal of crystal violet from aqueous solution by adsorption onto eggshells: Equilibrium, kinetics, thermodynamicsand artificial neural network modeling. Waste and Biomass Valorisation 4, 655–664.
10
Do, T.H., Nguyen, V.T., Dung, N.Q., Chu, M.N., Van Kiet, D., Ngan, T.T.K. and Van Tan, L. (2020). Study on methylene blue adsorption of activated carbon made from Moringa oleifera leaf. In Materials Today: Proceedings, (Elsevier Ltd), pp. 3405–3413.
11
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12
Fernandes, A.N., Almeida, C.A.P., Menezes, C.T.B., Debacher, N.A. and Sierra, M.M.D. (2007). Removal of methylene blue from aqueous solution by peat. J. Hazard. Mater. 144, 412–419.
13
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14
Garba, Z.N., Bello, I., Galadima, A. and Lawal, A.Y. (2015). Optimisation of adsorption conditions using central composite design for the removal of copper (II) and lead (II) by defatted papaya seed. Karbala Int. J. Mod. Sci. 2, 20–28.
15
Gosetti, F., Gianotti, V., Angioi, S., Polati, S., Marengo, E. and Gennaro, M.C. (2004). Oxidative degradation of food dye E133 Brilliant Blue FCF: Liquid chromatography-electrospray mass spectrometry identification of the degradation pathway. J. Chromatogr. A 1054, 379–387.
16
Gupta, V.K. and Suhas (2009). Application of low-cost adsorbents for dye removal - A review. J. Environ. Manage. 90, 2313–2342.
17
Hou, M.F., Ma, C.X., Zhang, W. De, Tang, X.Y., Fan, Y.N. and Wan, H.F. (2011). Removal of rhodamine B using iron-pillared bentonite. J. Hazard. Mater. 186, 1118–1123.
18
Huang, L.H., Sun, Y.Y., Yang, T. and Li, L. (2011). Adsorption behavior of Ni (II) on lotus stalks derived active carbon by phosphoric acid activation. Desalination 268, 12–19.
19
Khaled, A., Nemr, A. El, El-Sikaily, A. and Abdelwahab, O. (2009). Removal of Direct N Blue-106 from artificial textile dye effluent using activated carbon from orange peel: Adsorption isotherm and kinetic studies. J. Hazard. Mater. 165, 100–110.
20
Khan, T.A., Khan, E.A. and Shahjahan (2015). Removal of basic dyes from aqueous solution by adsorption onto binary iron-manganese oxide coated kaolinite: Non-linear isotherm and kinetics modeling. Appl. Clay Sci. 107, 70–77.
21
Khosravi, M. and Arabi, S. (2016). Application of response surface methodology (RSM) for the removal of methylene blue dye from water by nano zero-valent iron (NZVI). Water Sci. Technol. 74, 343–352.
22
Kumar, K., Saravana Devi, S., Krishnamurthi, K., Gampawar, S., Mishra, N., Pandya, G.H., and Chakrabarti, T. (2006). Decolorisation, biodegradation and detoxification of benzidine based azo dye. Bioresour. Technol. 97, 407–413.
23
Kumari, M. and Gupta, S.K. (2019). Response surface methodological (RSM) approach for optimising the removal of trihalomethanes (THMs) and its precursor’s by surfactant modified magnetic nanoadsorbents (sMNP) - An endeavor to diminish probable cancer risk. Sci. Rep. 9, 18339.
24
Kushwaha, A.K., Gupta, N. and Chattopadhyaya, M.C. (2014). Removal of cationic methylene blue and malachite green dyes from aqueous solution by waste materials of Daucus carota. J. Saudi Chem. Soc. 18, 200–207.
25
Lalhruaitluanga, H., Prasad, M.N.V. and Radha, K. (2011). Potential of chemically activated and raw charcoals of Melocanna baccifera for removal of Ni(II) and Zn(II) from aqueous solutions. Desalination 271, 301–308.
26
Lin, J., Ye, W., Baltaru, M.C., Tang, Y.P., Bernstein, N.J., Gao, P., Balta, S., Vlad, M., Volodin, A., Sotto, A., Luis, P., Zydney, A.L., Van der Bruggen, B., (2016). Tight ultrafiltration membranes for enhanced separation of dyes and Na2SO4 during textile wastewater treatment. J. Memb. Sci. 514, 217–228.
27
Le Man, H., Behera, S.K. and Park, H.S. (2010). Optimisation of operational parameters for ethanol production from korean food waste leachate. Int. J. Environ. Sci. Technol. 7, 157–164.
28
Medhat, A., El-Maghrabi, H.H., Abdelghany, A., Abdel Menem, N.M., Raynaud, P.,
29
Moustafa, Y.M., Elsayed, M.A. and Nada, A.A. (2021). Efficiently activated carbons from corn cob for methylene blue adsorption. Appl. Surf. Sci. Adv. 3, 100037.
30
Mittal, A., Mittal, J., Malviya, A., Kaur, D. and Gupta, V.K. (2010). Decoloration treatment of a hazardous triarylmethane dye, Light Green SF (Yellowish) by waste material adsorbents. J. Colloid Interface Sci. 342, 518–527.
31
Mohan, S.V., Ramanaiah, S. V. and Sarma, P.N. (2008). Biosorption of direct azo dye from aqueous phase onto Spirogyra sp. I02: Evaluation of kinetics and mechanistic aspects. Biochem. Eng. J. 38, 61–69.
32
Myers, R. h., Montgomery, D.C. and Anderson-Cook, C.M. (2009). Response Surface Methodology: Process and Product Optimisation Using Designed Experiments (John Wiley & Sons).
33
Pathania, D., Sharma, S. and Singh, P. (2017). Removal of methylene blue by adsorption onto activated carbon developed from Ficus carica bast. Arab. J. Chem. 10, S1445–S1451.
34
Prasad, R. and Yadav, K.D. (2020). Use of response surface methodology and artificial neural network approach for methylene blue removal by adsorption onto water hyacinth. Water Conserv. Manag. 4, 73–79.
35
Prasad, R., Sharma, D., Yadav, K.D. and Ibrahim, H. (2021). Eichhornia crassipes as biosorbent for industrial wastewater treatment: Equilibrium and kinetic studies. Can. J. Chem. Eng. 1–12.
36
Rai, A., Mohanty, B. and Bhargava, R. (2016). Supercritical extraction of sunflower oil: A central composite design for extraction variables. Food Chem. 192, 647–659.
37
Sadhukhan, B., Mondal, N.K. and Chattoraj, S. (2016). Optimisation using central composite design (CCD) and the desirability function for sorption of methylene blue from aqueous solution onto Lemna major. Karbala Int. J. Mod. Sci. 2, 145–155.
38
Saltabaş, Ö., Teker, M. and Konuk, Z. (2012). Biosorption of cationic dyes from aqueous solution by water hyacinth roots. Glob. Nest J. 14, 24–31.
39
Samarbaf, S., Tahmasebi Birgani, Y., Yazdani, M. and Babaei, A.A. (2019). A comparative removal of two dyes from aqueous solution using modified oak waste residues: Process optimisation using response surface methodology. J. Ind. Eng. Chem. 73, 67–77.
40
Sarma, G.K., Sen Gupta, S. and Bhattacharyya, K.G. (2016). Adsorption of Crystal violet on raw and acid-treated montmorillonite, K10, in aqueous suspension. J. Environ. Manage. 171, 1–10.
41
Tan, I.A.W., Ahmad, A.L. and Hameed, B.H. (2009). Adsorption isotherms, kinetics, thermodynamics and desorption studies of 2,4,6-trichlorophenol on oil palm empty fruit bunch-based activated carbon. J. Hazard. Mater. 164, 473–482.
42
Tharaneedhar, V., Senthil Kumar, P., Saravanan, A., Ravikumar, C. and Jaikumar, V. (2017). Prediction and interpretation of adsorption parameters for the sequestration of methylene blue dye from aqueous solution using microwave assisted corncob activated carbon. Sustain. Mater. Technol. 11, 1–11.
43
Vaez, M., Zarringhalam Moghaddam, A. and Alijani, S. (2012). Optimisation and modeling of photocatalytic degradation of azo dye using a response surface methodology (RSM) based on the central composite design with immobilised Titania nanoparticles. Ind. Eng. Chem. Res. 51, 4199–4207.
44
Vakili, M., Rafatullah, M., Gholami, Z. and Farraji, H. (2016). Treatment of Reactive Dyes from Water and Wastewater through Chitosan and its Derivatives. In Smart Materials for Waste Water Applications, pp. 347–377.
45
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46
Zhou, W., Zhu, D., Tan, L., Liao, S., Hu, Z. and Hamilton, D. (2007). Extraction and retrieval of potassium from water hyacinth (Eichhornia crassipes). Bioresour. Technol. 98, 226–231.
47
ORIGINAL_ARTICLE
Assessment of Water Resources Pollution Carrying Capacity in The Sa Kaeo Special Economic Zone, Thailand
The Phromhot Canal is the only natural water source for consumption and agriculture the Sa Kaeo special economic zone, Thailand. At present, the Phromhot Canal is facing a serious problem with water quality. Our study carried out to analyze and assess the pollution carrying capacity of the natural water resource. The sampling sites were examined 7 stations cut across the downstream areas. All these stations were served as the control station to represent the actual condition of the Phromhot Canal. The results indicated that the water quality of the Phromhot Canal after flowing through the Aranyaprathet Municipality's wastewater treatment plant (AM's-WWTP) was severely contaminated. Effluents from the AM's-WWTP does not meet the effluent quality standard of the Ministry of Natural Resources and Environment, Thailand. In addition, it can flow into the water body up to 6,439.55 m3/day. The maximum amount of a pollutant (in terms of BOD loading) allowed to enter a water body of the Phromhot Canal should be ≤ 0.08 kgBOD/day (dry period) and 16.52 kgBOD/day (wet period). While the Phromhot Canal has to carry BOD loading up to 51.12 kgBOD/day. For this reason, the Phromhot Canal at after flowing through the WWTP was unable to the pollution carrying capacity. From the field survey, the AM's-WWTP is not suitable for wastewater treatment, which has a capacity of 923.93 m3/day. Therefore, it is necessary to strictly control the drainage of the wastewater from the Aranyaprathet Municipality's wastewater treatment system, both quantitative and geographic.
https://jpoll.ut.ac.ir/article_84113_6636209f8f13b03303f38f33221d3cd9.pdf
2021-10-01
815
830
10.22059/poll.2021.322758.1073
Water quality
Municipal Wastewater
Pollutant emission
BOD loading
Chitsanuphong
Pratum
enchitsanu@gmail.com
1
Faculty of Environment and Resource Studies, Mahidol University, P.O. Box 73170, Nakhon Pathom, Thailand
LEAD_AUTHOR
Akyol, A. (2012). Treatment of paint manufacturing wastewater by electrocoagulation. Desalination., 285; 91–99.
1
Altaee, A., Sharif, A., Zaragoza, G. and Ismail, A. (2015). Evaluation of FO-RO and PRO-RO designs for power generation and seawater desalination using impaired water feeds. Desalination, 368; 27–35.
2
Angriani, P., Sumarmi, Ruja, I. N. and Bachri, S. (2018). River management: The importance of the roles of the public sector and community in river preservation in Banjarmasin (A case study of the Kuin River, Banjarmasin, South Kalimantan – Indonesia). Sustain. Cities Soc., 43; 11-20.
3
APHA, 2012. Standard methods for the examination of water and wastewater, 22nd edition edited by Rice, E. W., Baird, R. B., Eaton A. D. and Clesceri, L. S. American Public Health Association (APHA), American Water Works Association (AWWA) and Water Environment Federation (WEF), Washington, D.C., USA.
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Aziz, H. A., Adlan, M. N., Zahari, M. S. M. and Alias, S. (2004). Removal of ammoniacal nitrogen (N-NH3) from municipal solid waste leachate by using activated carbon and limestone. Waste Manage. Res., 22; 371-375.
6
Bao, X., Wu, Q., Shi, W., Wang, W., Yu, H., Zhu, Z., Zhang, X., Zhang, Z., Zhang, R. and Cui, F. (2019). Polyamidoamine dendrimer grafted forward osmosis membrane with superior ammonia selectivity and robust antifouling capacity for domestic wastewater concentration. Water Res., 153; 1–10.
7
Boyd, G. R., Zhang, S. and Grimm, D. A. (2005). Naproxen removal from water by chlorination and biofilm processes. Water Res., 39; 668–676.
8
Bulsathaporn, A. (2008). The application of mathematical models for an environmental flow assessment and total maximum daily load (TMDL) of prachinburi–bangpakong river. Dissertation, Mahidol University, 165p.
9
Cao, F., Lu, Y., Dong, S. and Li, X. (2020). Evaluation of natural support capacity of water resources using principal component analysis method: a case study of Fuyang district, China. Appl. Water Sci., 10: 192.
10
Chang, I. S., Jang, J. K., Gil, G. C., Kim, M., Kim, H. J., Cho, B. W. and Kim, B. H. (2004). Continuous determination of biochemical oxygen demand using microbial fuel cell type biosensor. Biosens. Bioelectron., 19(6); 607-613.
11
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47
ORIGINAL_ARTICLE
Biological and Geochemical Studies of Urinary Tract Stones in Lorestan Province
Mineralogy studies can help understand the interactions of geographical, environmental, and geological factors. Considering frequent occurrence of urinary tract stones in the south and west of Iran, the present paper examines trace elements, like heavy metals, in 53 urine stone samples collected from patients in Lorestan Province. It investigates the mineralogy of the stones, using X-ray diffraction. The samples are then classified into five mineral groups (calcium oxalate, urate, cysteine, calcium oxalate-urate, and calcium oxalate/phosphate). Results from this analysis are confirmed by SEM images, showing the crystalline form of the mineral phases. The microscopic studies show that only the mineral group of calcium oxalate (whewellite) could be detected in thin sections, prepared from urinary tract stone samples. The main and trace elements in each group are determined through ICP-MS method with the results showing that calcium is the most abundant substance in urinary tract stones, compared to other elements. This is caused by the role of calcium in most basic functions of cell metabolism. The correlation between magnesium and strontium is 0.64, originated from the placement of high amounts of strontium in calcium oxalate minerals. The positive correlation between sodium and calcium also indicates that sodium is replaced by calcium due to the similarity of the ionic radius in the crystal structure. Results from this study can help us find the causes behind the frequent occurrence of urinary tract stones in Lorestan Province.
https://jpoll.ut.ac.ir/article_84109_cecddfbd2406a72e4e2fbfd74ae95b16.pdf
2021-10-01
831
842
10.22059/poll.2021.322969.1075
mineralogy
scanning electron microscope
calcium oxalate
Urinary tract stones
Saadat
Aghajari
saadataghajari55@gmail.com
1
Department of Environment, Ahvaz Branch, Islamic Azad University, Ahvaz, Iran
AUTHOR
Sima
Sabzalipour
shadi582@yahoo.com
2
Department of Environment, Ahvaz Branch, Islamic Azad University, Ahvaz, Iran
LEAD_AUTHOR
Ahad
Nazarpour
ahadnazarpour59@gmail.com
3
Department of Geology, Ahvaz Branch, Islamic Azad University, Ahvaz, Iran
AUTHOR
Maryam
Mohammadiroozbahani
mmohammadiroozbahani@yahoo.com
4
Department of Environment, Ahvaz Branch, Islamic Azad University, Ahvaz, Iran
AUTHOR
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43
ORIGINAL_ARTICLE
Seasonal Dynamics of Heavy Metal Concentrations in Water, Fish and Sediments from Haor Region of Bangladesh
Heavy metal concentrations in water, fish, and sediments from Bangladesh's haor region were investigated. Fish and sediment samples were taken once a season and evaluated using standard methods, while water samples were collected monthly. Results showed that metals in water (mg/L) were found in order of Mn (0.1694) > Cu (0.0189) > Zn (0.0045) > Pb (0.0040) > Cd (0.0028) within the maximum permissible level of Environment Conservation Rules (ECR). Mean concentrations of metal in fish (mg/kg–dry wt.) found in order of Zn (56.16) > Cu (25.47) > Mn (4.36) > Pb (2.19) > Cd (1.27) that were higher than maximum allowable level of Food and Agricultural Organization (FAO) except Cu. Metal in sediments (mg/kg) found in order of Mn (127.61) > Zn (32.51) > Pb (10.09) > Cu (5.40) > Cd (0.43), and except Cu all metal concentrations were lower than the Environmental Protection Agency's (EPA) probable effect concentrations. In water and sediments, pollution indices revealed a critical pollution threshold for water, and a range of unpolluted to highly polluted for sediments. Sampling sites had low potential ecological risk, despite the fact that metals were showing signs of a negative impact on people' health. Furthermore, bio-concentration factor for fish and water was low to extremely high, but for fish and sediment was low. The level of heavy metal contamination in haor shows the situation is alarming for biota and residents of the region. The relevant authority should control and monitor the aquatic ecology in order to protect it.
https://jpoll.ut.ac.ir/article_84110_712e1d3d3b31b03ed81fb88f6f54a28f.pdf
2021-10-01
843
857
10.22059/poll.2021.323206.1076
aquatic environment
Heavy metal
Health risk
pollution indices
Bangladesh
Md. Sirajul
Islam
islammstazu@yahoo.com
1
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Md. Mazedur
Rahman
mazeduresrm@gmail.com
2
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Md. Humayun
Kabir
kabirmh07@gmail.com
3
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
LEAD_AUTHOR
Md. Enamul
Hoq
hoq_me@yahoo.com
4
Bangladesh Fisheries Research Institute, Freshwater Station, Mymensingh-2201, Bangladesh
AUTHOR
Nowara Tamanna
Meghla
nowaratamanna@gmail.com
5
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Suravi
Suravi
suravi_esrm@yahoo.com
6
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Shamim
Al Mamun
shamim084du@yahoo.com
7
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Md. Eusuf
Sarker
yousufmbstu3740@gmail.com
8
Department of Environmental Science and Resource Management, Mawlana Bhashani Science and Technology University, Tangail-1902, Bangladesh
AUTHOR
Adefemi O.S., Olaofe O. and Asaolu, S.S., (2004), Concentration of Heavy metals in water sediment and fish parts (Illisha africana) from Ureje dam, Ado-Ekiti, Ekiti State. Nigerian Journal of Biology and Physical Sciences, 3, 111-114.
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Ahmed M.K., Ahamed S., Rahman S., Haque M.R. and Islam, M.M., (2009), Heavy metals concentration in water, sediments and their bioaccumulations in some freshwater fishes and mussel in Dhaleshwari River, Bangladesh. Terrestrial and Aquatic Environmental Toxicology, 3(1), 33-41.
4
Akter D., Islam M.S., Hoque M.M.M., Kabir M.H. and Rehnuma, M., (2019), Assessment of heavy metals contents in water and sediments of the Meghna River in Bangladesh. Bangladesh Journal of Environmental Science, 37, 32-39.
5
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81
ORIGINAL_ARTICLE
Exploring the use of Macrophytes as Biological Indicators for Organic Pollution of Chanchaga River in North Central Nigeria
Macrophytes are creatures with low versatility and cannot stay away from any mix of streamflow, nutrient accessibility, and other physical and chemical attributes that impact their survival in the aquatic system. Sampling for macrophytes in Chanchaga River was conducted monthly for a 6-month period (May - October 2019). Sampling stations were selected at approximately equal distance along the streamline, the aquatic vegetation were surveyed, and some environmental variables were analysed using standard methods. Results obtained indicated that temperature ranged from 24.6-28.4°C; pH 6.4 -9.7; Electrical conductivity 28.0-79.0μS cm-1; Total dissolved solids 16-75 mg L-1; Dissolved oxygen(DO) 1.3-5.2 mg L-1; Nitrate 0.217-0.654 mg L-1; Phosphate 0.084-0.211 mg L-1; Biological oxygen demand (BOD) 0.89-5.4 mg L-1 and total alkalinity 8.00-11.00 mgL-1 for the study period. A total of eleven (11) macrophyte species belonging to ten genera and eight families were identified during the entire study. Variations in terms of families showed that Araliaceae was the most abundant followed by Poaceae, while Cyperaceae had more species throughout the study period. The high frequency of Araliaceae, Cyperaceae, and Poaceae families suggests that the environmental characteristics favour these species. We propose the use of Cyperus digitatus, Cyperus papyrus and Mimosa spp. as macrophytes indicators of organic pollution in Chanchaga River.
https://jpoll.ut.ac.ir/article_84042_078e6d8255617d8e7232c1950bf9e665.pdf
2021-10-01
859
870
10.22059/poll.2021.323765.1087
aquatic plants
Araliaceae
Environmental variables
lotic system
physicochemical parameters
Andrew
Ali
aliandy598@gmail.com
1
Applied Hydrobiology Unit, Department of Animal Biology, Federal University of Technology, P.M.B 65, Minna, Niger State, Nigeria
AUTHOR
Grace
Obi-Iyeke
geoobiiyeke@delsu.edu.ng
2
Department of Botany, Delta State University, P.M.B. 1, Abraka, Nigeria
AUTHOR
Unique
Keke
uniquekkn@gmail.com
3
Applied Hydrobiology Unit, Department of Animal Biology, Federal University of Technology, P.M.B 65, Minna, Niger State, Nigeria
AUTHOR
Francis
Arimoro
francisarimoro@gmail.com
4
Applied Hydrobiology Unit, Department of Animal Biology, Federal University of Technology, P.M.B 65, Minna, Niger State, Nigeria
LEAD_AUTHOR
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44
ORIGINAL_ARTICLE
Improving Phytoremediation Efficiency of Copper-spiked Calcareous Soils by Humic Acid Applications
In current study, the enhanced efficiency of copper (Cu) phytoremediation potential of Calendula officinalis L. was investigated in a Cu-spiked calcareous soil, using foliar and soil application of humic acid. For this purpose, in a greenhouse experiment, seedlings of C. officinalis were transferred to Cu-spiked soils (0, 250 and 500 mg/kg) and treated separately with soil (soil drench) and foliar (spraying plant leaves) humic acid applications at different levels (0, 10, 20 μM). The humic acid treatments were applied 2 weeks after transferring plant, and eventually the various biochemical-physiological traits and phytoremediation indices of Cu in C. officinalis were measured at (specific) time points. According to the results, C. officinalis grew normally without any toxicity signs in Cu-spiked soils, however with increasing the Cu levels, the dry weight biomass decreased and antioxidant enzymes activities increased. Both foliar and soil humic acid application in Cu-spiked soils increased dry weight biomass, photosynthetic pigment contents, Cu concentration, and bioconcentration factor (BCF). Furthermore, the application of this organic substance, obviously moderated the Cu stress since the antioxidant enzymes activities reduced compared to the control. Based on the results, the obtained translocation factor (TF) and BCF values of Cu, which were >1, indicated that this plant is a Cu-hyperaccumulator, which could extract Cu via phytoextraction mechanism. Generally, the results of this study showed that, among the humic acid treatments, application of 20 μM (especially soil drench application) had the best effect on increasing Cu phytoremediation efficiency in the studied soil and it recommended to enhance the efficiency of Cu phytoremediation in calcareous soils.
https://jpoll.ut.ac.ir/article_84114_a543792208d1857c60067f709869020e.pdf
2021-10-01
871
884
10.22059/poll.2021.324145.1095
Calendula officinalis L. Alkaline soil
Heavy metals
Humic Acid
Phytoextraction
Vahid Reza
Saffari
safariv@uk.ac.ir
1
Research and Technology Institute of Plant Production, Shahid Bahonar University, Kerman, Iran
LEAD_AUTHOR
Mahboub
Saffari
mahboobsaffari@gmail.com
2
Department of Environment, Institute of Science and High Technology and Environmental Sciences, Graduate University of Advanced Technology, Kerman, Iran.
AUTHOR
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55
ORIGINAL_ARTICLE
Biochemical and Physiochemical Assessment of Air Pollution Tolerance Index of Selected Plant Species at Ikpoba Okha Gas Flaring Site, Edo State, Nigeria
The Air Pollution Tolerance index (APTI) of six plants located within Ikpoba Okha gas flaring site in Oredo Local Government Area of Edo State, Nigeria during wet and dry seasons were assessed. Plant samples for this research work were randomly collected from the vicinity of the flaring site. Six (6) sample of each plant was used for laboratory analysis. The plant parameters assessed include relative water content (RWC), the ascorbic acid content (AAC), total leaf chlorophyll (TLC) and pH extract of the leaves and were used to compute the Air pollution tolerance indices (APTI). Based on the analyzed result, the RWC in Drypetes leonensis, Ficus exasperata Vahl, Chromolaena odorata (Linn) and Gmelina arborea Roxb. ex Smith species in dry season were higher than those in wet season. Icacina tricantha showed a relatively high level of acidity when compared to others. A. boonei De Wild has the highest ascorbic acid content in the leaves in both seasons. The highest level of chlorophyll contents was recorded in the dry season with Drypetes leonensis having the highest, followed by Icacina trichantha. There was no statistically significant difference in pH and total chlorophyll contents between samples collected in wet and dry season; however, there were significant difference observed in ascorbic acid and RWC in both seasons. APTI in wet and dry season showed a statistically significant difference. This study recommends planting of tolerant species that can acts as bio-indicators especially in gas flaring stations in Nigeria.
https://jpoll.ut.ac.ir/article_84115_dc1f1b3713b93caf12516e3792426ea4.pdf
2021-10-01
885
893
10.22059/poll.2021.324224.1098
Chlorophyll
Ascorbic acid
pH
tolerance
Bio
indicators
Anthony
Akande
anthonyakande17@gmail.com
1
Institute of Ecology and Environmental Studies, Obafemi Awolowo University, Ile Ife, Osun State, Nigeria
LEAD_AUTHOR
Esther
Dada
dada.omotola@gmail.com
2
Department of Biological Sciences, Elizade University, Ilara Mokin, Ondo State.
AUTHOR
Johnson
Olusola
johnsonolusola06@gmail.com
3
Department of Geography and Planning Science, Ekiti State University, Ado Ekiti, Nigeria
AUTHOR
Moyosola
Adeyemi
moyo_adeyemi@yahoo.com
4
Department of Geology and Mineral Sciences, Crawford University, Igbesa, Ogun State, Nigeria
AUTHOR
Aasawari, A .T. and Umesh, B. K. (2017). Assessment of air pollution tolerance index of plants; a comparative study. Int. J. Pharm Pharm Sci., 9(7); 83-89.
1
Agbaire, P.O. and Esiefarienrhe, E. (2009). Air pollution tolerance indices of some plants around Otorogun Gas Plant in Delta state, Nigeria. J. Appl. Sci. Environ. Manag. 13(1):11–14.
2
Aguiar-Silva, C., Brandao, S.E., Domingos, M. and Bulbovas, P. (2016). Antioxidant responses of Atlantic Forest native tree species as indicators of increasing tolerance to oxidative stress when they are exposed to air pollutants and seasonal tropical climate. Ecological Indicators. 63: 154-164.
3
Bignal, K.L., Ashmore, M.R. and Headley, A.D. (2008). Effects of air pollution from road transport on growth and physiology of six transplanted bryophyte species. Environ. Poll. 156: 332-340
4
Conklin, P. L. (2001). Recent advances in the role and biosynthesis of ascorbic acid in plants. Plant, Cell & Environment. 24: 383-394.
5
Escobedo, F.J., Wanger, J.E. and Nowak, D.J. (2008). Analyzing the cost effectiveness of Santiago, Chile’s policy of using urban forests to improve air quality. Journal of Environmental Management. 86(1): 148-157.
6
Govindaraju, M., Ganeshkumar, R.S., Muthukumaran, V.R. and Visvanathan, P. (2012). Identification and evaluation of air-pollution tolerant plants around lignite-based thermal power station for greenbelt development. Environ Sci Pollut Res 19(4):1210–1223
7
Iqbal, M.Z., Shafig, M., Qamar Zaidi, S. and Athar, M. (2015). Effect of automobile pollution on chlorophyll content of roadside urban trees. Global J. Environ. Sci. Manage. 1(4): 283-296.
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Joshi, N., Chauhan, A. and Joshi, P.C. (2009). Impact of industrial air pollutants on some biochemical parameters and yield in wheat and mustard plants. Environmentalist, 29: 398-404
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Joshi, P.C. and Swami, A. (2007). Physiological responses of some tree species under roadside automobile pollution stress around city of Haridwar, India. Environmentalist 27:365–374.
10
Joshi, P.C. and Swami, A. (2009). Air pollution induced changes in the photosynthetic pigments of selected plant species. J. Environ. Biol. 30:295-298.
11
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14
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Kumar, M. and Nandini, N. (2013). Identification and Evaluation of Air Pollution Tolerance Index of Selected Avenue Tree Species of Urban Bangalore, India, Int. J. Emerg. Technol. Comput. Appl. Sci., 13: 388-390.
16
Kumari, J. and Deswal, S. (2017). Air pollution tolerance index: A comparative study. J Bas App Eng Res.4:128-133.
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Liu, Y.J and Ding, H. (2008).Variation in air pollution tolerance index of plants near a steel factory: implication for landscape –plant species, selection for industrial areas. Wseas Trans. Environ. Dev. 4:24-32.
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Ninave, A.S. (2001). Evaluation of air pollution tolerance index of selected Plants. www.jeb.co.in/. / paper_26. Pdf. Accessed 18/05/2021.
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Panda, L.R.L. and Aggarwal, R.K. (2018).Assessment of air pollution tolerance index and anticipated performance index of plants growing alongside the roads in sub- temperate condition of Himachal Pradesh, India. Int J Cur Microbiol App Sci; 7: 79-93.
20
Pathak, V., Tripathi, B.D. and Mishra, V.K. (2011). Evaluation of anticipated performance index of some tree species for green belt development to mitigate traffic generated noise. Urban Forestry and Urban Greening, 10 (1): 61-66
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Rai, P.K. (2013). Environmental magnetic studies of particulates with special reference to biomagnetic monitoring using roadside plant leaves. Atmos. Environ., 72: 113-129
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Shannigrahi, A.S., Fukushim, T. and Sharma, R.C (2004). Anticipated Air Pollution Tolerance of some plant species considered for green belt development in and around an industrial/urban area in India: An overview. Int. J. Environ. Stud. 61(2):125-137.
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26
Tanee, F. B. G., Albert, E.and Amadi, B. R. (2014). Biochemical properties and Air pollution tolerance indices of plants in Port Harcourt city, Nigeria British Journal of Applied Science and Technology 4(34): 4835-4845.
27
Tanee, F. B. G. and Albert, E. (2013). Air pollution tolerance indices of plants growing around Umuebulu Gas Flare Station in Rivers State, Nigeria; African Journal of Environmental Science and Technology Vol. 7(1), pp. 1-8.
28
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29
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31
ORIGINAL_ARTICLE
The Effect of Land Use Changes on Water Quality (Case Study: Zayandeh-Rud Basin, Isfahan, Iran)
The present study aims at investigating land use changes (as one of the effective human factors on water systems) as well as its relation with water quality at spatial scales of the entire basin, sub-basin and defined buffers (10 and 15 km) in Zayandeh-Rud Basin, Isfahan, Iran. By means of supervised classification method along with maximum likelihood algorithm, it classifies the land use map into five categories, including agriculture, bare lands, urban areas, vegetation, and water. The research collects data for 11 water quality parameters in seven sampling stations of Zayandeh-Rud Basin in 2002, 2009, and 2015 from Isfahan Water and Sewerage Organization. Correlation analysis is then conducted to investigate the effect of land use changes on water quality at different spatial scales. Land use analysis in the entire basin shows that despite an increase in urban and agricultural lands from 2002 to 2015, bare lands, vegetation, and water covers have had a decreasing trend. Moreover, various land uses at different scales show some correlation with water quality parameters. The strongest correlations in this study belong to sub-basin scale. Therefore, it is recommended to use this spatial scale to investigate the relation between land use and water quality parameters
https://jpoll.ut.ac.ir/article_84043_f6e64d5c8ced60761571fdc16f2f4459.pdf
2021-10-01
895
904
10.22059/poll.2021.324387.1100
Human Factors
surface water
Spatial scale
urbanization
Mahin
Saedpanah
mahin3921@gmail.com
1
Environmental Pollution, University of Kurdistan, Sanandaj, Iran
LEAD_AUTHOR
Marzieh
Reisi
m.reisi@uok.ac.ir
2
Environmental Engineering, University of Melbourne, Melbourne, Australia
AUTHOR
Mozhgan
Ahmadi Nadoushan
m.ahmadi@khuisf.ac.ir
3
Department of Environmental Sciences, Waste and Wastewater Research Center, Isfahan (Khorasgan) Branch, Islamic Azad Universit, Isfahan, Iran
AUTHOR
Alavipanah, S.K. (2016). Fundamentals of modern remote sensing and interpretation of satellite images and aerial photos. Tehran University Press., 800 p.
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Al-hadithi, M. (2012). Application of water quality index to assess suitability of groundwater quality for drinking purposes in Ratmao-Pathri Rao watershed, Haridwar District, India. American Journal of Scientific and Industrial Research., 3(6); 395-402.
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Camara, M., Jamil, N.R. and Abdullah, A.F. (2019). Impact of land uses on water quality in Malaysia: a review. Ecological Processes., 8(10); 1-10.
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Chaudhry, F.N. and Malik, M.F. (2017). Factors affecting water pollution: a review. Journal of Ecosystem and Ecography., 7(225); 1-3.
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Giri, S. and Qiu, Z. (2016). Understanding the relationship of land uses and water quality in twenty first century: a review. Journal of Environmental Management., 173, 41-48.
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18
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26
ORIGINAL_ARTICLE
Biosorption of Reactive Red 120 Dye from Aqueous Solutions by using Mahagoni (Swietenia mahagoni) Wood and Bark Charcoal: Equilibrium, and Kinetic Studies
This study analyzed the potential use of Mahagoni wood charcoal (MWC) and Mahagoni bark charcoal (MBC) as biosorbent for reactive red 120 (RR 120) dye removal from aqueous solutions. The effect of different operating parameters such as contact time (1–210 min), pH (3–11), adsorbent dose (1–20 g/L), and initial RR 120 concentration (5–70 mg/L) on adsorption processes was studied under batch adsorption experiments. The maximum removal of RR 120 by MWC (78%) and MBC (88%) was achieved when the optimum conditions were initial RR 120 concentration (5 mg/L), pH (3), adsorbents dose (10 g/L) and equilibrium contact time (150 min). The RR 120 adsorption data of MWC and MBC were better described by the Langmuir and Freundlich isotherm models, respectively. The MWC and MBC showed maximum adsorption capacities of 3.806 and 5.402 mg/g, respectively. Kinetic adsorption data of all adsorbents (MWC and MBC) followed the pseudo-second-order model and this adsorption process was controlled by chemisorption with multi-step diffusion. A lower desorption rate advocated that both strong and weak binding forces could exist between RR 120 molecules and adsorbents. The study results revealed that the utilization of either MWC and or MBC as an adsorbent for treating RR 120 is effective and environmentally friendly.
https://jpoll.ut.ac.ir/article_84063_a8d404c52fda7d67f889e4b08a8592b2.pdf
2021-10-01
905
921
10.22059/poll.2021.325135.1110
Adsorption efficiency
Adsorbent
anionic dye
Biomass
Tapos Kumar
Chakraborty
taposchakraborty@just.edu.bd
1
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O.Box 7408, Jashore, Bangladesh.
LEAD_AUTHOR
Gopal
Ghosh
prianka_ghosh@yahoo.com
2
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
Mst. Nowshin
Akter
nowshinkhushi@gmail.com
3
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
Keya
Adhikary
keyaadhikaryest@gmail.com
4
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
Md. Shahnul
Islam
shahnulkoushik140208@gmail.com
5
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
Prianka
Ghosh
priankaes08@gmail.com
6
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O.Box 7408, Jashore, Bangladesh.
AUTHOR
Samina
Zaman
saminazaman25@gmail.com
7
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
Ahsan
Habib
esthabib28@gmail.com
8
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
A. H. M. Enamul
Kabir
ahsanhabibsobuj71@gmail.com
9
Department of Environmental Science and Technology, Jashore University of Science and Technology, P.O. Box 7408, Jashore, Bangladesh.
AUTHOR
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55
ORIGINAL_ARTICLE
The Effect of Monsoon on Chemical Composition and Bioaccumulation of Heavy Metals in Scomberomorus commerson, Lacepede 1800, from Oman Sea
This study was performed to determine the chemical compositions and heavy metals in the muscle of Scomberomorus commerson from the Oman Sea, during the two seasons, pre-monsoon and post-monsoon in 2018. The protein, fat, moisture, and ash contents were determined by AOAC (Association of Official Analytical Chemists) methods. Heavy metal (Zn, Cu, and Pb) analyses were performed by atomic absorption spectrophotometer after acid digestion. There were significant differences between protein, fat, moisture, and ash values in muscle tissue in two seasons (P< 0.05). The highest content of protein (22.53±2.09%) and fat (4.15±1.25%) was recorded in pre-monsoon. The mean concentrations of heavy metals (μg g-1dw) in muscle tissue were 0.08-0.05 for Zn, 0.04-0.02 for Cu, and 0.02-0.01 for Pb in the pre and post-monsoon, respectively. The accumulation of heavy metals in muscle followed the Zn>Cu>Pb. The amounts of Zn, Cu, and Pb were below maximum permissible limits (MPL) recommended by international standards (FAO, FAO/WHO, and MAFF). Results revealed that estimated daily and weekly intakes of Zn, Cu, and Pb were far below the permissible tolerable daily intake (PTWI) recommended by FAO/WHO. Therefore, consumption of S. commerson in the pre and post-monsoon has no risks for human health in the Oman Sea.
https://jpoll.ut.ac.ir/article_84044_31299a1d820f2c2379c113c0147e6bf5.pdf
2021-10-01
923
932
10.22059/poll.2021.325185.1111
mackerel
Protein
Pollutant
monsoon
Oman Sea
Asma
Esmaeilzade Ashini
asma72.esmaelzadeh@gmail.com
1
Department of Marine Biology, Faculty of Marine Science, Chabahar Maritime University, Chabahar, Iran
AUTHOR
Parvin
Sadeghi
parvin.sadeghi@gmail.com
2
Department of Marine Biology, Faculty of Marine Science, Chabahar Maritime University, Chabahar, Iran
LEAD_AUTHOR
Mohammad Mansoor
Tootooni
m.tootooni@yahoo.com
3
Department of Marine Biology, Faculty of Marine Science, Chabahar Maritime University, Chabahar, Iran
AUTHOR
Ahmed, Q. (2013). Determination of Heavy metals in Indian Mackerel Fishes (Family- Scombridae) from Karachi Coast. Ph.D. thesis. Department of Zoology University of Karachi.
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Sadeghi, E., Mohammadi, M., Sharafi, K. and Bohlouli, S. (2015). Determination and assessment of three heavy metal content (Cd, Pb and Zn) in Scomberomorous commerson fish caught from the Persian Gulf. Bulg. Chem. Commun., 47 (D); 220-223.
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49
ORIGINAL_ARTICLE
Analysis of Water Quality Trends Using the Mann-Kendall Test and Sen’s Estimator of Slope in a Tropical River Basin
Trends in water quality, either increasing or decreasing over the long term, are becoming an essential guide to understanding water quality. This study aims to analyse the trends in water quality in the upstream part of the Bernam River Basin, Malaysia from 1998 to 2018. This study involved the collection of data on water quality from the Department of Environment, Malaysia. Six main parameters of the water quality index (WQI) were chosen, including the dissolved oxygen (DO), biochemical oxygen demand (BOD), chemical oxygen demand (COD), ammoniacal nitrogen (NH3-N), total suspended solids (TSS) and pH. The analysis methods applied are the Mann-Kendall test and Sen’s estimator of slope. The results of the WQI value trend analysis revealed that most stations have decreasing trends. A trend analysis of the parameters found that most stations had increasing trends for the DO, BOD, NH3-N and pH parameters, while decreasing trends for the COD and TSS parameters were observed. An increasing trend indicated that the water quality parameters were getting better, and a decreasing trend indicated the opposite. This study will benefit the parties responsible for planning and monitoring developments to reduce water pollution around the upstream Bernam River Basin. In the upstream of Bernam River Basin, land use changes have occurred rapidly, especially forest areas have been explored for human settlements, agricultural and industrial activities. Thus, the sustainability of the river basin can be maintained and valued by the various parties in the future. The river basin is also important as a domestic water supply for the residents of Selangor and Perak.
https://jpoll.ut.ac.ir/article_84045_7f74f8cc4837ea932e5ba894087948b3.pdf
2021-10-01
933
942
10.22059/poll.2021.325794.1118
Trend Analysis
water pollution
Water quality index
Bernam river basin
Physico-chemical parameters
Mohmadisa
Hashim
mohmadisa@fsk.upsi.edu.my
1
Department of Geography & Environment, Faculty of Human Sciences, Universiti Pendidikan Sultan Idris, 35900 Tanjong Malim, Perak, Malaysia
LEAD_AUTHOR
Nasir
Nayan
nasir@fsk.upsi.edu.my
2
Department of Geography & Environment, Faculty of Human Sciences, Universiti Pendidikan Sultan Idris, 35900 Tanjong Malim, Perak, Malaysia
AUTHOR
Dewi Liesnoor
Setyowati
liesnoor2015@mail.unnes.ac.id
3
Department of Geography, Faculty of Social Science, Universitas Negeri Semarang, Gunungpati, Kota Semarang, 50229 Indonesia
AUTHOR
Zahid Mat
Said
zahid@fsmt.upsi.edu.my
4
Department of Biology, Faculty of Sciences & Mathematics, Universiti Pendidikan Sultan Idris, 35900 Tanjong Malim, Perak, Malaysia
AUTHOR
Hanifah
Mahat
hanifah.mahat@fsk.upsi.edu.my
5
Department of Geography & Environment, Faculty of Human Sciences, Universiti Pendidikan Sultan Idris, 35900 Tanjong Malim, Perak, Malaysia
AUTHOR
Yazid
Saleh
yazid@fsk.upsi.edu.my
6
Department of Geography & Environment, Faculty of Human Sciences, Universiti Pendidikan Sultan Idris, 35900 Tanjong Malim, Perak, Malaysia
AUTHOR
Abdul Rahim, L., Hashim, M., Che Ngah, M. S. Y., Nayan, N. and Saleh, Y. (2014). Seepage water quality: A case study in Ulu Yam and Kuala Kubu Bharu, Selangor. Geografi, 2(1); 86-97.
1
Ahmadi, M., Ravanbakhsh, M., Ahmadi, K. and Ramavandi, B. (2015). Trend analysis of long-term water quality for Zohre River water, Iran. Pollution Research, 34(3); 489–496.
2
Ali, R., Kuriqi, A., Abubaker, S. and Kisi, O. (2019). Long-term trends and seasonality detection of the observed flow in Yangtze River using Mann-Kendall and Sen’s Innovative Trend Method. 1855. Water, 11(9); 1855.
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Ang, K. H. (2015). The quality of water resources in Malaysia: An analysis. Geografia: Malaysian Journal of Society & Space, 11(6); 98–108.
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Antonopoulos, V., Papamichail, D. and Mitsiou, K. (2001). Statistical and trend analysis of water quality and quantity data for the Strymon river in Greece. Hydrol. Earth Syst. Sci., 5(4); 679–691.
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Camara, M., Jamil, N. R. and Abdullah, A. F. B. (2019). Impact of land uses on water quality in Malaysia: A review. Ecol. Process., 8(1); 1–10.
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Cech, T. V. (2005). Principles of water resources: History, development, management, and policy (2nd ed.), John Wiley & Sons, London.
7
Che Ngah, M. S. Y., Reid, I. and Hashim, M. (2012). Rainfall trend analysis using 50 years historical data in newly developed catchment in Peninsular Malaysia. Middle East Journal of Scientific Research, 11(5); 668-673.
8
Faridah, O., Alaa Eldin, M. E. and Ibrahim, M. (2012). Trend analysis of a tropical urban river water quality in Malaysia. J. Environ. Monit., 14(12); 3164–3173.
9
Giri, S. and Qiu, Z. (2016). Understanding the relationship of land uses and water quality in twenty first century: A review. Journal of Environmental Management, 173; 41–48.
10
Irena, N., Noorul Hassan, Z., Sharif Moniruzzaman, S., Nurul Farahen, I. and Lavania, B. (2016). Effectiveness of water quality index for monitoring Malaysian River Water Quality. Pol. J. Environ. Stud., 25(1); 1–9. Ismail, W. R. and Hashim, M. (2014). Changing trends of rainfall and sediment fluxes in the Kinta River catchment, Malaysia. IAHS-AISH Proceedings and Report, 367; 340–345.
11
Ismail, W. R., Bakar, S. & Rahaman, Z. A. (2013). Sediment and nutrient export by water from an agricultural catchment: An analysis of hysteresis patterns in the Upper Relau River, Penang. Geografi, 1(1); 74-101.
12
Izyan Munirah, M. Z., Suhaimi, S. and Norhayati, M. T. (2017). The evaluation of spatial variation of water quality in Sungai Setiu Basin, Terengganu. Sains Malaysiana, 46(9); 1513–1520.
13
Lento, J., Dillon, P. J. and Somers, K. M. (2012). Evaluating long-term trends in littoral benthic macroinvertebrate communities of lakes recovering from acid deposition. Environ. Monit. Assess., 184(12); 7175–7187.
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Luo, P., He, B., Takara, K., Razafindrabe, B. H., Nover, D. and Yamashiki, Y. (2011). Spatiotemporal trend analysis of recent river water quality conditions in Japan. J. Environ. Monit., 13(10); 2819–2829.
15
Luo, P., Kang, S., Apip, Zhou, M., Lyu, J., Aisyah Siti, Binaya, M., Regmi, R. K. and Nover, D. (2019). Water quality trend assessment in Jakarta: A rapidly growing Asian megacity. PloS One, 14(7); 1–17.
16
Mahmoodi, N., Osati, K., Salajegheh, A. and Saravi, M. M. (2021). Trend in river water quality: Tracking the overall impacts of climate change and human activities on water quality in the Dez River Basin. J. Water Health, 19(1); 159-173.
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18
Mohamad Adam Omar, Zullyadini A. Rahaman and Wan Ruslan Ismail. (2018). Sediment and nutrient concentration from different land use and land cover of Bukit Merah Reservoir (BMR) Catchment, Perak, Malaysia. Geografi, 2(2); 52-65.
19
Mohd. Azlan, A. and Sarimah, S. (2002). Impact of development on water quality of Kerian River downstream. In. National Conference in Science, Technology and Social Sciences, 1–10.
20
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21
Mohd Harun, A. (2012). Principles in water analysis for environmental science, Universiti Malaysia Sabah Press, Kota Kinabalu Sabah.
22
Mustapha, A. (2013). Detecting surface water quality trends using Mann-Kendall tests and Sen’s slope estimates. International Journal of Agriculture Innovations and Research, 1; 108–114.
23
Naddafi, K., Honari, H. and Ahmadi, M. (2007). Water quality trend analysis for the Karoon River in Iran. Environ. Monit. Assess., 134; 305–312.
24
Nayan, N., Saleh, Y., Hashim, M., Mahat, H. and See, K. L. (2019). Investigating groundwater quality in the flood prone neighborhood area in Malaysia. Indonesian Journal of Geography, 51(2); 123-130.
25
Nur Hishaam, S., Mohd Khairul Amri, K., Ahmad Dasuki, M., Muhammad Azizi, A., Fazureen, A., Ismail Zainal, A. and Norsyuhada, H. (2015). Trend analysis of Pahang River using non-parametric analysis: Mann Kendall’s trend test. Malaysian Journal of Analytical Sciences, 19(6); 1327–1334.
26
Nurain, M. and Ang, K. H. (2015). Water quality of UTM River: A preliminary assessment based on six parameters of Water Quality Index. Geografia Malaysian Journal of Society and Space, 11(1); 107–115.
27
Ratnaningsih, D., Nasution, E. L., Wardhani, N. T., Pitalokasari, O. D. and Fauzi, R. (2019). Water pollution trends in Ciliwung River based on water quality parameter. IOP Conf. Ser.: Earth Environ. Sci., 407 (2019) 012006.
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Saeed, T. U. and Attaullah, H. (2014). Impact of extreme floods on groundwater quality (in Pakistan). British J. of Environment & Climate Change, 4(1); 133–151.
29
Salam, M. A., Kabir, M. M., Yee, L. F., A/l Eh Rak, A. and Khan, M.S. (2019). Water quality assessment of Perak River, Malaysia. Pollution, 5(3); 637-648.
30
Spellman, F. R. (2008). The science of water (2nd ed.), CRC Press, New York.
31
Suhaimi, S., Norhayati, M. T., Lee, C. Y. and Siti Rohayu, A. R. (2006). Impact of monsoon on water quality in Besut River Basin, Terengganu. Malaysia Journal of Analytical Sciences, 10(1); 143–148.
32
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Tabari, H., Marofi, S. and Ahmadi, M. (2011). Long-term variations of water quality parameters in the Maroon River, Iran. Environ. Monit. Assess., 177(1–4); 273–287.
34
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35
Zhai, X., Xia, J. and Zhang, Y. (2014). Water quality variation in the highly disturbed Huai River Basin, China from 1994 to 2005 by multi-statistical analyses. Science of the Total Environment, 496; 594–606.
36
ORIGINAL_ARTICLE
Use of Reverse Electrodialysis to Harvest Salinity Gradient Energy from Oilfield Produced Water
Two lab-scale electrodialysis (RED) stacks with different intermembrane spacing were used in this study. Each stack consists of two membrane pairs. Thick intermembrane spacing stack was made of four identical plexiglass sections, with outer dimensions 5 cm * 5 cm * 1.5 cm and an inner cross-section of 3 cm diameter each to construct two diluted solution compartments and two concentrated solution compartments. For the thin intermembrane spacing configuration, four rubber spacers with a thickness of 1 mm and an inner opening of 3 cm each were used instead of these sections. Two copper sheets were used as anode and cathode electrodes. Different solutions with NaCl concentrations of 15,000, 30,000 and 200,000 mg/l were used as a concentrated solution and different solutions with relatively low NaCl concentrations of 25, 1000 and 3600 mg/l were used as a diluted solution. A 30,000 mg/l NaCl solution was used as a diluted solution when the concentrated stream was with NaCl concentration of 200,000 mg/l. The electrode solution was of 15,000 mg/l (~0.25 M) NaCl and 8,000 mg/l (~0.05 M) CuSO4.5H2O. The results of this study confirmed the validity of using RED technology to harvest energy from salinity gradient using saline and freshwater available abundantly particularly in Iraq. An experiment on a synthetic hypersaline oil field co-produced water as a concentrated stream and seawater as a diluted stream showed that the system performance is reproducible and stable. A maximum power density of 0.029 W/m2 could be harvested.
https://jpoll.ut.ac.ir/article_84046_45e194ee05978d3cd520da77ca17629a.pdf
2021-10-01
943
957
10.22059/poll.2021.326042.1124
Electrode
Ion exchange membrane
Anode
Cathode
Talib
Abbas
talibrshd@yahoo.com
1
Environment and Water Directorate, Ministry of Science and Technology, Baghdad, Iraq
LEAD_AUTHOR
Mustafa
Al-Furaiji
m.h.o.alfuraiji@alumnus.utwente.nl
2
Environment and Water Directorate, Ministry of Science and Technology, Baghdad, Iraq
AUTHOR
Al-Furaiji, M., Kadhom, M., Kalash, K., Waisi, B. and Albayati, N. (2020). Preparation of thin-film composite membranes supported with electrospun nanofibers for desalination by forward osmosis. Drink. Water Eng. Sci. 13, 51–57. https://doi.org/10.5194/dwes-13-51-2020
1
Al-Furaiji, M.H.O., Arena, J.T., Chowdhury, M., Benes, N., Nijmeijer, A. and McCutcheon, J.R. (2018). Use of forward osmosis in treatment of hyper-saline water. Desalin. Water Treat. 133, 1–9. https://doi.org/10.5004/dwt.2018.22851
2
Al-Rubaie, M.S., Dixon, M.A. and Abbas, T.R. (2015). Use of flocculated magnetic separation technology to treat Iraqi oilfield co-produced water for injection purpose. Desalin. Water Treat. 53, 2086–2091. https://doi.org/10.1080/19443994.2013.860400
3
Alalwan, H.A. and Alminshid, A.H. (2021). CO2 capturing methods: Chemical looping combustion (CLC) as a promising technique. Sci. Total Environ. 788, 147850. https://doi.org/10.1016/j.scitotenv.2021.147850
4
Alalwan, H.A., Augustine, L.J., Hudson, B.G., Abeysinghe, J.P., Gillan, E.G., Mason, S.E., Grassian, V.H. and Cwiertny, D.M. (2021). Linking Solid-State Reduction Mechanisms to Size-Dependent Reactivity of Metal Oxide Oxygen Carriers for Chemical Looping Combustion. ACS Appl. Energy Mater. 4, 1163–1172. https://doi.org/10.1021/acsaem.0c02029
5
Alminshid, A.H., Abbas, M.N., Alalwan, H.A., Sultan, A.J. and Kadhom, M.A. (2021). Aldol condensation reaction of acetone on MgO nanoparticles surface: An in-situ drift investigation. Mol. Catal. 501, 111333. https://doi.org/10.1016/j.mcat.2020.111333
6
Avci, A.H., Tufa, R.A., Fontananova, E., Di Profio, G. and Curcio, E. (2018). Reverse Electrodialysis for energy production from natural river water and seawater. Energy 165, 512–521. https://doi.org/10.1016/j.energy.2018.09.111
7
Bodner, E.J., Saakes, M., Sleutels, T., Buisman, C.J.N. and Hamelers, H.V.M. (2019). The RED Fouling Monitor: A novel tool for fouling analysis. J. Memb. Sci. 570–571, 294–302. https://doi.org/10.1016/j.memsci.2018.10.059
8
Castaño, S.V. (2016). Energy generation from salinity gradients through Reverse Electrodialysis and Capacitive Reverse Electrodialysis Energy generation from salinity gradients through Reverse Electrodialysis and Capacitive Reverse Electrodialysis 103.
9
Coleman Gilstrap, M. (2013). Renewable electricity generation from salinity gradients using reverse electrodialysis.
10
D’Angelo, A., Tedesco, M., Cipollina, A., Galia, A., Micale, G. and Scialdone, O. (2017). Reverse electrodialysis performed at pilot plant scale: Evaluation of redox processes and simultaneous generation of electric energy and treatment of wastewater. Water Res. 125, 123–131. https://doi.org/10.1016/j.watres.2017.08.008
11
Hassan, Q.H., Shaker Abdul Ridha, G., Hafedh, K.A.H. and Alalwan, H.A. (2021). The impact of Methanol-Diesel compound on the performance of a Four-Stroke CI engine. Mater. Today Proc. 42, 1993–1999. https://doi.org/10.1016/j.matpr.2020.12.247
12
Hu, J., Xu, S., Wu, X., Wu, D., Jin, D., Wang, P. and Leng, Q. (2018). Theoretical simulation and evaluation for the performance of the hybrid multi-effect distillation—reverse electrodialysis power generation system. Desalination 443, 172–183. https://doi.org/10.1016/j.desal.2018.06.001
13
Huang, Y., Mei, Y., Xiong, S., Tan, S.C., Tang, C.Y. and Hui, S.Y. (2018). Reverse Electrodialysis Energy Harvesting System Using High-Gain Step-Up DC/DC Converter. IEEE Trans. Sustain. Energy 9, 1578–1587. https://doi.org/10.1109/TSTE.2018.2797320
14
Kim, H.-K., Lee, M.-S., Lee, S.-Y., Choi, Y.-W., Jeong, N.-J. and Kim, C.-S. (2015). High power density of reverse electrodialysis with pore-filling ion exchange membranes and a high-open-area spacer. J. Mater. Chem. A 3, 16302–16306. https://doi.org/10.1039/C5TA03571F
15
Loza, S.A., Korzhov, A.N., Loza, N. V. and Romanyuk, N.A. (2020). Energy generation by reverse electrodialysis. IOP Conf. Ser. Mater. Sci. Eng. 791, 012057. https://doi.org/10.1088/1757-899X/791/1/012057
16
Mei, Y. and Tang, C.Y. (2018). Recent developments and future perspectives of reverse electrodialysis technology: A review. Desalination 425, 156–174. https://doi.org/10.1016/j.desal.2017.10.021
17
Tedesco, M., Cipollina, A., Tamburini, A., van Baak, W. and Micale, G. (2012). Modelling the Reverse ElectroDialysis process with seawater and concentrated brines. Desalin. Water Treat. 49, 404–424. https://doi.org/10.1080/19443994.2012.699355
18
Tedesco, M., Hamelers, H.V.M. and Biesheuvel, P.M. (2018). Nernst-Planck transport theory for (reverse) electrodialysis: III. Optimal membrane thickness for enhanced process performance. J. Memb. Sci. 565, 480–487. https://doi.org/10.1016/j.memsci.2018.07.090
19
Tedesco, M., Mazzola, P., Tamburini, A., Micale, G., Bogle, I.D.L., Papapetrou, M. and Cipollina, A. (2015). Analysis and simulation of scale-up potentials in reverse electrodialysis. Desalin. Water Treat. 55, 3391–3403. https://doi.org/10.1080/19443994.2014.947781
20
Tufa, R.A., Pawlowski, S., Veerman, J., Bouzek, K., Fontananova, E., di Profio, G., Velizarov, S., Goulão Crespo, J., Nijmeijer, K. and Curcio, E. (2018). Progress and prospects in reverse electrodialysis for salinity gradient energy conversion and storage. Appl. Energy 225, 290–331. https://doi.org/10.1016/j.apenergy.2018.04.111
21
Veerman, J., Saakes, M., Metz, S.J. and Harmsen, G.J. (2010). Reverse electrodialysis: evaluation of suitable electrode systems. J. Appl. Electrochem. 40, 1461–1474. https://doi.org/10.1007/s10800-010-0124-8
22
Vermaas, D.A., Guler, E., Saakes, M. and Nijmeijer, K. (2012). Theoretical power density from salinity gradients using reverse electrodialysis. Energy Procedia 20, 170–184. https://doi.org/10.1016/j.egypro.2012.03.018
23
ORIGINAL_ARTICLE
Removal of Thymol Blue from Aqueous Solution by Natural and Modified Bentonite: Comparative Analysis of ANN and ANFIS Models for the Prediction of Removal Percentage
In this study natural bentonite (NB) and acid-thermal co-modified bentonite (MB) were utilized as adsorbents for the removal of Thymol Blue (TB) from aqueous solution. The batch adsorption experiments were conducted under different experimental conditions. The artificial neural network (ANN) and adaptive neuro fuzzy inference systems (ANFIS) were applied to estimate removal percentage (%) of TB. Mean squared error (MSE), root mean square error (RMSE) and coefficient of determination (R2) values were used to evaluate the results. In addition, the experimental data were fitted isotherm models (Langmuir, Freundlich and Temkin) and kinetic models (pseudo first order (PFO), pseudo second order (PSO) and intra-particle diffusion (IPD)). The adsorption of TB on both the NB and MB followed well the PSO kinetic model, and was best suited Langmuir isotherm model. When the temperature was increased from 298 K to 323 K for 20 mg/L of TB initial concentration, the removal percentage of TB onto the NB and MB increased from 74.91% to 84.07% and 81.19% to 93.12%, respectively. This results were confirmed by the positive ΔH° values indicated that the removal process was endothermic for both the NB and MB. The maximum adsorption capacity was found as 48.7805 mg/g and 117.6471 mg/g for the NB and MB, respectively (at 323 K). As a result, with high surface area and adsorption capacity, the MB is a great candidate for TB dye removal from wastewater, and the ANFIS model is better than the ANN model at estimating the removal percentage of the dye.
https://jpoll.ut.ac.ir/article_84111_e50c788d81c14cfeafc56df02bf8f1af.pdf
2021-10-01
959
980
10.22059/poll.2021.326041.1125
Adsorption
Bentonite
Thymol Blue
Artificial Neural Networks
ANFIS
Hülya
Koyuncu
hulya.koyuncu@btu.edu.tr
1
Department of Chemical Engineering, Faculty of Engineering and Natural Sciences, University of Bursa Technical, P.O.Box 16310, Bursa, Turkey
LEAD_AUTHOR
Adnan
Aldemir
adnanaldemir@yyu.edu.tr
2
Department of Chemical Engineering, Faculty of Engineering, University of Van Yüzüncü Yıl, P.O.Box 65080, Van, Turkey
AUTHOR
Ali Rıza
Kul
alirizakul@yyu.edu.tr
3
Department of Chemistry, Faculty of Science, University of Van Yüzüncü Yıl, P.O.Box 65080, Van, Turkey
AUTHOR
Murat
Canayaz
mcanayaz@yyu.edu.tr
4
Department of Computer Engineering, Faculty of Engineering, University of Van Yüzüncü Yıl, P.O.Box 65080, Van, Turkey
AUTHOR
Adeyemo, A.A., Adeoye I.O. and Bello, O.S. (2017). Adsorption of dyes using different types of clay: a review. Appl. Water. Sci. 7, 543–568.
1
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40
ORIGINAL_ARTICLE
Investigation of Heavy Metal Traces during Drilling Operations in the Bibi Hakimeh Oil Field, Iran
Drilling operations release considerable amounts of drilling fluids that contain pollutants such as heavy metals and hydrocarbons. By means of the ICP-OES device, the concentration of metals in the drilling mud deposited in the accumulation pools (around the drill rigs), the drilling mud used in the well (initial, input, and output mud), the soil around the drilling rig, and the control sample can be determined. Comparison of metal accumulation volume with current standards (upper crust and the region’s soil) indicates that the initial drilling mud contains As, Cd, Mo, Cu, and Ag metals. Also, the outflow and associated cuttings are contaminated with Sb, showing a geological formation origin for this metal. In case of Pb, Ba, Cr, and Mn, the level of contamination is in a medium range wherein the source of the contamination is recycled mud and drilling rocks in the previous phases. Contamination of other metals is evaluated in the low range. Geo-accumulation index (Igeo), Enrichment Coefficient (EF), and Contamination Factor (CF) are used to determine the level of pollution. Results show that As, Pb, Ba, Mn, Mo, Cd, Co, Cu, and Zn have caused a lot of pollution in the area and their amounts should be controlled.
https://jpoll.ut.ac.ir/article_84112_08baa07f9fda8222904986c8ab384f22.pdf
2021-10-01
981
992
10.22059/poll.2021.321954.1062
Geo-accumulation index
mud waste
Contamination Factor
Enrichment Coefficient
Shahram
Baikpour
baikpour2004_rsgsi@yahoo.com
1
Medical Geology Research Centre, Science and Research Branch, Islamic Azad University, P.O. Box 14515/775, Tehran, Iran
LEAD_AUTHOR
Mohammad Javad
Noorani
javad.noorani@gmail.com
2
Department of Natural Resources and Environment, Science and Research Branch, Islamic Azad University, P.O. Box 14515/775, Tehran, Iran
AUTHOR
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34
ORIGINAL_ARTICLE
Production of Eco-Friendly Geopolymer Concrete by using Waste Wood Ash for a Sustainable Environment
Climate change could be exacerbated by waste disposal problems, which destroy the ecosystem. Utilizing waste byproducts in creating eco-friendlier geopolymer concrete was hypothesised to be suitable and sustainable to overcome the negative impacts of wastes. The researchers had missed out on developing an alternate binder due to increasing demand for fly ash, high alkaline activators, and higher curing temperatures. This research used waste wood ash that is readily accessible in local restaurants and has an inherent potassium constituent. It has decided to replace the fly ash with waste wood ash obtained through nearby restaurants at intervals of 10 percent. The fresh and mechanical features have been discovered over long curing periods to assess the impact of waste wood ash. SEM and XRD have been used for characterising the microstructure of selected geopolymer mixes. In terms of setting properties and all mechanical parameters, replacing 30 percent waste wood ash produced enhanced results. The optimised mix could be used in geopolymer to replace fly ash and reduce the cost of alkaline activators while also reducing ecosystem damage.
https://jpoll.ut.ac.ir/article_84062_a6315c7834c13376359ca8e2e8ec2117.pdf
2021-10-01
993
1006
10.22059/poll.2021.320857.1039
Wood waste ash
Low calcium
Eco-friendly geopolymer concrete
SEM
XRD
Kadarkarai
Arunkumar
arunapcivil@gmail.com
1
School of Environmental and Construction Technology, Kalasalingam Academy of Research and Education, Krishnan kovil, Tamil Nadu, India
LEAD_AUTHOR
Muthiah
Muthukannan
civilkannan@gmail.com
2
School of Environmental and Construction Technology, Kalasalingam Academy of Research and Education, Krishnan kovil, Tamil Nadu, India
AUTHOR
Arunachalam
Suresh Kumar
sureshalmighty@gmail.com
3
School of Environmental and Construction Technology, Kalasalingam Academy of Research and Education, Krishnan kovil, Tamil Nadu, India
AUTHOR
Arunasankar
Chithambar Ganesh
chithambarmailid@gmail.com
4
Department of Civil Engineering, Sree Vidya Nikethan Engineering College, Tripati, India
AUTHOR
Rangaswamy
Kanniga Devi
rkannigadevi@gmail.com
5
School of Computer Science and Engineering, Kalasalingam Academy of Research and Education, Krishnan kovil, Tamil Nadu, India
AUTHOR
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