ORIGINAL_ARTICLE
Effect of biochar on nitrogen retention in soil under corn plant inoculated with arbuscular mycorrhizal fungi
Maintaining the levels of nitrogen in agricultural fields to ensure crop yield performance is challenging due to the complex dynamics of nitrogen transformation in soil. Nitrogen is mainly taken up by plant roots in the form of nitrate, but it is considered as an environmental pollutant that threatens human and animal health. Therefore, it is necessary to use adsorbent compounds to retain nitrate in the soil. The effectiveness of two types of biochar produced from rice husk (Br) and populous wood (Bp) and two arbuscular mycorrhizal fungi, namely Funneliformis intraradices (Mi) and Funneliformis versiforme (Mv), on nitrate leaching in soil was evaluated. The soil columns planted with corn were filled with an artificial sandy clay loam soil fertigated with urea fertilizer under glasshouse conditions . After nine weeks of growing the plants, a pulse of nitrogen (0.48 g urea per core) was added to the columns. One week after the addition of urea, the shoots of the plants were removed, and the columns immediately flushed with 500 ml of deionized water to leach the soil nitrogen from the columns. The results showed that the shoots' dry-weight increased significantly (p≤ 0.05) in almost all the treatments with the highest in the BrMi treatment when compared to the control (C). The nitrate concentration in the leachate decreased 79% (from 23.2 mg/l in C treatment to 4.2 mg/l in Bp treatment), but the nitrate concentration in the soil solution increased up to 6.7-fold (Bp was the highest), which suggested a high N retention by the biochars used. It was concluded that the application of biochar and mycorrhizal fungi could reduce nitrogen loss through this artificial sandy clay loam soil and may have some implications in environment conservation.
https://aet.irost.ir/article_923_cef51d7d4f00b96e41db57a3fcaeb543.pdf
2019-07-01
133
140
10.22104/aet.2020.3874.1191
Biochar
Fertilizer
Nitrate leaching
Mycorrhizae
Ali
Abbaspour
abbaspour2008@gmail.com
1
Department of soil and water, Faculty of Agriculture, Shahrood University of Technology
LEAD_AUTHOR
Hamid Reza
Asghari
hamidasghari@gmail.com
2
Department of Agronomy, Faculty of Agriculture, Shahrood University of Technology
AUTHOR
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1
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5
[6] Shi, K., Qiu, Y., Li, B., Stenstrom, M.K. (2016). Effectiveness and potential of straw-and wood-based biochars for adsorption of imidazolium-type ionic liquids. Ecotoxicology and environmental safety, 130, 155–162.
6
[7] El-Deen, G.E.S. (2016). Sorption of Cu (II), Zn (II) and Ni (II) from aqueous solution using activated carbon prepared from olive stone waste. Advances in environmental technology, 3, 147–161.
7
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8
[9] Bogusz, A. Oleszczuk, P. (2020). Effect of biochar addition to sewage sludge on cadmium, copper and lead speciation in sewage sludge-amended soil. Chemosphere, 239, 124719.
9
[10] Beesley, L., Moreno-Jiménez, E., Gomez-Eyles, J.L. (2010). Effects of biochar and greenwaste compost amendments on mobility, bioavailability and toxicity of inorganic and organic contaminants in a multi-element polluted soil. Environmental pollution, 158(6), 2282–2287.
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[11] Heaney, N., Ukpong, E., Lin, C. (2019). Low-molecular-weight organic acids enable biochar to immobilize nitrate. Chemosphere, 124872.
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[12] Zheng, H., Wang, Z., Deng, X., Herbert, S., Xing, B. (2013). Impacts of adding biochar on nitrogen retention and bioavailability in agricultural soil. Geoderma, 206, 32–39.
12
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[14] Rafique, M., Ortas, I., Rizwan, M., Chaudhary, H.J., Gurmani, A.R., & Munis, M.F.H. (2020). Residual effects of biochar and phosphorus on growth and nutrient accumulation by maize (Zea mays L.) amended with microbes in texturally different soils. Chemosphere, 238, 124710.
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[15] Kasozi, G.N., Zimmerman, A.R., Nkedi-Kizza, P., Gao, B. (2010). Catechol and humic acid sorption onto a range of laboratory-produced black carbons (biochars). Environmental science and technology, 44(16), 6189–6195.
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[17] Sciubba, L., Cavani, L., Marzadori, C., Ciavatta, C. (2013). Effect of biosolids from municipal sewage sludge composted with rice husk on soil functionality. Biology and fertility of soils, 49(5), 597–608.
17
[18] Parvage, M.M., Ulén, B., Eriksson, J., Strock, J., Kirchmann, H. (2013). Phosphorus availability in soils amended with wheat residue char. Biology and fertility of soils, 49(2), 245–250.
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[20] Asghari, H.R. Cavagnaro, T.R. (2012). Arbuscular mycorrhizas reduce nitrogen loss via leaching. PloS one, 7(1), e29825.
20
[21] Asghari, H.R. Cavagnaro, T.R. (2011). Arbuscular mycorrhizas enhance plant interception of leached nutrients. Functional plant biology, 38(3), 219–226.
21
[22] Asghari, H.R., Chittleborough, D.J., Smith, F.A., & Smith, S.E. (2005). Influence of arbuscular mycorrhizal (AM) symbiosis on phosphorus leaching through soil cores. Plant and soil, 275(1–2), 181–193.
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[23] Fiol, N. Villaescusa, I. (2009). Determination of sorbent point zero charge: usefulness in sorption studies. Environmental chemistry letters, 7(1), 79–84.
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[27] Singh, B., Macdonald, L.M., Kookana, R.S., van Zwieten, L., Butler, G., Joseph, S., et al. (2014). Opportunities and constraints for biochar technology in Australian agriculture: looking beyond carbon sequestration. Soil research, 52(8), 739–750.
27
[28] Dempster, D.N., Jones, D.L., Murphy, D. V (2012). Organic nitrogen mineralisation in two contrasting agro-ecosystems is unchanged by biochar addition. Soil biology and biochemistry, 48, 47–50.
28
[29] Van Zwieten, L., Kimber, S., Morris, S., Chan, K.Y., Downie, A., Rust, J., et al. (2010). Effects of biochar from slow pyrolysis of papermill waste on agronomic performance and soil fertility. Plant and soil, 327, (1–2), 235–246.
29
[30] Robertson, G.P. Groffman, P.M. 2007. Nitrogen transformations. in: Paul, E. D. (Ed), Soil microbiology, ecology and biochemistry. Elsevier, pp. 341–364.
30
[31] Marcos, M.S., Bertiller, M.B., Cisneros, H.S., & Olivera, N.L. (2016). Nitrification and ammonia-oxidizing bacteria shift in response to soil moisture and plant litter quality in arid soils from the Patagonian Monte. Pedobiologia, 59(1–2), 1–10.
31
[32] Yuan, F., Ran, W., Shen, Q., Wang, D. (2005). Characterization of nitrifying bacteria communities of soils from different ecological regions of China by molecular and conventional methods. Biology and fertility of soils, 41(1), 22–27.
32
[33] Amonette, J.E. Joseph, S. 2012. Characteristics of biochar: microchemical properties. in: Lehman, J. and Joseph, S. (Eds). Biochar for environmental management. Routledge, pp. 65–84.
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[34] Uchimiya, M., Lima, I.M., Klasson, K.T., Wartelle, L.H. (2010). Contaminant immobilization and nutrient release by biochar soil amendment: roles of natural organic matter. Chemosphere, 80(8), 935–940.
34
[35] Yang, F., Cao, X., Gao, B., Zhao, L., Li, F. (2015). Short-term effects of rice straw biochar on sorption, emission, and transformation of soil NH4+-N. Environmental Science and pollution research, 22(12), 9184–9192.
35
[36] Wang, Z., Zong, H., Zheng, H., Liu, G., Chen, L., Xing, B. (2015). Reduced nitrification and abundance of ammonia-oxidizing bacteria in acidic soil amended with biochar. Chemosphere, 138, 576–583.
36
[37] Berglund, L.M., DeLuca, T.H., Zackrisson, O. (2004). Activated carbon amendments to soil alters nitrification rates in Scots pine forests. Soil biology and biochemistry, 36(12), 2067–2073.
37
[38] Malekbala, M.R., Hosseini, S., Yazdi, S.K., Soltani, S.M., Malekbala, M.R. (2012). The study of the potential capability of sugar beet pulp on the removal efficiency of two cationic dyes. Chemical engineering research and design, 90(5), 704–712.
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[39] Černohlávková, J., Jarkovský, J., Nešporová, M., Hofman, J. (2009). Variability of soil microbial properties: effects of sampling, handling and storage. Ecotoxicology and environmental safety, 72(8), 2102–2108.
39
[40] Cavagnaro, T.R., Smith, F.A., Smith, S.E., Jakobsen, I. (2005). Functional diversity in arbuscular mycorrhizas: exploitation of soil patches with different phosphate enrichment differs among fungal species. Plant, cell and environment, 28(5), 642–650.
40
[41] Corkidi, L., Merhaut, D.J., Allen, E.B., Downer, J., Bohn, J., Evans, M. (2011). Effects of mycorrhizal colonization on nitrogen and phosphorus leaching from nursery containers. HortScience, 46(11), 1472–1479.
41
ORIGINAL_ARTICLE
Mass Transfer Study in Brine Water Treatment by Forward Osmosis Process
Forward osmosis (FO) is an energy-saving separation process that can be used in desalination applications. This work investigated the effect of mass transfer phenomenon on the FO desalination process. For this purpose, the water flux was studied through a bench scale system using a flat sheet FO membrane and feeds with various salinity. Then, the mass transfer resistances, which appear in the form of concentration polarization (CP) for the FO process, were evaluated qualitatively and quantitatively, using the collected experimental data and by employing a mathematical model. The results indicated that the increase in feed salinity led to a decrease in water flux due to the counteracted part of the draw solution osmotic pressure, thus leading to a lower effective osmotic pressure and driving force. Also, according to the results, there was a significant difference between the theoretical and experimental fluxes, indicating the influence of the mass transfer effects on the osmotic pressure drop. The modeling results showed that the internal concentration polarization (ICP) still held more contribution to the osmotic pressure loss. Furthermore, it was observed that as the feed solution concentration increased, both the ICP and dilutive external concentration polarization (DECP) decreased, whereas the concentrative ECP (CECP) intensified. Therefore, increasing the CECP led to a significant reduction in the effective osmotic pressure. In addition, increasing the draw solution concentration was accompanied by a much more severe ICP that limited the enhancement of effective flux.
https://aet.irost.ir/article_932_c8d28dec4667f27c7ebf268a3372dbeb.pdf
2019-07-01
141
148
10.22104/aet.2020.3946.1195
Forward Osmosis (FO)
Brine wastewater
concentration polarization
Mass transfer
Razieh
Ahmadizadeh
razieh.ahmadizadeh@gmail.com
1
Department of Chemical Technologies, Iranian Research Organization for Science and Technology (IROST), Tehran, Iran
AUTHOR
Soheila
Shokrollahzadeh
shokrollahzadeh@yahoo.com
2
Department of Chemical Technologies, Iranian Research Organization for Science and Technology (IROST), Tehran, Iran
AUTHOR
Seyed Mehdi
Latifi
sm.latifi@yahoo.com
3
Department of Chemical Technologies, Iranian Research Organization for Science and Technology (IROST), Tehran, Iran
LEAD_AUTHOR
[1] Qin, J. J., Lay, W. C. L., Kekre, K. A. (2012). Recent developments and future challenges of forward osmosis for desalination: a review. Desalination and water treatment, 39(1-3), 123-136.
1
[2] Hey, T., Bajraktari, N., Davidsson, Å, Vogel, J., Madsen, H. T., Hélix-Nielsen, C., Jönsson, K. (2018). Evaluation of direct membrane filtration and direct forward osmosis as concepts for compact and energy-positive municipal wastewater treatment. Environmental technology, 39(3), 264-276.
2
[3] Kim, J., Jeong, K., Park, M. J., Shon, H. K., Kim, J. H. (2015). Recent advances in osmotic energy generation via pressure-retarded osmosis (PRO): a review. Energies, 8(10), 11821-11845.
3
[4] Hasanoğlu, A., Gül, K. (2016). Concentration of skim milk and dairy products by forward osmosis. Journal of the Turkish Chemical Society Section B: Chemical engineering, 1(1), 149-160.
4
[5] Johnson, D. J., Suwaileh, W. A., Mohammed, A. W., Hilal, N. (2018). Osmotic's potential: An overview of draw solutes for forward osmosis. Desalination, 434, 100-120. pressure retarded osmosis (PRO). Separation and purification technology, 156, 856-860.
5
[6] J McCutcheon, J. R., McGinnis, R. L., Elimelech, M. (2006). Desalination by ammonia–carbon dioxide forward osmosis: influence of draw and feed solution concentrations on process performance. Journal of membrane science, 278(1-2), 114-123.
6
[7] Cath, T. Y., Childress, A. E., Elimelech, M. (2006). Forward osmosis: principles, applications, and recent developments. Journal of membrane science, 281(1-2), 70-87.
7
[8] Qasim, M., Darwish, N. A., Sarp, S., Hilal, N. (2015). Water desalination by forward (direct) osmosis phenomenon: A comprehensive review. Desalination, 374, 47-69.
8
[9] Johnson, D. J., Suwaileh, W. A., Mohammed, A. W., Hilal, N. (2018). Osmotic's potential: An overview of draw solutes for forward osmosis. Desalination, 434, 100-120
9
[10] Akther, N., Sodiq, A., Giwa, A., Daer, S., Arafat, H. A., Hasan, S. W. (2015). Recent advancements in forward osmosis desalination: a review. Chemical engineering journal, 281, 502-522.
10
[11] Tow, E. W., Warsinger, D. M., Trueworthy, A. M., Swaminathan, J., Thiel, G. P., Zubair, S. M., Myerson, A. S. (2018). Comparison of fouling propensity between reverse osmosis, forward osmosis, and membrane distillation. Journal of membrane science, 556, 352-364.
11
[12] Li, L., Liu, X. P., Li, H. Q. (2017). A review of forward osmosis membrane fouling: Types, research methods and future prospects. Environmental technology reviews, 6(1), 26-46.
12
[13] Linares, R. V., Li, Z., Yangali-Quintanilla, V., Ghaffour, N., Amy, G., Leiknes, T., Vrouwenvelder, J. S. (2016). Life cycle cost of a hybrid forward osmosis–low pressure reverse osmosis system for seawater desalination and wastewater recovery. Water research, 88, 225-234.
13
[14] Phuntsho, S., Hong, S., Elimelech, M., Shon, H. K. (2014). Osmotic equilibrium in the forward osmosis process: Modelling, experiments and implications for process performance. Journal of membrane science, 453, 240-252.
14
[15] Tan, C. H., Ng, H. Y. (2008). Modified models to predict flux behavior in forward osmosis in consideration of external and internal concentration polarizations. Journal of membrane science, 324(1-2), 209-219.
15
[16] McCutcheon, J. R., Elimelech, M. (2007). Modeling water flux in forward osmosis: implications for improved membrane design. AIChE journal, 53(7), 1736-1744.
16
[17] Phillip, W. A., Yong, J. S., & Elimelech, M. (2010). Reverse draw solute permeation in forward osmosis: modeling and experiments. Environmental science and technology, 44(13), 5170-5176.
17
[18] Bae, C., Park, K., Heo, H., Yang, D. R. (2017). Quantitative estimation of internal concentration polarization in a spiral wound forward osmosis membrane module compared to a flat sheet membrane module. Korean journal of chemical engineering, 34(3), 844-853.
18
[19] Loeb, S., Titelman, L., Korngold, E., Freiman, J. (1997). Effect of porous support fabric on osmosis through a Loeb-Sourirajan type asymmetric membrane. Journal of membrane science, 129(2), 243-249.
19
[20] Qin, J. J., Chen, S., Oo, M. H., Kekre, K. A., Cornelissen, E. R., Ruiken, C. J. (2010). Experimental studies and modeling on concentration polarization in forward osmosis. Water science and technology, 61(11), 2897-2904.
20
[21] Suh, C., Lee, S. (2013). Modeling reverse draw solute flux in forward osmosis with external concentration polarization in both sides of the draw and feed solution. Journal of membrane science, 427, 365-374.
21
[22] Wang, Y., Zhang, M., Liu, Y., Xiao, Q., Xu, S. (2016). Quantitative evaluation of concentration polarization under different operating conditions for forward osmosis process. Desalination, 398, 106-113.
22
[23] Helfer, F., Lemckert, C., Anissimov, Y. G. (2014). Osmotic power with pressure retarded osmosis: theory, performance and trends–a review. Journal of membrane science, 453, 337-358.
23
[24] Ortega-Bravo, J. C., Ruiz-Filippi, G., Donoso-Bravo, A., Reyes-Caniupán, I. E., Jeison, D. (2016). Forward osmosis: Evaluation thin-film-composite membrane for municipal sewage concentration. Chemical engineering journal, 306, 531-537.
24
[25] Phuntsho, S., Shon, H. K., Hong, S., Lee, S., Vigneswaran, S. (2011). A novel low energy fertilizer driven forward osmosis desalination for direct fertigation: evaluating the performance of fertilizer draw solutions. Journal of membrane science, 375(1-2), 172-181.
25
[26] Bui, N. N., Arena, J. T., McCutcheon, J. R. (2015). Proper accounting of mass transfer resistances in forward osmosis: Improving the accuracy of model predictions of structural parameter. Journal of membrane science, 492, 289-302.
26
ORIGINAL_ARTICLE
Toxicity of zero-valent iron nanoparticles and its fate in Zea mays
Application of nanotechnology has gained remarkable interest in recent years and environmental exposure to nanomaterials is becoming inevitable. Therefore, nanotoxicity problem is gaining more attention. Zero-valent iron nano particles (nZVI) are being used widely for different purposes such as environmental remediation. Excessive amounts of nanomaterials may pose inhibitory effects on growth of plants cultivated in nZVI-affected soils which has been addressed in this research. Moreover, fate of nZVI in plants was investigated in the present study. Plant seeds were exposed to different concentrations of nZVI i.e. 0, 100, 250, 500, 800 and 1000 mg/kg. Z. mays was selected as the model plant in this study and found to be a tolerant plant species in presence of low to moderate levels of nZVI in soil. However, addition of higher doses of nZVI reduced seedling emergence and biomass establishment. Results indicated that the total Fe concentrations in Z. mays treated with nZVI increased compared to the control. Considerably higher accumulation of Fe in roots of Z. mays compared to the shoots in all treatments was found. Results indicated that the total Fe contents in Z. mays treated with nZVI were higher than those in control, with the highest Fe accumulation capacity of 24666.2 µg per pot which was obtained in soil received 500 mg/kg nZVI. Overally, toxic effects of higher doses of nZVI on plants were observed in this study. Intelligent use of nZVI for environmental purposes such as applying low to moderate levels of nZVI in soil remediation activities could remarkably prevent their adverse impacts on plant species, promote plant phytoextraction capability, and reduce nZV emission in the environment.
https://aet.irost.ir/article_934_915453b7bd36b5a63e41e61a2dfa68f4.pdf
2019-07-01
149
156
10.22104/aet.2020.4181.1208
Zero-valent iron nanoparticles
toxicity
Z. mays
plant growth
phytoextraction
Ali
Daryabeigi Zand
adzand@ut.ac.ir
1
School of Environment, College of Engineering, University of Tehran, Tehran, Iran.
LEAD_AUTHOR
[1] Dutschk, V., Karapantsios, T., Liggieri, L., McMillan, N., Miller, R., Starov, V. (2014). Smart and green interfaces: from single bubbles/drops to industrial environmental and biomedical applications. Advances in colloid and interface science, 209, 109-126.
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[2] Aslani, F., Bagheri, S., Muhd Julkapli, N., Juraimi, A. S., Hashemi, F. S. G., Baghdadi, A. (2014). Effects of engineered nanomaterials on plants growth: an overview. The scientific world journal, 1-28.
2
[3] Singh, J., Lee, B.-K. (2016). Influence of nano-TiO2 particles on the bioaccumulation of Cd in soybean plants (Glycine max): A possible mechanism for the removal of Cd from the contaminated soil. Journal of environmental management, 170, 88-96.
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[4] Rizzello, L., Pompa, P. P. (2014). Nanosilver-based antibacterial drugs and devices: mechanisms, methodological drawbacks, and guidelines. Chemical society reviews, 43(5), 1501-1518.
4
[5] Rede, D., Santos, L. H., Ramos, S., Oliva-Teles, F., Antão, C., Sousa, S. R., Delerue-Matos, C. (2016). Ecotoxicological impact of two soil remediation treatments in Lactuca sativa seeds. Chemosphere, 159, 193-1981.
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[6] Khiew, P., Chiu, W., Tan, T., Radiman, S., Abd-Shukor, R., & Chia, C. H. (2011). Capping effect of palm-oil based organometallic ligand towards the production of highly monodispersed nanostructured material. Palm oil: Nutrition, uses and impacts, 189-219.
6
[7] Unrine, J. M., Colman, B. P., Bone, A. J., Gondikas, A. P., Matson, C. W. (2012). Biotic and abiotic interactions in aquatic microcosms determine fate and toxicity of Ag nanoparticles. Part 1. Aggregation and dissolution. Environmental science and technology, 46(13), 6915-6924.
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[8] Foltête, A.S., Masfaraud, J.-F., Bigorgne, E., Nahmani, J., Chaurand, P., Botta, C., Cotelle, S. (2011). Environmental impact of sunscreen nanomaterials: ecotoxicity and genotoxicity of altered TiO2 nanocomposites on Vicia faba. Environmental pollution, 159(10), 2515-2522.
8
[9] Huang, D., Qin, X., Peng, Z., Liu, Y., Gong, X., Zeng, G., Wang, X. (2018). Nanoscale zero-valent iron assisted phytoremediation of Pb in sediment: Impacts on metal accumulation and antioxidative system of Lolium perenne. Ecotoxicology and Environmental safety, 153, 229-237.
9
[10] Huang, R., Dong, M., Mao, P., Zhuang, P., Paz-Ferreiro, J., Li, Y., Li, Z. (2020). Evaluation of phytoremediation potential of five Cd (hyper) accumulators in two Cd contaminated soils. Science of the total environment, 137581.
10
[11] Gil-Díaz, M., Pinilla, P., Alonso, J., Lobo, M. (2017). Viability of a nanoremediation process in single or multi-metal (loid) contaminated soils. Journal of hazardous materials, 321, 812-819.
11
[12] Diego, B., Rubén, F., Lorena, W. (2020). Nanoremediation of As and metals polluted soils by means of graphene oxide nanoparticles. Scientific Reports, 10(1), 1-10
12
[13] Mokarram-Kashtiban, S., Hosseini, S. M., Kouchaksaraei, M. T., Younesi, H. (2019). The impact of nanoparticles zero-valent iron (nZVI) and rhizosphere microorganisms on the phytoremediation ability of white willow and its response. Environmental science and pollution research, 26(11), 10776-10789.
13
[14] Brasili, E., Bavasso, I., Petruccelli, V., Vilardi, G., Valletta, A., Dal Bosco, C., Di Palma, L. (2020). Remediation of hexavalent chromium contaminated water through zero-valent iron nanoparticles and effects on tomato plant growth performance. Scientific reports, 10(1), 1-11.
14
[15] Ma, X., Gurung, A., Deng, Y. (2013). Phytotoxicity and uptake of nanoscale zero-valent iron (nZVI) by two plant species. Science of the total environment, 443, 844-849.
15
[16] Wang, J., Fang, Z., Cheng, W., Yan, X., Tsang, P. E., Zhao, D. (2016). Higher concentrations of nanoscale zero-valent iron (nZVI) in soil induced rice chlorosis due to inhibited active iron transportation. Environmental pollution, 210, 338-345.
16
[17] Kim, J.H., Lee, Y., Kim, E.J., Gu, S., Sohn, E. J., Seo, Y. S., Chang, Y.S. (2014). Exposure of iron nanoparticles to Arabidopsis thaliana enhances root elongation by triggering cell wall loosening. Environmental science and technology, 48(6), 3477-3485.
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[18] Papazoglou, E. G., Fernando, A. L. (2017). Preliminary studies on the growth, tolerance and phytoremediation ability of sugarbeet (Beta vulgaris L.) grown on heavy metal contaminated soil. Industrial crops and products, 107, 463-471.
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[19] Walkley, A., Black, I. A. (1934). An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil science, 37(1), 29-38.
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[21] Wannaz, E. D., Carreras, H. A., Abril, G. A., Pignata, M. L. (2011). Maximum values of Ni2+, Cu2+, Pb2+ and Zn2+ in the biomonitor Tillandsia capillaris (Bromeliaceae): Relationship with cell membrane damage. Environmental and experimental botany, 74, 296-301.
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[22] Fang, R. (1991). Application of atomic absorption spectroscopy in sanitary test. In: Beijing university press, Beijing.
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[23] Embrandiri, A., Rupani, P., Shahadat, M., Singh, R., Ismail, S., Ibrahim, M., Kadir, M. A. (2017). The phytoextraction potential of selected vegetable plants from soil amended with oil palm decanter cake. International journal of recycling of organic waste in agriculture, 6(1), 37-45.
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[24] Yoon, H., Kang, Y.-G., Chang, Y.-S., Kim, J.-H. (2019). Effects of zerovalent iron nanoparticles on photosynthesis and biochemical adaptation of soil-grown arabidopsis thaliana. Nanomaterials, 9(11), 1543.
24
[25] Du, W., Sun, Y., Ji, R., Zhu, J., Wu, J., Guo, H. (2011). TiO2 and ZnO nanoparticles negatively affect wheat growth and soil enzyme activities in agricultural soil. Journal of environmental monitoring, 13(4), 822-828.
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[26] Abdel Latef, A. A. H., Srivastava, A. K., El‐sadek, M. S. A., Kordrostami, M., Tran, L. S. P. (2018). Titanium dioxide nanoparticles improve growth and enhance tolerance of broad bean plants under saline soil conditions. Land degradation and development, 29(4), 1065-1073.
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[27] Kleiber, T., Markiewicz, B. (2013). Application of “Tytanit” in greenhouse tomato growing. Acta scientiarum polonorum. Hortorum cultus, 12(3), 117-126.
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[28] Pan, X., Zhang, D., Chen, X., Bao, A., Li, L. (2011). Antimony accumulation, growth performance, antioxidant defense system and photosynthesis of Zea mays in response to antimony pollution in soil. Water, air, and soil pollution, 215(1-4), 517-523.
28
[29] Wan, X., Lei, M., Chen, T. (2016). Cost–benefit calculation of phytoremediation technology for heavy-metal-contaminated soil. Science of the total environment, 563, 796-802.
29
[30] Ehsan, S., Ali, S., Noureen, S., Mahmood, K., Farid, M., Ishaque, W., Rizwan, M. (2014). Citric acid assisted phytoremediation of cadmium by Brassica napus L. Ecotoxicology and environmental safety, 106, 164-172.
30
[31] Ashraf, S., Ali, Q., Zahir, Z. A., Ashraf, S., Asghar, H. N. (2019). Phytoremediation: Environmentally sustainable way for reclamation of heavy metal polluted soils. Ecotoxicology and environmental safety, 174, 714-727.
31
[32] Bhargava, A., Carmona, F. F., Bhargava, M., Srivastava, S. (2012). Approaches for enhanced phytoextraction of heavy metals. Journal of environmental management, 105, 103-120.
32
[33] Hell, R., Stephan, U. W. (2003). Iron uptake, trafficking and homeostasis in plants. Planta, 216(4), 541-551.
33
[34] Singh, O., Jain, R. (2003). Phytoremediation of toxic aromatic pollutants from soil. Applied microbiology and biotechnology, 63(2), 128-135.
34
[35] Zand, A. D., Nabibidhendi, G., Mehrdadi, N., Shirdam, R., Tabrizi, A. M. (2010). Total petroleum hydrocarbon (TPHs) Dissipation through rhizoremediation by plant species. Polish journal of environmental studies, 19(1) 115-122.
35
[36] Wang, S., Shi, X., Sun, H., Chen, Y., Pan, H., Yang, X., Rafiq, T. (2014). Variations in metal tolerance and accumulation in three hydroponically cultivated varieties of Salix integra treated with lead. PloS One, 9(9) 1-11.
36
[37] Vatehová, Z., Kollárová, K., Zelko, I., Richterová-Kučerová, D., Bujdoš, M., Lišková, D. (2012). Interaction of silicon and cadmium in Brassica juncea and Brassica napus. Biologia, 67(3), 498-504.
37
[38] Singh, J., Lee, B.-K. (2018). Effects of Nano-TiO2 particles on bioaccumulation of 133Cs from the contaminated soil by Soybean (Glycine max). Process safety and environmental protection, 116, 301-311.
38
[39] Din, B. U., Rafique, M., Javed, M. T., Kamran, M. A., Mehmood, S., Khan, M., Chaudhary, H. J. (2020). Assisted phytoremediation of chromium spiked soils by Sesbania Sesban in association with Bacillus xiamenensis PM14: A biochemical analysis. Plant Physiology and biochemistry, 146, 249-258.
39
[40] Wang, Y., Fang, Z., Kang, Y., Tsang, E. P. (2014). Immobilization and phytotoxicity of chromium in contaminated soil remediated by CMC-stabilized nZVI. Journal of hazardous materials, 275, 230-237.
40
[41] Zhao, L., Sun, Y., Hernandez-Viezcas, J. A., Hong, J., Majumdar, S., Niu, G., Gardea-Torresdey, J. L. (2015). Monitoring the environmental effects of CeO2 and ZnO nanoparticles through the life cycle of corn (Zea mays) plants and in situ μ-XRF mapping of nutrients in kernels. Environmental science and technology, 49(5), 2921-2928.
41
[42] Kamran, M., Malik, Z., Parveen, A., Zong, Y., Abbasi, G. H., Rafiq, M. T., Rafay, M. (2019). Biochar alleviates Cd phytotoxicity by minimizing bioavailability and oxidative stress in pak choi (Brassica chinensis L.) cultivated in Cd-polluted soil. Journal of environmental management, 250, 109500.
42
ORIGINAL_ARTICLE
Removal of Ni (II) from aqueous solution using modified MCM-41 nano-adsorbents
In this study, a synthetic and modified PPAP-MPTMS-MCM-41 nano-adsorbent was used to remove nickel (II) during a batch process. Studying the parameters that were effective on adsorption revealed that the PPAP-MPTMS-MCM-41 adsorbent was the most effective in the adsorption of nickel (II) from a standard solution (Conc. = 5 mg/L, volume = 100 mL) under the following conditions: pH=8, contact time = 20 min, 6 wt.% of poly para-aminophenol (PPAP) ligand, adsorbent mass = 0.3 g, 1 molar hydrochloric acid (to remove nickel from the adsorbent), and NaCl salt with a concentration of less than 100 g/L. The results showed that the Langmuir isotherm had a higher linear and non-linear fitting with the experimental data. Investigating the kinetic models and mass transfer of this adsorption process showed that the experimental data were in good agreement with the pseudo-second-order kinetic model and the intra-particle mass transfer model. According to thermodynamic studies, this adsorption process is endothermic; its Gibbs free energy value is positive such that with an increase in temperature, it goes to lower values, and thus the process progresses spontaneously.
https://aet.irost.ir/article_939_d271d1873c6ca969830fb76bec47cae8.pdf
2019-07-01
157
169
10.22104/aet.2020.4178.1207
Mesoporous MCM-41
Nano-adsorbent
Isotherm
Nickel
Behrouz
Raei
b.raei@mhriau.ac.ir
1
Department of Chemical Engineering, Mahshahr Branch, Islamic Azad University, Mahshahr, Iran
LEAD_AUTHOR
afsaneh
barekat
afsaneh.barekat@yahoo.com
2
Department of chemistry, Mahshahr Branch, Islamic Azad University, Mahshahr, Iran
AUTHOR
Habibollah
Shariyatinia
h.shariatinia@gmail.com
3
Department of Chemical Engineering, Mahshahr Branch, Islamic Azad University, Mahshahr, Iran
AUTHOR
[1] Duda-Chodak A, Blaszczyk U. (2008). The impact of nickel on human health. Journal of elementology, 13(4),685-693.
1
[2] Badruddoza A, Tay A, Tan P, Hidajat K, Uddin M. (2011). Carboxymethyl-β-cyclodextrin conjugated magnetic nanoparticles as nano-adsorbents for removal of copper ions: synthesis and adsorption studies. Journal of hazardous materials, 185(2-3),1177-1186.
2
[3] Song J, Kong H, Jang J. (2011). Adsorption of heavy metal ions from aqueous solution by polyrhodanine-encapsulated magnetic nanoparticles. Journal of colloid and interface science, 359(2),505-511.
3
[4] Khan TA, Singh VV. (2010). Removal of cadmium (II), lead (II), and chromium (VI) ions from aqueous solution using clay, Toxicological and environ chemistry 92(8),1435-1446.
4
[5] Subramani BS, Shrihari S, Manu B, Babunarayan K. (2019). Evaluation of pyrolyzed areca husk as a potential adsorbent for the removal of Fe2+ ions from aqueous solutions. Journal of environmental management, 246,345-354.
5
[6] Abadi MJ, Nouri S, Zhiani R, Heydarzadeh H, Motavalizadehkakhky A. (2019). Removal of tetracycline from aqueous solution using Fe-doped zeolite. International journal of industrial chemistry, 10(4),291-300.
6
[7] Mousavi SZ, Manteghian M, Shojaosadati SA, Pahlavanzadeh H. (2018). Keratin nanoparticles: synthesis and application for Cu (II) removal. Advances in Environmental Technology, 4(2), 83-93.
7
[8] Sharaf G, Abdel-Galil E, El-eryan Y. (2018). Modeling studies for adsorption of phenol and co-pollutants onto granular activated carbon prepared from olive oil industrial waste. Advances in environmental technology, 4(1),23-40.
8
[9] Schulz-Ekloff G, Wöhrle D, van Duffel B, Schoonheydt RA. (2002). Chromophores in porous silicas and minerals: preparation and optical properties. Microporous and mesoporous materials, 51(2),91-138.
9
[10] Scott BJ, Wirnsberger G, Stucky GD. (2001). Mesoporous and mesostructured materials for optical applications. Chemistry of materials, 13(10),3140-3150.
10
[11] Moriguchi I, Honda M, Ohkubo T, Mawatari Y, Teraoka Y. (2004). Adsorption and photocatalytic decomposition of methylene blue on mesoporous metallosilicates. Catalysis today, 90(3-4),297-303.
11
[12] Adjdir, M. (2010). Synthesis of mesoporous nanomaterials from natural sources as low-cost nanotechnology (Doctoral dissertation, Verlag nicht ermittelbar).
12
[13] Øye G, Sjöblom J, Stöcker M. (2001). Synthesis, characterization and potential applications of new materials in the mesoporous range. Advances in colloid and interface science, 89,439-466.
13
[14] Pinnavaia T. (1999). Selective adsorption of Hg 2+ by thiol-functionalized nanoporous silica. Chemical communications, (1), 69-70.
14
[15] Liu AM, Hidajat K, Kawi S, Zhao DY. (2000). A new class of hybrid mesoporous materials with functionalized organic monolayers for selective adsorption of heavy metal ions. Chemical communications, (13), 1145-1146.
15
[16] Algarra M, Jiménez MV, Rodríguez-Castellón E, Jiménez-López A, Jiménez-Jiménez J. (2005). Heavy metals removal from electroplating wastewater by aminopropyl-Si MCM-41. Chemosphere, 59(6), 779-786.
16
[17] Ebrahimzadeh H, Tavassoli N, Sadeghi O, Amini M, Vahidi S, Aghigh SM, Moazzen E. (2012). Extraction of nickel from soil, water, fish, and plants on novel pyridine-functionalized MCM-41 and MCM-48 nanoporous silicas and its subsequent determination by FAAS. Food analytical methods, 5(5),1070-1078.
17
[18] Ghorbani M, Nowee SM. (2015). Kinetic studies of Pb and Ni adsorption onto MCM-41 amine-functionalized nano particle. Advances in environmental technology, 1(2), 101-104.
18
[19] He R, Wang Z, Tan L, Zhong Y, Li W, Xing D, Wei C, Tang Y. (2018). Design and fabrication of highly ordered ion imprinted SBA-15 and MCM-41 mesoporous organosilicas for efficient removal of Ni2+ from different properties of wastewaters. Microporous and mesoporous materials, 257,212-221.
19
[20] Northcott KA, Miyakawa K, Oshima S, Komatsu Y, Perera JM, Stevens GW .(2010). The adsorption of divalent metal cations on mesoporous silicate MCM-41. Chemical engineering journal, 157(1),25-28.
20
[21] Jalali M, Aliakbar A. (2013). Electrochemical synthesis and characterization of a new selective chelating agent for Ni (II) and its environmental analytical application. Analytical methods, 5(22),6352-6359.
21
[22] Aliakbar A, Jalali M. (2014). Electrosynthesis of a new selective chelating agent for solid phase extraction of Ni (II) from water samples: characterisation and analytical applications. International journal of environmental analytical chemistry, 94(6),562-578.
22
[23] Teymouri M, SAMADI MA, Vahid A. (2011). A rapid method for the synthesis of highly ordered MCM-41 International Nano Letters, 1(1),34-37.
23
[24] Jalali M, Aliakbar A. (2015). Synthesis, characterisation and application of mercapto- and polyaminophenol-bifunctionalised MCM-41 for dispersive micro solid phase extraction of Ni(II) prio to inductively coupled plasma-optical emission spectrometry (DMSPE-ICP-OES). International journal of environmental analytical chemistry, 95(6),542-555.
24
[25] Showkat AM, Zhang Y-p, Kim MS, Gopalan AI, Reddy KR, Lee K. (2007). Analysis of heavy metal toxic ions by adsorption onto amino-functionalized ordered mesoporous silica. Bulletin-Korean chemical society, 28(11),1985.
25
[26] Khosa MA, Ullah A. (2014). In-situ modification, regeneration, and application of keratin biopolymer for arsenic removal. Journal of hazardous materials, 278,360-37.
26
[27] Freundlich H. (1906). Uber die adsorption in losungen [Adsorption in solution]” Zeitschrift für physikalische chemie, 57, 384-470.
27
[28] Langmuir I. (1916). The constitution and fundamental properties of solids and liquids. Part I. Solids. Journal of the American chemical society, 38(11),2221-2295.
28
[29] Ayawei N, Ebelegi AN, Wankasi D. (2017). Modelling and interpretation of adsorption isotherms. Journal of chemistry, 2017 (11),1-11.
29
[30] Redlich O, Peterson DL. (1959). A useful adsorption isotherm. Journal of physical chemistry, 63(6),1024-1024.
30
[31] Sips R .(1948). On the structure of a catalyst surface. The journal of chemical physics, 16(5),490-495.
31
[32] Qiu, H., Lv, L., Pan, B. C., Zhang, Q. J., Zhang, W. M., Zhang, Q. X. (2009). Critical review in adsorption kinetic models. Journal of Zhejiang University-Science A, 10(5), 716-724.
32
[33] Pérez-Quintanilla D, Sánchez A, del Hierro I, Fajardo M, Sierra I. (2007). Preparation, characterization, and Zn2+ adsorption behavior of chemically modified MCM-41 with 5-mercapto-1-methyltetrazole. Journal of colloid and interface science, 313(2),551-562.
33
[34] Aksu Z. (2002). Determination of the equilibrium, kinetic and thermodynamic parameters of the batch biosorption of nickel (II) ions onto Chlorella vulgaris. Process biochemistry, 38(1),89-99.
34
ORIGINAL_ARTICLE
Spatio Seasonal Discrepancies in the Physico-chemical Parameters along the Surface Water of Gahirmatha Estuary, East Coast of India in the Bay of Bengal
Water is a key factor in our lives, yet this valuable asset is progressively under threat. From the total share of the Earth's water, only 2% is fresh water, which is available for various life forms, including humans. Monitoring the quality of water is very important to check the physical, chemical, and biological characteristics, and the subsequent control of its wholesomeness. Particularly, the estuarine water bodies that are rich in diversity confront more threats for contamination in the entire riverine framework. This study was carried out to evaluate the current status of various physico-chemical properties of four different estuarine locations of the Gahirmatha coast, in the Indian state of Odisha in the eastern part of the Bay of Bengal: water temperature, pH, conductivity, TDS, TSS, turbidity, salinity, DO, BOD, total alkalinity, fluoride, Nitrite-N, Ammonia-N, Nitrate-N, phosphate, silicate, total chlorophyll. The study was carried out during the pre-monsoon (March to April) and post-monsoon (November to December) seasons in 2019. The surface water samples were collected from designated stations both during low tide and high tide to observe tidal influence. The data were subjected to statistical analysis regarding correlation coefficient, principal component analysis (PCA), and cluster analysis (CA) for interpretation. The Pearson correlation showed that the results were significantly correlated both at the 0.05 and 0.01 level of significance. When PCA was interpolated for the pre-monsoon and post-monsoon data, three broad groups were categorized. The highest eigen value was about 10.87 during the pre-monsoon and 9.07 during the post-monsoon season, and the cluster analysis showed there were two major groups of parameters with respect to the Euclidean distance. The observed variations in the concentration of these physico-chemical parameters in the estuarine waters of the Gahirmatha may be attributed to the riverine inputs from the catchment of rivers like the Brahmani, Baitarani, and Dhamra, which are associated with anthropogenic local activities.
https://aet.irost.ir/article_962_e9b7c3fb335f9ceec45aef0d24f0395c.pdf
2019-07-01
171
183
10.22104/aet.2020.4306.1216
Estuarine water body
Gahirmatha coast
Physico-chemical parameters
Statistical techniques
East coast of Bay of Bengal
Bhabani
Panda
bpanda607@gmail.com
1
Department of Chemistry, Centurion University, Odisha, India
LEAD_AUTHOR
SS Kalikinkar
Mahanta
mymummy5083@gmail.com
2
2P.G. Department of Environmental sciences, Sambalpur University, Odisha, India
AUTHOR
[1] Arimieari, L. W., Sangodoyin, A. Y., Ereoforiokuma, N. S. (2014). Assessment of surface water quality in some selected locations in Port Harcourt, Nigeria. International journal of engineering research and technology, 3(7), 1146-1151.
1
[2] Rahmanian, N., Ali, S. H. B., Homayoonfard, M., Ali, N. J., Rehan, M., Sadef, Y., Nizami, A. S. (2015). Analysis of physiochemical parameters to evaluate the drinking water quality in the State of Perak, Malaysia. Journal of chemistry, 1-10.
2
[3] Onifade, A. K., Ilori, R. M. (2008). Microbiological analysis of sachet water vended in Ondo State, Nigeria. Environmental research journal, 2(3), 107-110.
3
[4] Ababio, O.e Y. (2005). New school chemistry for senior secondary schools. African first publisher Ltd, Onitsha. 3rd edn, 292.
4
[5] Pardeshi, B.M. (2019). Screening of physicochemical parameters of water samples from pune area, india, Journal of emerging technologies and innovative research, 6(5), 63-68.
5
[6] Ramana, V., Rao, L. M., Manjulatha, C. (2015). Physico-chemical parameters of coastal waters of Visakhapatnam, east coast of India. Asian journal of experimental sciences, 29(1, 2), 7-10.
6
[7] Choudhury, S. B., Panigrahy, R. C. (1991). Seasonal destribution and behaviour of nutrients in the creek and coastal waters of Gopalpur, East Coast of India. Mahasagar, 24(2), 81-88.
7
[8] Gothandaraman, N. (1993). Studies on micro Zooplankton (Doctoral dissertation, PhD. thesis, Annamalai University, India).
8
[9] Panda, B. S., Mahanta, S. K. (2008). Quantification of Poly Aromatic Hydrocarbons in Waters of Mahanadi Estuary at Paradeep, Odisha. International research journal of engineering and technology, 7(6), 6971-6981.
9
[10] Smith, S. V., Swaney, D. P., Talaue-Mcmanus, L., Bartley, J. D., Sandhei, P. T., McLAUGHLIN, C. J, Wulff, F. (2003). Humans, hydrology, and the distribution of inorganic nutrient loading to the ocean. BioScience, 53(3), 235-245.
10
[11] Panda, B. S., Mahanta, SS K. (2020). Determination of herbicides and pesticides in estuary and sea water of Mahanadi, near Paradeep, Odisha, International journal of research and analytical reviews, 7(3,727), 686-697.
11
[12] Pejman, A.H., Nabi Bidhendi, G.R., Karbassi, A.R., Mehradi, N., Esmaeili, B.M. (2009). Evaluation of spatial and seasonal variations in surface water quality using multivariate statistical techniques. International journal of environmental science and technology, 6(3), 467–476.
12
[13] Yang, L., Song, X., Zhang, Y., Yuan, R., Ma, Y., Han, D., Bu, H. (2012). A hydro-chemical framework and water quality assessment of river water in the upper reaches of the Huai River Basin, China. Environmental earth science, 67(7), 2141–2153.
13
[14] Qadir, A., Malik, R.N., Husain, S.Z. (2008). Spatio-temporal variations in water quality of Nullah Aik-tributary of the river Chenab, Pakistan. Environmental monitoring and assessment, 140(1), 43–59.
14
[15] Zhang, X., Wang, Q., Liu, Y., Wu, J., Yu, M. (2011). Application of multivariate statistical techniques in the assessment of water quality in the Southwest New Territories and Kowloon, Hong Kong. Environmental monitoring and assessment, 173(1–4), 17–27.
15
[16] Mustapha, A., Aris, A.Z. (2012). Spatial aspects of surface water quality in the Jakara Basin, Nigeria using chemometric analysis. Journal of environmental science and health, Part A, 47(10), 1455–1465.
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[17] Martin, G.D., Vijay, J.G., Laluraj, C.M., Madhu, N.V., Joseph, M., Nair, G.V.M., Gupta, K.K. (2008). Fresh water influence on nutrient Stoichiometry in a tropical estuary, southwest coast of India. Applied ecology and environs. Research, 6(1), 57-64.
17
[18] Mc Lusky, D.S., Elliott, M. (2004). The estuarine ecosystem: ecology, threats and management, 3rd ed. Oxford University Press Inc., New York, NY, USA, 214.
18
[19] Jeyageetha, J.C., Sugirtha, P.K. (2015). Study of physico-chemical parameters of sea water in Tuticorin Coastal area and assessing their Quality, Tamil Nadu, India., Journal of chemical and pharmaceutical research, 7(5), 1298-1304.
19
[20] Behera, S., Tripathy, B., Kuppusamy, S., Choudhury, B.C. Pandav, B. (2016). Fisheries impact on breeding of olive ridley turtles (lepidochelysolivacea) along the gahirmatha coast, Bay of Bengal, Odisha, India. Herpetological Journal, 26, 93-98.
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[21] Behera, A., Pati, S.S., Mishra, S., Nayak. (2017). Report Card of Gahirmatha Coastal Stretch 2015, ICZMP, SPCB, Odisha, 7.
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[22] Mishra, R.R., Rath, B., Thatoi, H. (2008). Water Quality Assessment of Aquaculture Ponds Located in Bhitarkanika Mangrove ecosystem, Orissa, India. Turkish journal of fisheries and aquatic sciences, 8, 71-77.
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[23] Mishra, R.R., Swain, M.R., Dangar, T.K., Thatoi, H. (2012). Diversity and seasonal fluctuation of predominant microbial communities in Bhitarkanika, a tropical mangrove ecosystem in India. Revista de biología tropical, 60(2), 909-924.
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[24] Chauhan, R., Ramanathan, Al. (2008). Evaluation of water quality of Bhitarkanika mangrove system, Orissa, east coast of India. Indian journal of marine sciences, 37, 153-158.
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[25] Gupta, N.C., Das, S., Basak, Uday. (2007). Useful Extracellular Activity of Bacteria Isolated from Bhitarkanika Mangrove ecosystem of Orissa Coast. Malaysian journal of microbiology, 3, 15-18.
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[26] Qasim, S. Z. (1977). Biological productivity of the Indian Ocean. Indian journal of marine sciences, 6122–137
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[27] Radhakrishna, K., Devassy, V. P., Bhargava, R. M. S. (1978). Primary production in the Northern Arabian Sea, Indian journal of marine sciences, 7, 271–275.
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[28] Prasanna, S. K., Muraleedharan, P.M., Prasad, T. G. (2002). Why is the Bay of Bengal less productive during SM as compared to the Arabian Sea, Geophysical research letters, 29(24), 2238–2435.
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[29] Panda, U. C., Sundaray, S. K., Rath, P., Nayak, B. B., Bhatta, D. (2006). Application of factor and cluster analysis for characterization of river and estuarine water systems–a case study: Mahanadi River (India). Journal of hydrology, 331(3-4), 434-445.
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[30] Gomes, H. R., Goes, J. I., Saino, T. (2000). Influence of physical processes and freshwater discharge on the seasonality of phytoplankton regime in the Bay of Bengal. Continental shelf research, 20(3), 313-330.
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[31] Madhu, N.V., Maheswaran, P.A., Jyothibabu, R. (2002) Enhanced biological production off Chennai triggered by October 1999 super cyclone (Orissa). Current science, 82(12), 1472–1479.
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[32] Madhupratap, M., Gauns, M., Ramaiah, N. (2003). Biogeochemistry of the Bay of Bengal: physical, chemical and primary productivity during summer monsoon. Deep sea research, 50, 881–896
32
[33] Coastal regulation zone notification, (2011). Coastal regulation zone notification, Ministry of Environment and Forests (Department of Environment, Forests and Wildlife), Gazette of India, Extraordinary, Part-II, Section 3, Sub-section (ii) of dated the 6th January, 2011.
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[34] Biswal, D., Behera, A., Pati, S.S., Mishra, S., Nayak, S., Mishra, S., Panda, B.S., Behera, R. (2019). Status and trends of Coastal Parameters (2013-2018), Paradeep, Gahirmatha Dhamra coastal environment. ICZMP, SPCB, Odisha, 208.
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[35] Parsons, T. R., Maita, Y., Lalli, C. M. (1984). A manual of Chemical and biological methods for seawater analysis. Pergamon Press, Oxford, 173.
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[36] Olsen, A.R., Sedransk, J., Edwards, D., Gotway, C. A., Liggett, W., Rathbun, S., Reckhow, K. H., Young, L. J. (1999). Statistical issues for monitoring ecological and natural resources in the United States. Environmental monitoring and assessment, 54, 1-45.
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[37] Sundaray, S.K., Panda, U.C., Nayak, B.B., Bhatta, D. (2006). Multivariate statistical techniques for the evaluation of spatial and temporal variation in water quality of Mahanadi River–Estuarine system (India) a case study. Environmental geochemistry and health, 28, 317–330.
37
[38] Pradhan, U.K., Shirodkar, P.V., Sahu, B. K. (2009). Physico-chemical characteristics of the coastal water off Devi estuary, Orissa and evaluation of its seasonal changes using chemometric techniques. Current science, 96 (9), 1203-1209.
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[39] Helena, B., Pardo, R., Vega, M., Barrado, E., Fernandez, J.M., Fernandez, L. (2000). Temporal evolution of groundwater composition in an alluvial (Pisuerga river, Spain) by principal component analysis. Water research, 34, 807–816.
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[40] Singh, K.P., Malik, A., Mohan, D., Sinha, S. (2004). Multivariate statistical techniques for the evaluation of spatial and temporal variations in water quality of Gomti River (India) – a case study. Water research, 38, 3980–3992.
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[41] Liu, C.W., Lin, K.H., Kuo, Y. M. (2003). Application of factor analysis in the assessment of ground water in a blackfoot disease area in Taiwan. Science of the total environment, 313, 77–89.
41
ORIGINAL_ARTICLE
Analysis and zoning of air pollution in urban landscape using different models of spatial analysis (Case study: Tehran)
In this study, spatial zoning models were compared to evaluate the concentrations of PM 2.5 on a large scale in the urban landscape of Tehran. The spatial analysis of PM 2.5 concentration was conducted based on the data from twenty-four stations that measure and monitor the air in Tehran. Three interpolation models were used to assess the air pollution status via Arc GIS 10.6.1 software: universal kriging (UK), ordinary kriging (OK), and inverse distance weighted (IDW). The root mean square error (RMSE) and correlation coefficient (R2) were applied to compare the spatial models and select the best model. Standardized root-mean-square error (RMSE) was used to select the best conditions for running the OK and UK models. The results showed that the southern and central regions of Tehran had high concentrations of PM 2.5, and the annual mean of all the stations exceeded the EPA standard (15 μ/m3). According to the annual average, station 16 had the highest concentration of PM2.5 (112.75 μ/m3). The results of RMSE showed that the OK model was more suitable than the others for the spatial zoning of air pollution in the urban landscape (RMSE=9.322).
https://aet.irost.ir/article_969_962ae7d37e3c061c59fa8a09f2be8313.pdf
2019-07-01
185
191
10.22104/aet.2020.4251.1210
Air pollution
Spatial zoning
Interpolation models
Tehran
PM 2.5
Noushin
Birjandi
birjandi@lu.ac.ir
1
Faculty of Agriculture and Natural Resources, Lorestan University, Iran
AUTHOR
Morteza
Ghobadi
ghobadim93@gmail.com
2
Faculty of Agriculture and Natural Resources, Lorestan University, Iran
LEAD_AUTHOR
Masoume
Ahmadi
ahmadipari93@gmail.com
3
Faculty of Environment, College of Engineering, University of Tehran, Iran
AUTHOR
[1] Tainio, M., Sofiev, M., Hujo, M., Tuomisto, J. T., Loh, M., Jantunen, M. J., Porvari, P. (2009). Evaluation of the European population intake fractions for European and Finnish anthropogenic primary fine particulate matter emissions. Atmospheric environment, 43(19), 3052-3059.
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[2] Sosa, B. S., Porta, A., Lerner, J. E. C., Noriega, R. B., Massolo, L. (2017). Human health risk due to variations in PM10-PM2. 5 and associated PAHs levels. Atmospheric environment, 160(2), 27-35.
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[3] Jiang, N., Yin, S., Guo, Y., Li, J., Kang, P., Zhang, R., Tang, X. (2018). Characteristics of mass concentration, chemical composition, source apportionment of PM2. 5 and PM10 and health risk assessment in the emerging megacity in China. Atmospheric pollution research, 9(2), 309-321.
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[4] Pio, C., Alves, C., Nunes, T., Cerqueira, M., Lucarelli, F., Nava, S., Karanasiou, A. (2020). Source apportionment of PM2. 5 and PM10 by Ionic and Mass Balance (IMB) in a traffic-influenced urban atmosphere, in Portugal. Atmospheric environment, 223(22), 117-132.
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[5] Basu, N., Lanphear, B. P. (2019). The challenge of pollution and health in Canada. Canadian journal of public health, 110(2), 159-164.
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[6] Feng, C., Li, J., Sun, W., Zhang, Y., Wang, Q. (2016). Impact of ambient fine particulate matter (PM 2.5) exposure on the risk of influenza-like-illness: a time-series analysis in Beijing, China. Environmental health, 15(1), 17-28.
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[7] Yin, P., Brauer, M., Cohen, A., Burnett, R. T., Liu, J., Liu, Y., Zhou, M. (2017). Long-term fine particulate matter exposure and nonaccidental and cause-specific mortality in a large national cohort of Chinese men. Environmental health perspectives, 125(11), 102-117.
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[8] Sicard, P., Khaniabadi, Y. O., Perez, S., Gualtieri, M., De Marco, A. (2019). Effect of O 3, PM 10 and PM 2.5 on cardiovascular and respiratory diseases in cities of France, Iran and Italy. Environmental science and pollution research, 26(31), 32645-32665
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[9] Janssen, N. A. H., Fischer, P., Marra, M., Ameling, C., Cassee, F. R. (2013). Short-term effects of PM2. 5, PM10 and PM2. 5–10 on daily mortality in the Netherlands. Science of the total environment, 463(9), 20-26.
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[10] Kollanus, V., Prank, M., Gens, A., Soares, J., Vira, J., Kukkonen, J., Lanki, T. (2017). Mortality due to vegetation fire–originated PM2. 5 exposure in Europe—assessment for the years 2005 and 2008. Environmental health perspectives, 125(1), 30-37.
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[11] Ciarelli, G., Colette, A., Schucht, S., Beekmann, M., Andersson, C., Manders-Groot, A., Adani, M. (2019). Long-term health impact assessment of total PM2. 5 in Europe during the 1990–2015 period. Atmospheric environment: 12(3), 100-132.
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[12]. Wang, Y., Shi, L., Lee, M., Liu, P., Di, Q., Zanobetti, A., Schwartz, J. D. (2017). Long-term exposure to PM2. 5 and mortality among older adults in the southeastern US. Epidemiology, 28(2), 189- 207.
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[13]. Yazdi, M. D., Wang, Y., Di, Q., Zanobetti, A., Schwartz, J. (2019). Long-term exposure to PM2. 5 and ozone and hospital admissions of Medicare participants in the Southeast USA. Environment international, 130(21), 104-119.
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[14] Maji, K. J., Arora, M., Dikshit, A. K. (2018). Premature mortality attributable to PM2. 5 exposure and future policy roadmap for ‘airpocalypse’affected Asian megacities. Process safety and environmental protection, 118(9), 371-383.
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[15] Liang, F., Xiao, Q., Gu, D., Xu, M., Tian, L., Guo, Q., Liu, Y. (2018). Satellite-based short-and long-term exposure to PM2. 5 and adult mortality in urban Beijing, China. Environmental pollution, 242(11), 492-499
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[16] Yorifuji, T., Kashima, S., Tani, Y., Yamakawa, J., Doi, H. (2019). Long-term exposure to fine particulate matter and natural-cause and cause-specific mortality in Japan. Environmental epidemiology, 3(3), 111-131.
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[17] Ansari, M., Ehrampoush, M. H. (2019). Meteorological correlates and AirQ+ health risk assessment of ambient fine particulate matter in Tehran, Iran. Environmental research, 170(21), 141-150.
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[18] Liu, M., Zhou, G., Saari, R. K., Li, S., Liu, X., Li, J. (2019). Quantifying PM2. 5 mass concentration and particle radius using satellite data and an optical-mass conversion algorithm. ISPRS journal of photogrammetry and remote sensing, 158(1), 90-98.
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[19] Shukla, K., Kumar, P., Mann, G. S., Khare, M. (2020). Mapping spatial distribution of particulate matter using Kriging and inverse distance weighting at supersites of megacity Delhi. Sustainable cities and society, 54(8), 101-118.
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[20] Hinojosa-Baliño, I., Infante-Vázquez, O., Vallejo, M. (2019). Distribution of PM2. 5 air pollution in Mexico City: Spatial analysis with land-use regression model. Applied sciences, 9(14), 29-36.
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[21] Ehrampoush, M. H., Jamshidi, S., Zare Sakhvidi, M. J., Miri, M. (2017). A Comparison on Function of Kriging and inverse distance weighting models in PM10 zoning in Urban Area. Journal of environmental health and sustainable development, 2(4), 379-387.
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[22] Kim, S. Y., Yi, S. J., Eum, Y. S., Choi, H. J., Shin, H., Ryou, H. G., Kim, H. (2014). Ordinary kriging approach to predicting long-term particulate matter concentrations in seven major Korean cities. Environmental health and toxicology, 29(1), 112-134.
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[23] Sampson, P. D., Richards, M., Szpiro, A. A., Bergen, S., Sheppard, L., Larson, T. V., Kaufman, J. D. (2013). A regionalized national universal kriging model using Partial least squares regression for estimating annual PM2. 5 concentrations in epidemiology. Atmospheric environment, 75(5), 383-392.
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[24] Habibi, R., Alesheikh, A. A., Mohammadinia, A., Sharif, M. (2017). An assessment of spatial pattern characterization of air pollution: A case study of CO and PM2. 5 in Tehran, Iran. ISPRS international journal of Geo-information, 6(9), 270-284.
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[25] Pardakhti, A., Ebrahimi Qadi, M. (2019). Introduction and application of new GIS_AQI model: Integrated pollution control in Tehran. Pollution, 5(4), 789-801.
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[26] Haghparast, M., Haji Seyed Mirza Hosseini, S. A., Mansouri, N., Ghodousi, J. (2019). Prediction of air pollution index by the GIS tools during cold seasons in the commercial zones of Tehran. Environmental energy and economic research, 3(3), 241-260.
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[27] Xu, S., Zou, B., Lin, Y., Zhao, X., Li, S., Hu, C. (2019). Strategies of method selection for fine-scale PM2. 5 mapping in an intra-urban area using crowdsourced monitoring. Atmospheric measurement techniques, 12(5), 114-128.
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[28] Cao, R., Li, B., Wang, Z., Peng, Z. R., Tao, S., Lou, S. (2020). Using a distributed air sensor network to investigate the spatiotemporal patterns of PM2. 5 concentrations. Environmental pollution, 42(5), 135-149.
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[29] Wang, Y., Bechle, M. J., Kim, S. Y., Adams, P. J., Pandis, S. N., Pope III, C. A., Marshall, J. D. (2020). Spatial decomposition analysis of NO2 and PM2. 5 air pollution in the United States. Atmospheric environment, 12(2), 117-128.
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[30] Zhang, T., Liu, P., Sun, X., Zhang, C., Wang, M., Xu, J., Huang, L. (2020). Application of an advanced spatiotemporal model for PM2. 5 prediction in Jiangsu Province, China. Chemosphere, 246(2), 125-139.
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[31] Yang, W., Wang, G., Bi, C. (2017). Analysis of longrange transport effects on PM2. 5 during a short severe haze in Beijing, China. Aerosol and air quality Research, 17(21), 1610-1622.
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[32] Norpoor, A., Feyz, M. A. (2014). Determination of the Spatial and Temporal Variation of SO2, NO2 and Particulate Matter Using GIS Techniques and Estimation of Concentration Modeling with LUR Method (Case Study: City of Tehran), Journal of environmental studies, 40(3), 723-738.
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[33] Berman, J. D., Breysse, P. N., White, R. H., Waugh, D. W., Curriero, F. C. (2015). Evaluating methods for spatial mapping: Applications for estimating ozone concentrations across the contiguous United States. Environmental technology and innovation, 3(2), 1-10.
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[34] Halek, F., Kavousi-Rahim, A. (2014). GIS assessment of the PM 10, PM 2.5 and PM 1.0 concentrations in urban area of Tehran in warm and cold seasons. The international archives of photogrammetry, Remote sensing and spatial information sciences, 40(2), 141-153.
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