بررسی توانایی گیاه‌پالایی گونه‌های مرتعی به خاک های آلوده به مس و منگنز

نوع مقاله : مقاله پژوهشی

نویسندگان

1 دانش آموخته کارشناسی ارشد دانشکده مهندسی منابع طبیعی و محیط زیست، گروه مرتع و آبخیزداری، دانشگاه آزاد اسلامی واحد علوم و تحقیقات (تهران)

2 دانشکده منابع طبیعی، گروه مهندسی احیا مناطق خشک و کوهستانی، دانشگاه تهران

3 دانشیار دانشکده مهندسی منابع طبیعی و محیط زیست، گروه مرتع و آبخیزداری، دانشگاه آزاد اسلامی واحد علوم و تحقیقات (تهران)

4 بخش تحقیقات حفاظت خاک و آبخیزداری، مرکز تحقیقات و آموزش کشاورزی و منابع طبیعی استان زنجان، سازمان تحقیقات، آموزش و ترویج کشاورزی، زنجان، ایران.

چکیده

این تحقیق با هدف ارزیابی میزان آلودگی خاک­های اطراف مراتع قلعه محمد­علی­خان شهرستان ری (در فاصله 78 کیلومتری جاده تهران-قم) و همچنین شناسایی گونه­های بومی مناسب برای گیاه­­پالایی در خاک­های آلوده به فلزات سنگین مس و منگنز، در قالب طرح کاملاً تصادفی، در دو جهت موافق و مخالف باد غالب اجرا گردید.از خاک، اندام هوایی و زیرزمینی گیاهان مرتعی از 10 سایت اطراف معدن مس جاده قم – جنوب تهران (5 سایت در جهت باد غالب و 5 سایت در خلاف جهت باد غالب) نمونه‌هایی جمع­آوری شد. نمونه­های گیاهان در هر سایت از 3 نقطه مرکزی، گوشه بالا و پایین و در داخل پلات یک­متر­مربعی و نمونه­های خاک از داخل همین پلات­ها از عمق ریشه­دوانی برداشته شدند و غلظت فلزات سنگین (مس و منگنز) توسط دستگاه ICP-OES قرائت گردید. بر طبق نتایج، غلظت فلزات مس و منگنز در مناطق 10 گانه در جهت باد غالب و خلاف جهت باد غالب دارای ‌غلظت‌های متفاوتی بودند. غلظت مس در شاخساره گیاهان (01/2) در هر دو جهت باد بیش‌تر از اندام‌های زیرزمینی (19/1) بود. به عبارتی، فاکتور انتقال در ارتباط با فلز مس بزرگتر از یک بود.این امر نشان می‌دهد که به احتمال زیاد بتوان این گیاهان را به عنوان بیش‌اندوز مس در نظر گرفت. بنابراین، این گیاهان بومی دارای توانایی گیاه­پالایی در خاک­های مراتع منطقه بودند.

کلیدواژه‌ها

موضوعات


عنوان مقاله [English]

Investigation of Phytoremediation Ability of Rangeland Species in Soils Contaminated with Copper and Manganese

نویسندگان [English]

  • tahmineh sahihi 1
  • mohammad Jafari 2
  • seyed akbar Javadi 3
  • Mohammad Tahmoures 4
1 Graduate student of Faculty of Natural Resources and Environmental Engineering, Department of Rangeland and Watershed Management, Islamic Azad University, Science and Research Branch (Tehran).
2 Department of Reclamation of Arid and Mountainous Regions, Natural Resources Faculty, University of Tehran, Karaj, Iran.
3 Associate Professor, Faculty of Natural Resources and Environmental Engineering, Department of Rangeland and Watershed Management, Islamic Azad University, Science and Research Branch (Tehran).
4 Soil Conservation and Watershed Management Department, Zanjan Agricultural and Natural Resources Research Center, AREEO, Zanjan, Iran.
چکیده [English]

This study was carried out to evaluate the amount of soil contamination in Qaleh Mohammad-Ali-Khan (Ray city) rangelands and also to identify the phytoremediation ability of native species in soil contaminated with copper (Cu) and manganese (Mn) based on a completely randomized design in the dominant and opposite wind direction. Soil samples, shoot and root samples of rangeland plants were collected from 10 sites around the mine (5 sites in the dominant wind direction and 5 sites in the opposite wind direction). Soil and plant samples were extracted by oxidation method and the copper and manganese concentrations were analyzed by ICP.Concentrations of heavy metals of Cu and Mn in the direction and opposite direction of the dominant wind have different concentrations, so that the plots located near the mine have a higher concentration of heavy metals. Cu concentration in the shoots of plants (2.01) in both direction was greater than that of the roots (1.19) that means the TF value was greater than one (TF>1). Therefore, they can be an appropriate choice for the phytoremediation of Cu-contaminated soils. Thus, these native plants have an implication of carrying out phytoremediation in the rangeland soils.

کلیدواژه‌ها [English]

  • Soil contamination
  • Heavy metals
  • Phytoremediation
  • rangeland species
Abdel-Salam, A. A., Salem, H. M., Abdel-Salam, M. A., & Seleiman, M. F. (2015). Phytochemical removal of heavy metal-contaminated soils Heavy metal contamination of soils (pp. 299-309): Springer.
Adelekan, B. A., & Alawode, A. O. (2011). Contributions of municipal refuse dumps to heavy metals concentrations in soil profile and groundwater in Ibadan Nigeria. Journal of Applied Biosciences, 40, 2727-2737.
Adriano, D. C. (2001). Chapter 10 Lead. Trace Elements in Terrestrial Environments: Biogeochemistry, Bioavailability, and Risks of Metals Springer-Verlag.
Alloway, B. J. (1990). Soil processes and the behaviour of metals. Heavy metals in soils., 7-28.
Alloway, B.  J. (2012). Heavy metals in soils: trace metals and metalloids in soils and their bioavailability (Vol. 22): Springer Science & Business Media.
Aman, M. S., Jafari, M., Karimour Reihan, M., and Motesharezade, B., (2018). Assessing some shrub species for phytoremediation of soils contaminated with lead and zinc. Environmental earth sciences. 77, 82.
Asadi Ghalehni, H., Poozesh, V., (2018). Effect of Sulfur Application on Growth, Photosynthetic Pigments, Antioxidant Activity and Arsenic Accumulation in Coriander (Coriandrum sativum) under Arsenic Stress. Journal of Chemical Health Risks. 8, 265-276.
Baker, A. J. M., & Brooks, R. (1989). Terrestrial higher plants which hyperaccumulate metallic elements. A review of their distribution, ecology and phytochemistry. Biorecovery.1(2), 81-126.
Buszewski, B., Jastrzębska, A., Kowalkowski, T., & Górna-Binkul, A. (2000). Monitoring of selected heavy metals uptake by plants and soils in the area of Toruń, Poland. Pol. J. Environ. Stud9(6), 511-515.
Dalvand, M., & Hamidian, A. (2014). Investigating the Effects of Cu, Pb, Zn and Mn Concentrations in Artemisia spp. Above Ground Biomass in the Rangelands of Darreh Zereshk Copper Mine-Taft. Rangeland, 8(3), 219-229.
Farzamisepehr, M., Norozi, H. A. F., Farajzadeh, MA. (2013). phytoremediation Potential of Polypogon Monsepeliensis L. in Remediation of Petroleum Polluted Soil.
 Fazeli, M, & Osanloo, M. (2014). Mine Facility Location Selection in Open-Pit Mines Based on a New Multistep-Procedure Mine Planning and Equipment Selection (pp. 1347-1360): Springer.
Gaida, M. M., Landoulsi, N. R., Rejeb, M. N., & Smiti, S. (2013). Growth and photosynthesis responses of Rosmarinus officinalis L. to heavy metals at Bougrine mine. African Journal of Biotechnology, 12(2).
Ghosh, M., & Singh, SP. (2005). A review on phytoremediation of heavy metals and utilization of it’s by products. Asian J Energy Environ, 6(4), 18.
Golchin, A. and Shafiei, S (2006). Investigating the Impact of Zanjan Lead and Zinc Factories on Heavy Metal Pollution of Crops and Orchards, Soil Conference, Environment and Sustainable Development, Karaj, Tehran University of Agriculture and Natural Resources. (In Farsi)
Gupta, D. K., Vandenhove, H., & Inouhe, M. (2013). Role of phytochelatins in heavy metal stress and detoxification mechanisms in plants Heavy metal stress in plants (pp. 73-94): Springer.
Harada, H., Kurauchi, M., Hayashi, R., & Eki, T. (2007). Shortened lifespan of nematode Caenorhabditis elegans after prolonged exposure to heavy metals and detergents. Ecotoxicology and environmental safety66(3), 378-383.
Huat, B. G. T. (2017). Effect of Manganese and Cadmum on Biological Attributes of Wild Water Spinach  (Ipomoea aquatica Forssk.).
Irani, M., et al., (2010). Leaves antimicrobial activity of Glycyrrhiza glabra L. Iranian journal of pharmaceutical research: IJPR. 9, 425.
Jiang, J., Wang, J., Liu, S., Lin, C., He, M., & Liu, X. (2013). Background, baseline, normalization, and contamination of heavy metals in the Liao River Watershed sediments of China. Journal of Asian Earth Sciences73, 87-94.
Karkanis, A., Martins, N., Petropoulos, S. A., and Ferreira, I.C.F.R., (2018). Phytochemical composition, health effects, and crop management of liquorice (Glycyrrhiza glabra L.): Α medicinal plant. Food reviews international. 34, 182-203.
National Risk Management Research Laboratory (US). (2000). Introduction to phytoremediation. National Risk Management Research Laboratory, Office of Research and Development, US Environmental Protection Agency.
McGrath, S. P., & Zhao, F. J. (2003). Phytoextraction of metals and metalloids from contaminated soils. Current opinion in biotechnology14(3), 277-282.
Maleki, T., Akhani, H. (2018). Ethnobotanical and ethnomedicinal studies in Baluchi tribes: A case study in Mt. Taftan, southeastern Iran. Journal of ethnopharmacology. 217, 163-177.
Moameri, M., Jafari, M., Tavili, A., Motasharezadeh, B., & Zare Chahouki, MA. (2017). Rangeland plants potential for phytoremediation of contaminated soils with lead, zinc, cadmium and nickel (case study: Rangelands around National Lead & Zinc Factory, Zanjan, Iran). Journal of Rangeland Science, 7(2), 160-171.
Moosavi, S. Gh, & Seghatoleslami, M. J. (2013). Phytoremediation: a review. Advance in Agriculture and Biology, 1(1), 5-11.
Motesharezadeh, B. & Gh.R. Savabeghi., 2015. Phytoremediation or Green Purification. University of Tehran Press. 223 p (In Farsi).
Nouri, J., Lorestani, B., Yousefi, N., Khorasani, N., Hasani, A. H., Seif, F., & Cheraghi, M. (2011). Phytoremediation potential of native plants grown in the vicinity of Ahangaran lead–zinc mine (Hamedan, Iran). Environmental Earth Sciences62(3), 639-644.
Papafilippaki, A. K., Kotti, M. E., & Stavroulakis, G. G. (2008). Seasonal variations in dissolved heavy metals in the Keritis River, Chania, Greece. Global nest. The international journal10(3), 320-325.
Saba, G., Parizanganeh, AH., Zamani, A., & Saba, J. (2015). Phytoremediation of Heavy Metals Contaminated Environments: Screening for Native Accumulator Plants in Zanjan-Iran. International Journal of Environmental Research, 9(1), 309-316.
Sekabira, K., Oryem–Origa, H., Mutumba, GB., & Basamba, TA. (2011). Heavy metal phytoremediation by Commelina benghalensis (L) and Cynodon dactylon (L) growing in urban stream sediments.
Serbaji, MM., Azri, C., & Medhioub, K. (2012). Anthropogenic contributions to heavy metal distributions in the surface and sub-surface sediments of the northern coast of Sfax, Tunisia. International Journal of Environmental Research, 6(3), 613-626.
Tavili, A., Jahantab, E., Jafari, M., Motesharezade, B., Zarghan, N., Saffari Amman, M. (2019). Assessment of TPH and nickel contents associated with tolerant native plants in petroleum-polluted area of Gachsaran, Iran. Arabian Journal of Geosciences. 12, 325.
Vodyanitskii, Yu N. (2016). Standards for the contents of heavy metals in soils of some states. annals of agrarian science, 14(3), 257-263.
Yanqun, Z., Yuan, L., Schvartz, C., Langlade, L., & Fan, L. (2004). Accumulation of Pb, Cd, Cu and Zn in plants and hyperaccumulator choice in Lanping lead–zinc mine area, China. Environment International30(4), 567-576.
Yari Moghadam N., Cheraghi, M., Hasani, AH., & Javid, AH. (2013). Evaluation of heavy metals (Cu, Zn, Pb and Cd) in Hamadan Abshine River. Journal of Health and Development; 2(4): 296-304. (In Farsi).
Yoon, J., Cao, X., Zhou, Q., & Ma, L. Q. (2006). Accumulation of Pb, Cu, and Zn in native plants growing on a contaminated Florida site. Science of the total environment, 368(2-3), 456-464.
Zheljazkov, V. D., Jeliazkova, E. A., Kovacheva, N., & Dzhurmanski, A. (2008). Metal uptake by medicinal plant species grown in soils contaminated by a smelter. Environmental and experimental botany, 64(3), 207-216.