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Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals

Received: 14 December 2021    Accepted: 16 March 2022    Published: 20 April 2022
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Abstract

Today, human activities such as pesticides, fertilizers, industrial and nuclear wastes, and Nano pollutants, which contain heavy metals, affect the performance and flexibility of soil ecosystems, microorganisms, and plants. It also pollutes surface water, groundwater and the food chain. The aim of this study was to investigate the phytoremediation potential of heavy metals from soil by Vetiver and the effect of these metals on plant morphological changes in greenhouse conditions. Soil contamination with heavy metals has become a worldwide concern. This research was conducted as a factorial design with four different heavy metals (lead, cadmium, manganese and nickel) with three varying levels and also three replications for each treatment. The results of analysis of variance, Duncan test, showed that the effect of applied treatments on lead uptake in roots and shoots increased significantly (P ≤ 0.05) with increasing levels of treatments. The biological concentration factor was more than one, and the transfer factor was close to one. Therefore, it can be used as a phytostablization plant. Also, with different levels of heavy metal treatments, the highest average height of total plants was related to lead, manganese, nickel and cadmium treatments with values of 167.54, 166.66, 165.85 and 163.88cm, respectively. The highest average root roots of plants were related to lead, manganese, nickel and cadmium treatments with values of 42.27, 42.36, 41.85 and 41.61 Cm, respectively. The highest average root roots of plants were related to the treatments of lead, manganese, nickel and cadmium with values of 125.28, 124.29, 124.02 and 121.68 Cm, respectively. Therefore, among all treatments, plants treated with cadmium had the lowest growth. The results showed that Vetiver can be considered as a refining plant due to its vegetative characteristics, cost-effectiveness and high adaptation to environmental conditions.

Published in International Journal of Environmental Chemistry (Volume 6, Issue 1)
DOI 10.11648/j.ijec.20220601.12
Page(s) 7-27
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Phytoremedation, Vetiver Grass, Heavy Metals, Morphology

References
[1] Adam T. Ruley; Nilesh C. Sharma; Shivendra V. Sahi; Shree R. Singh; Kenneth S. Sajwan (2006). Effects of lead and chelators on growth, photosynthetic activity and Pb uptake in Sesbania drummondii grown in soil., 144 (1), 0–18. doi: 10.1016/j.envpol.2006.01.016.
[2] Anning, A. K., R. Akoto. 2018. Assisted phytoremediation of heavy metal contaminated soil from a mined site with Typha latifolia and Chrysopogon zizanioides. – Ecotoxicology and Environmental Safety. 148: 97-104. doi: 10.1016/j.ecoenv.2017.10.014.
[3] Aibibu, N., Liu, Y., Zeng, G. Wang, X., Chen, B., Song, H., Xu, L. 2010. Cadmiumaccumulation in Vetiveriazizanioides and its effects on growth, physiological and biochemical characters. Bioresource Technolo. 101 (16): 6297-6303. doi: 10.1016/j.biortech.2010.03.028.
[4] Ali, H., Khan, E., Sajad, M. A. 2013. Phytoremediation of heavy metals: concepts and applications. Chemosphere, 91 (7): 869–881. doi: 10.1016/j.chemosphere.2013.01.075.
[5] Alimardan, M., Ziarati, P., and Jafari Moghadam, R. 2016. Adsorption of Heavy Metal Ions from Contaminated Soil by integerrima Barberry. Biomed. Pharmacol. J. 9 (1): 169 75.‏ doi: 10.13005/bpj/924.
[6] Alloway, B. J. 2012. Heavy metals in soils: trace metals and metalloids in soils and their bioavailability. (3rd Ed.). Environ Pollut. (V. 22). Springer Sci. Business Media. doi: 10.1007/978-94-007-4470-7_2.
[7] ASTM. 2014. Standard Test Method for Analysis of Nickel Alloys by Flame Atomic Absorption Spectrometry (ASTM E1835-14, 2014).
[8] ASTM. 2014. Standard Test Method for Low Concentrations of Lead, Cadmium, and Cobalt in Paint by Atomic Absorption Spectroscopy (ASTM D3335 - 85a, 2014).
[9] ASTM. 2017. Standard Test Method for Manganese in Gasoline By Atomic Absorption Spectroscopy (ASTM D3831 – 12, 2017).
[10] Baccouch, S., A. Chaiui and E. El Ferjani. 2001. 'Nickel toxicity induces oxidative damage in Zea mays roots'. Journal of Plant Nutrition, 24: 1085-1095.
[11] Banerjee, R., Goswami, P., Lavania, S., Mukherjee, A., Lavania. U. C. 2019. Vetiver grass is a potential candidate for phytoremediation of iron ore mine spoil dumps. Ecol. Engineer. 132: 120-136. doi: 10.1016/j.ecoleng.2018.10.012.
[12] Banerjee, R., Goswami, P., Pathak, K., Mukherjee, A. 2016. Vetiver grass: an environment clean-up tool for heavy metal contaminated iron ore mine-soil. Ecol. Engineer. 90: 25–34. doi: 10.1016/j.ecoleng.2016.01.027.
[13] Baycu, G., T. Doganay, O. Hakan and G. Sureyya. 2006. Ecophysiological and seasonal variations in Cd, Pb, Zn, and Ni concentrations in the leaves of urban deciduous trees in Istanbul'. Environmental Pollution, 143: 545-554.
[14] Beladi, M., & Habibi, D. 2011. Phytoremediation of lead and copper by sainfoin (Onobrychis vicifolia): role of antioxidant enzymes and biochemical biomarkers. American-Eurasian Journal of Agricultural & Environmental Sciences, 10 (3), 440–449.
[15] Bilal, Qunshan Wei. 2021. Phytoremediation of contaminated soil Lead and Cadmium by Brassica júncea (L.) Czern plant Journal of Earth Sciences & Environmental Studies. Vol-5 Issue-4 (ISSN: 2472-6397) DOI: 10.25177/JESES.5.4.RA.10693.
[16] Chen, C., D. Huang and J. Liu. 2009. 'Functions and toxicity of Nickel in plants: advances and future prospects'. Clean Air Soil water, 37: 304-313.
[17] Chen Y., Shen, Z., and Li, X. 2004. The use of Vetivergrass (Vetiveriazizanioides) in the phytoremediation of soils contaminated with heavy metals. Appl. Geochem. 19 (10): 1553-1565. doi: 10.1016/j.apgeochem.2004.02.003.
[18] Danielson, R. E., and Sutherland, P. L. 1986. Porosity. Methods of Soil Analysis: Part 1 Physic. Mineralogic. Meth. 5: 443-461.
[19] Effendi, H., Munawaroh, A., Ayu, I. P. 2017. Crude oil spilled water treatment with Vetiveriazizanioidesin floating wetland. The Egyp. J. of Aquat. Res. 43 (3): 185-193. doi: 10.1016/j.ejar.2017.08.003.
[20] Effendi, H., Utomo, B. A., Pratiwi, N. T. 2020. Ammonia and orthophosphate removal of tilapia cultivation wastewater with Vetiveriazizanioides. J. of King. Saud Univers. Sci. 32 (1): 207-212. ‏doi: 10.1016/j.jksus.2018.04.018.
[21] Fan, U., Zhu, T., Li, M., He, J., Huang, R. 2017. Heavy Metal Contamination in Soil and Brown Rice and Human Health Risk Assessment near Three Mining Areas in Central China. J Healthcare Eng 2017: 2017. 4124302. doi: 10.1155/2017/4124302.
[22] Flathman, P. E., Lanza, G. R. 2010. Phytoremediation: current views on an emerging green technology. J. soil Contam. 7 (4): 415-432. doi: 10.1080/10588339891334438.
[23] Fomenky, N. N., Tening, A. S., Chuyong, G. B., Mbene, K., Asongwe, G. A., and Che, V. B. 2018. Selected physicochemical properties and quality of soils around some rivers of Cameroon. J. Soil. Sci and Environ Manag. 9 (5): 68-80.‏
[24] Gautam, M., Agrawal, M. 2017. Phytoremediation of metals using Vetiver (Chrysopogonzizanioides (L.) Roberty) grown under different levels of red mud in sludge amended soil. J. Geochem. Explor. 182: 218-227. doi: 10.1016/j.gexplo.2017.03.003.
[25] Ghosh, M. and Singh, S. P. (2005) A Review on Phytoremediation of Heavy Metals and Utilization of Its Byproducts. Applied Ecology and Environmental Research, 3, 18. http://dx.doi.org/10.15666/aeer/0301_001018.
[26] Gupta, A. K., Verma, S. K., Khan, K., & Verma, R. K. 2013. Phytoremediation using aromatic plants: A sustainable approach for remediation of heavy metals polluted sites. Environmental Science and Technology, 47 (18), 10115–10116.
[27] Habibi, H., Moghaddam, B. and Alikhani, H. A. 2017. Effect of biochar and biological treatments on nutrient concentrations (P, K, Ca, Mg, Fe and Mn) of Amaranths in oil polluted soil. Ir. Soil. Water. Res. 48 (2): 369-384.
[28] Issam A. Al-Khatib; Hassan A. Arafat; Raeda Daoud; Hadeel Shwahneh (2009). Enhanced solid waste management by understanding the effects of gender, income, marital status, and religious convictions on attitudes and practices related to street littering in Nablus – Palestinian territory., 29 (1), 449–455. doi: 10.1016/j.wasman.2008.02.004.
[29] Jeelani, N., Yang, W., Xu, L., Qiao, Y., An, S., Leng. X. 2017. Phytoremediation potential of Acoruscalamus in soils co-contaminated with cadmium and polycyclic aromatic hydrocarbons. Sci Rep. 7 (1): 1-9. doi: 10.1038/s41598-017-07831-3.
[30] Kafil, M., BoroomandNasab, S., Moazed, H., and Bhatnagar, A. 2019. Phytoremediation potential of Vetivergrass irrigated with waste water for treatment of metal contaminated soil. Inter. J. Phytoremediat. 21 (2): 92-100. doi: 10.1080/15226514.2018.1474443.
[31] Kavamura, V. N., Esposito, E. 2010. Biotechnological strategies applied to the decontamination of soils polluted with heavy metals. Biotechnol adv. 28 (1): 61-69. doi: 10.1016/j.biotechadv.2009.09.002.
[32] Kozhevnikova A. D., Seregin I. V., Bystrova E. I., Belyaeva A. I., Kataeva M. N., Ivanov V. B. 2009. The effects of lead, nickel, and strontium nitrates on cell division and elongation in maize roots. Russ. J. Plant Physiol. 56 242–250.
[33] Kumar, R. S., Saha, S., Dhaka, S., Kurade, M. B., Kang, C. U., Baek, S. H., and Jeon, B. H. 2017. Remediation of cyanide-contaminated environments through microbes and plants: a review of current knowledge and future perspectives. Geo Engineer. 20 (1): 28-40. doi: 10.1080/12269328.2016.1218303.
[34] Li DZ & Pritchard HW. 2009. The science and economics of ex situ plant conservation. Trends in Plant Sci 14 (11): 614-621. View Article.
[35] Liamas, A., C. I. Ullrich and A. Sanz. 2008. 'Ni2+ toxicity in rice: Effect on membrane functionality and plant water content'. Plant Physiology and Biochemistry, 46: 905-910.
[36] Lin, C., Liu, J., Liu, L., Zhu, T., Sheng L., and Wang, D. 2009. Soil amendment application frequency contributes to phytoextraction of lead by sunflower at different nutrient levels. Environ. Ex. Bot. 65 (2-3): 410-416. doi: 10.1016/j.envexpbot.2008.12.003.
[37] Mahmoud Soltani, S., Hanafi, M. M., Wahid, S. A., and Kharidah, S. M. S. 2015. Zinc fractionation of tropical paddy soils and their relationships with selected soil properties. Chem. Speciat. Bioavailability. 27 (2): 53-61.‏doi: 10.1080/09542299.2015.1023091.
[38] Malar Srinivasan., Sahi Shivendra Vikram, Paulo JC Favas and Venkatachalam Perumal. 2014. Lead heavy metal toxicity induced changes on growth and antioxidative enzymes level in water hyacinths [Eichhornia rassipes (Mart.)]. Botanical Studies, 2014. 55: 54.
[39] Malecka A., Piechalak A., Tomaszewska B. 2009. Reactive oxygen species production and antioxidative defense system in pea root tissues treated with lead ions: the whole roots level. Acta Physiol. Plant. 31 1053–1063.
[40] Mohammadzadeh, M., S. Rahimi Moghaddam, M. R. Chaichi and Y. Heidarzadeh. 2017. 'Phytoremediation ability of nickel contaminated soil using Sunflower (Helianthus annuus L.) and Sorghum (Sorghum bicolor L.)'. Journal of Soil Management and Sustainable Production, 6 (4): 131-142.
[41] Molas, J. and Baran, S. (2004) Relationship between the Chemical form of Nickel Applied to the Soil and Its Uptake and Toxicity to Barley Plants (Hordeum vulgare L.). Geoderma, 122, 247-255. https://doi.org/10.1016/j.geoderma.2004.01.011
[42] Molassiotis, A., T. Satipoulos, G. Tanou, G. Diamantidis and I. Therios. 2006. Boroninduced oxidative damage and antioxidant and nucleolytic responses in shoot tips culture of apple rootstock EM9 (Malus domestica Borkh.)'. Environmental and Experimental Botany, 56 (1): 54-62.
[43] Mojiri., A. Abdul Aziz., H. Tajuddin., R. B. M. Gavanji., S. and Gholami., A. 2015. Heavy Metals Phytoremediation from Urban Waste Leachate by the Common Reed (Phragmites australis). Phytoremediation Management of Environmental Contaminants, Volume 2. DOI: 10.1007/978-3-319-10969-5_7.
[44] Naeini, J. and M. Yousefi Rad. 2018. Phytoremediation capability of nickel and manganese polluted soil by Sorghum biocilor L.'. Iranian Journal of Plant Physiology 8 (3), 2427-2435.
[45] Nagajyoti, P. C., Lee, K. D., Sreekanth, T. V. M. 2010. Heavy metals, occurrence and toxicity for plants: a review. Environ Chem Lett. 8 (3): 199–216. doi: 10.1007/s10311-010-0297-8.
[46] Ng, C. C., Boyce, A. N., Rahman, M. M., Abas, M. R. 2016 a. Phytoassessment of soil heavy metal accumulation in tropical grasses. JAnim Plant Sci. 26 (3): 686-696.
[47] Ng, C C., Rahman, M. M., Boyce, A. N., Abas, M. R. 2016 b. Heavy metals phyto-assessment in commonly grown vegetables: water spinach (I. aquatica) and okra (A. esculentus). Springer Plus. 5 (1): 469. doi: 10.1186/s40064-016-2125-5.
[48] Ng, C. C., Boyce, A. N., Rahman, M. M., Abas, M. R. 2016 c. Effects of Different Soil Amendments on Mixed Heavy Metals Contamination in Vetiver Grass. Bull. Environ. Contam. Toxicol. 97 (5): 695-701. doi: 10.1007/s00128-016-1921-5.
[49] Nilay Nath, B. K. R., Sudipta, S. 2017. Comparative Analysis of Effects of Heavy Metal (Cd) on Chlorophyll Content of Different Rice (Oryza Sativa. L) Varieties (IR. 36 & Laghu) from Lower Gangetic Basin of West Bengal, India. Inter. J. of Engineer. Sci. Comput. 2: 14745-14748. doi: 10.24327/ijrsr.2017.0808.0694.
[50] Ojoawo, S. O., Udayakumar, G., Naik, P. 2015. Phytoremediation of phosphorus and nitrogen with Canna x generalis reeds in domestic wastewater through NMAMIT constructed wetland. Aquatic Procedia. 4: 349–356. doi: 10.1016/j.aqpro.2015.02.047.
[51] Omar A. Al-Khashman; Reyad A. Shawabkeh (2006). Metals distribution in soils around the cement factory in southern Jordan, 140 (3), 0–394. doi: 10.1016/j.envpol.2005.08.023.
[52] Pandey, N., Pathak, G. C., & Sharma, C. P. (2006). Zinc is critically required for pollen func-tion and fertilization in lentil. Journal of Trace Elements in Medicine and Biology, 20 (2), 89-96. View Article.
[53] Panja, S., Sarkar, D., Datta, R. 2018. Vetivergrass (Chrysopogonzizanioides) is capable of removing insensitive high explosives from munition industry wastewater. Chem. 209: 920-927. doi: 10.1016/j.chemosphere.2018.06.155.
[54] Piotrowska A, Bajguz A, Godlewska B, Czerpak R, Kaminska M. 2009. Jasmonic acid as modulator of lead toxicity in aquatic plant Wolffia arrhiza Lamnaceae). Environ Exp Bot 66: 507–513.
[55] Pulford, I. 2003. Phytoremediation of heavy metal-contaminated land by trees—a review. Environment International, 29 (4), 529–540. doi: 10.1016/s0160-4120(02)00152-6.
[56] Seroja, R., Effendi, H., Hariyadi, S. 2018. Tofu wastewater treatment using Vetivergrass (Vetiveriazizanioides) and zeliac. Appl. Water Sci. 8 (1): 2. doi: 10.1007/s13201-018-0640 y.
[57] Seregin, I. V. and A. D. Kozhevnikova. 2008. Physiological role of nickel and its toxic effects on higher plants'. Russian Journal of Plant Physiol. 53: 257–277.
[58] Shanti., S. S. and Karl-Josef Dietz2,. 2006. The significance of amino acids and amino acid-derived molecules in plant responses and adaptation to heavy metal stress. Journal of Experimental Botany, 57 (4), 711–726. doi: 10.1093/jxb/erj073.
[59] Shin MN, Shim J, You Y, Myung H, Bang KS, Cho M & Oh BT. 2012. Characterization of lead resistant endophytic Bacillus sp. MN3-4 and its potential for promoting lead accumulation in met-al hyperaccumulator Alnus firma. J of Hazardous Materials 199: 314-320. View Article.
[60] Shokry, Z., Borumand, N., Sarcheshme Pourand, M., Alizadeh, R. 2017. The Influence of Mycorrhiza-Arbuscular Fungi on Cadmium Phytoremediation by Ornamental Parsley Tageteserecta. J. Soil. Manage. Sustain. Product. 6 (1): 191-204.
[61] Siyar, R., Ardejani, D. F., Farahbakhsh, M., Norouzi, P., Yavarzadeh, M., and Maghsoudy, S. 2020. Potential of VetiverGrass for the Phytoremediation of a Real Multi-Contaminated Soil, Assisted by Electrokinetic. Chemosphere. 246: 125802. doi: 10.1016/j.chemosphere.2019.125802.
[62] Singh, S., Sounderajan, S., Kumar, K., Fulzele, D. P. 2017. Investigation of arsenic accumulation and biochemical response of in vitro developed Vetiveriazizanoides plants. Ecotoxicol. Environ. Saf. 145: 50-56. doi: 10.1016/j.ecoenv.2017.07.013.
[63] Rashid Shomali A, H. Khodaverdiloo and A. Samadi.2012. 'Accumulation and tolerance to soil cadmium by Pennisetum glausum, Chnopodium album, Portulaca oleracea and Descurainia sophia'. Iranian Journal of Soil Management and Sustainable Agriculture 2 (1): 45-62.
[64] Rezai, K. and Farbodnia, T. (2008) The response of pea plant to manganese toxicity in solution culture. Journal of Agricultural Science 3: 248-251.
[65] Ryser, P., & Sauder, W. R. 2006. Effects of heavy-metal-contaminated soil on growth, phenol-ogy and biomass turnover of Hieraciumpilo-selloides. Environmental Pollution, 140 (1), 52-61. View Article.
[66] Tambunan, J. A. M., Effendi, H., Krisanti, M. 2018. Phytomerediating batik wastewater using Vetiver Chryspogonzizanioides (L). Polish J. Environ. Stud. 27 (3): 1281–1288. doi: 10.1007/s13201-018-0640-y.
[67] Thakur Sveta, Singh Lakhveer, Wahid Zularisam, Siddiqui Muhammad Faisal, Atnaw Samson Mekbib, Mohd Fadhil. 2016. Plant-driven removal of heavy metals from soil: uptake, translocation, tolerance mechanism, challenges, and future perspectives. Environ Monit Assess 188: 206.
[68] Truong, P., Danh, L. T. 2015. The vetiver system for improving water quality. prevention and treatment of contaminated water and land, 2nd edn, San Antonio, TX, USA.
[69] Truong, P., Van, T. T., Pinners, E. 2008. Vetiver system applications technical reference manual, 2nd edn. The Vetiver Network International. 89.
[70] Turner AP & Dickinson NM (1993). Survival of Acer pseudoplatanus L (sycamore) seedlings on metalliferous soils. New Phytologist 123 (3): 509-521. View Article.
[71] Vaverková, M. D., D. Adamcová., M. Radziemska., S. Voběrková., Z. Mazur., J. Zloch. 2018. Assessment and evaluation of heavy metals removal from landfill leachate by Pleurotus ostreatus. – Waste and Biomass Valorization 9 (3): 503-511. doi: 10.1007/s12649-017-0015-x.
[72] Wachirawongsakorn, P., Jamnongkan, T., Latif, M. T. 2015. Removalof cyanide-contaminated water by Vetiver grasses. Modern. Appl. Sci. 9 (13): 252. doi: 10.5539/mas.v9n13p252.
[73] Wang., J. Chunhe Li, Erkang Wang and R. Stephen Berry (2010). Potential and flux landscapes quantify the stability and robustness of budding yeast cell cycle network. Proceedings of the National Academy of Sciences of the United States of America, 107 (18), 8195–8200. doi: 10.2307/25665515.
[74] Yang, R., S. Gao, W. Yang, M. Cao, S. Wang and F. Chen. 2008. Nickel toxicity induced antioxidant enzyme and phenylalanine ammonia-lyase activities in Jatropha curcas L. cotyledons'. Plant Soil Environ, 54: 294-300.
[75] Zhang, M.-K., Liu, Z.-Y., & Wang, H. 2010. Use of Single Extraction Methods to Predict Bioavailability of Heavy Metals in Polluted Soils to Rice. Communications in Soil Science and Plant Analysis, 41 (7), 820–831.
[76] Zhang. Z., Rengel, Z., and Meney, K. 2010. Cadmium accumulation and translocation in four emergent wetland species. Water. Air. Soil. Pollut. 212 (1-4): 239-249. doi: 10.1007/s11270-010-0339-7.
[77] Zhao, G.; Li, G.; Zhou, X.; Matsuo, I.; Ito, Y.; Suzuki, T.; Lennarz, W. J; Schindelin, H. 2009. Structural and mutational studies on the importance of oligosaccharide binding for the activity of yeast PNGase. Glycobiology, 19 (2), 118–125. doi: 10.1093/glycob/cwn108.
[78] Ziarati, P., and Shad, M. 2017. Investigation of heavy metals of lead, cadmium and nickel in Iranian and imported Iranian rice. Ir. J. Nutr. Sci and Food Technol. 12 (2): 97-104.
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    Fourud Gravand, Seyedeh Aghileh Hejazi. (2022). Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals. International Journal of Environmental Chemistry, 6(1), 7-27. https://doi.org/10.11648/j.ijec.20220601.12

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    Fourud Gravand; Seyedeh Aghileh Hejazi. Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals. Int. J. Environ. Chem. 2022, 6(1), 7-27. doi: 10.11648/j.ijec.20220601.12

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    Fourud Gravand, Seyedeh Aghileh Hejazi. Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals. Int J Environ Chem. 2022;6(1):7-27. doi: 10.11648/j.ijec.20220601.12

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  • @article{10.11648/j.ijec.20220601.12,
      author = {Fourud Gravand and Seyedeh Aghileh Hejazi},
      title = {Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals},
      journal = {International Journal of Environmental Chemistry},
      volume = {6},
      number = {1},
      pages = {7-27},
      doi = {10.11648/j.ijec.20220601.12},
      url = {https://doi.org/10.11648/j.ijec.20220601.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijec.20220601.12},
      abstract = {Today, human activities such as pesticides, fertilizers, industrial and nuclear wastes, and Nano pollutants, which contain heavy metals, affect the performance and flexibility of soil ecosystems, microorganisms, and plants. It also pollutes surface water, groundwater and the food chain. The aim of this study was to investigate the phytoremediation potential of heavy metals from soil by Vetiver and the effect of these metals on plant morphological changes in greenhouse conditions. Soil contamination with heavy metals has become a worldwide concern. This research was conducted as a factorial design with four different heavy metals (lead, cadmium, manganese and nickel) with three varying levels and also three replications for each treatment. The results of analysis of variance, Duncan test, showed that the effect of applied treatments on lead uptake in roots and shoots increased significantly (P ≤ 0.05) with increasing levels of treatments. The biological concentration factor was more than one, and the transfer factor was close to one. Therefore, it can be used as a phytostablization plant. Also, with different levels of heavy metal treatments, the highest average height of total plants was related to lead, manganese, nickel and cadmium treatments with values of 167.54, 166.66, 165.85 and 163.88cm, respectively. The highest average root roots of plants were related to lead, manganese, nickel and cadmium treatments with values of 42.27, 42.36, 41.85 and 41.61 Cm, respectively. The highest average root roots of plants were related to the treatments of lead, manganese, nickel and cadmium with values of 125.28, 124.29, 124.02 and 121.68 Cm, respectively. Therefore, among all treatments, plants treated with cadmium had the lowest growth. The results showed that Vetiver can be considered as a refining plant due to its vegetative characteristics, cost-effectiveness and high adaptation to environmental conditions.},
     year = {2022}
    }
    

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  • TY  - JOUR
    T1  - Vetiver Morphological Changes Under the Influence of Phytoremediation and Absorption of Heavy Metals
    AU  - Fourud Gravand
    AU  - Seyedeh Aghileh Hejazi
    Y1  - 2022/04/20
    PY  - 2022
    N1  - https://doi.org/10.11648/j.ijec.20220601.12
    DO  - 10.11648/j.ijec.20220601.12
    T2  - International Journal of Environmental Chemistry
    JF  - International Journal of Environmental Chemistry
    JO  - International Journal of Environmental Chemistry
    SP  - 7
    EP  - 27
    PB  - Science Publishing Group
    SN  - 2640-1460
    UR  - https://doi.org/10.11648/j.ijec.20220601.12
    AB  - Today, human activities such as pesticides, fertilizers, industrial and nuclear wastes, and Nano pollutants, which contain heavy metals, affect the performance and flexibility of soil ecosystems, microorganisms, and plants. It also pollutes surface water, groundwater and the food chain. The aim of this study was to investigate the phytoremediation potential of heavy metals from soil by Vetiver and the effect of these metals on plant morphological changes in greenhouse conditions. Soil contamination with heavy metals has become a worldwide concern. This research was conducted as a factorial design with four different heavy metals (lead, cadmium, manganese and nickel) with three varying levels and also three replications for each treatment. The results of analysis of variance, Duncan test, showed that the effect of applied treatments on lead uptake in roots and shoots increased significantly (P ≤ 0.05) with increasing levels of treatments. The biological concentration factor was more than one, and the transfer factor was close to one. Therefore, it can be used as a phytostablization plant. Also, with different levels of heavy metal treatments, the highest average height of total plants was related to lead, manganese, nickel and cadmium treatments with values of 167.54, 166.66, 165.85 and 163.88cm, respectively. The highest average root roots of plants were related to lead, manganese, nickel and cadmium treatments with values of 42.27, 42.36, 41.85 and 41.61 Cm, respectively. The highest average root roots of plants were related to the treatments of lead, manganese, nickel and cadmium with values of 125.28, 124.29, 124.02 and 121.68 Cm, respectively. Therefore, among all treatments, plants treated with cadmium had the lowest growth. The results showed that Vetiver can be considered as a refining plant due to its vegetative characteristics, cost-effectiveness and high adaptation to environmental conditions.
    VL  - 6
    IS  - 1
    ER  - 

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Author Information
  • Department of Environment, Islamic Azad University, Tonekabon Branch, Tonekabon, Iran

  • Department of Environment, Islamic Azad University, Lahijan Branch, Lahijan, Iran

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