اثر رقابت و سطوح مس بر وزن خشک گیاهچه و غلظت عناصر مس، فسفر، پتاسیم و منیزیم در لوبیا (Phaseolus vulgaris L.) و تاج‌خروس ریشه‌قرمز (Amaranthus retroflexus L.)

نوع مقاله : مقالات پژوهشی

نویسندگان

1 دانشجوی دکتری رشته علوم علف‌های‌هرز، گروه زراعت و اصلاح نباتات، دانشکده کشاورزی، دانشگاه بوعلی سینا، همدان، ایران

2 دانشیار زراعت، گروه زراعت و اصلاح نباتات، دانشکده کشاورزی، دانشگاه بوعلی سینا، همدان، ایران

چکیده

به منظور درک کافی از میزان جذب عنصر مس و تجمع سایر عناصر توسط گیاه لوبیا و علف­هرز تاج­خروس در غلظت­های مختلف مس، آزمایشی به صورت آب‌کشت (هیدروپونیک)، در گلخانه تحقیقاتی دانشکده کشاورزی دانشگاه بوعلی سینا در سال1395 اجرا شد. فاکتورهای آزمایش شامل غلظت مس در سه سطح 1، 25 و 50 میکرومولار سولفات مس (CuSO4) و مخلوط جایگزینی لوبیا (B) و تاج‌خروس (P) با نسبت­های 100درصد لوبیا+0درصد تاج‌خروس
(1B: 0P)، 75درصد لوبیا+25درصد تاج‌خروس (0.75B: 0.25P)، 50درصد لوبیا+50درصد تاج‌خروس
(0.5B: 0.5P)، 25درصد لوبیا+75درصد تاج‌خروس (0.25B: 0.75P) و 0درصد لوبیا+100درصد تاج‌خروس
(0B: 1P) بود. نتایج نشان داد در غلظت 1 میکرومولار سولفات مس، غلظت پتاسیم در ریشه لوبیا با افزایش تعداد بوته تاج­خروس در نسبت جایگزینی (0.25B: 0.75P) به‌ترتیب به میزان 7 درصد نسبت به کشت خالص لوبیا کاهش و در غلظت 25 و 50 میکرومولار سولفات مس به‌ترتیب به میزان10 و 15 درصد نسبت به کشت خالص لوبیا، افزایش نشان داد. در غلظت 25 میکرومولار سولفات مس، غلظت فسفر و منیزیم در ریشه لوبیا در نسبت جایگزینی 0.25B: 0.75P به‌ترتیب به میزان 17و 18درصد و در غلظت 50 میکرومولار، به میزان 21 و 26 درصد نسبت به کشت خالص لوبیا افزایش یافت. در شرایط فزونی مس، همجواری علف‌هرز تاج­خروس با لوبیا سبب کاهش آلودگی لوبیا به مس و ایجاد تعادل در جذب عناصر ضروری گیاه لوبیا شد. جذب فلز مس توسط علف‌هرز تاج­خروس، سبب بهبود رشد لوبیا تحت شرایط فزونی مس شد. بنابراین مدیریت اکولوژیکی گیاهان تجمع­دهنده فلز مس نظیر تاج‌خروس ریشه‌قرمز در مقابل ریشه‌کن‌کردن این علف‌هرز، در مزارع لوبیای دارای آلودگی مس، راهکار مناسبی می­باشد.

کلیدواژه‌ها


عنوان مقاله [English]

The effects of competition and excessive copper concentration on seedling dry matter and copper, phosphorus, potassium, and magnesium contents in common bean (Phaseolus vulgaris) and redroot pigweed (Amaranthus retroflexus)

نویسندگان [English]

  • Somayeh Bayat 1
  • Goudarz Ahmadvand 2
  • Ali Sepehri 2
1 PhD. Student of Weed Science, Department of Agronomy and Plant Breeding, Bu-Ali Sina University, Hamedan, Iran
2 Associate Professor of Agronomy, Department of Agronomy and Plant Breeding, Bu-Ali Sina University, Hamedan, Iran
چکیده [English]

Introduction
Soil contamination with heavy metals is one of the most serious problems in the agricultural environments. Due to excessive injudicious and unregulated use of agrochemicals such as pesticides, bactericides and fungicides, which contain Cu as an active component, contamination of agricultural soils with Cu is often occurred. In many plant species, excess copper (Cu) toxicity is an important disorder that limits uptake and accumulation of mineral nutrients. The root system of crops in contact with the roots of neighbor plants (crop or weed) has different characteristics in terms of heavy metals adsorption compared to the pure stand of crops. The position of the roots of heavy metal accumulator weeds may affect the absorption of such metals by adjacent crops in infected conditions. The heavy metal accumulator weeds by reducing or evacuating metals from the rhizosphere of the adjacent plants, cause the plants to be immune to the toxicity of metals. Biomass reduction is a dominant effect of copper toxicity in plants. Application of high copper doses (50 and 75 µM) in nutrient solution, decreased the dry weight of common bean plants in comparison with control. Contamination of soil can affect ecological interactions between plants such as the weed-crop competition. Positive plant-plant interactions are expected to be especially beneficial under high abiotic stresses and therefore, the facilitation effects could be enhanced by increasing stress intensity. Weeds possess the ability to accumulate heavy metal and nutrients, in comparison with crops. The role of nurse plants in facilitating plant community has been applied in severe conditions. Metal hyper-accumulator plants have a positive effect on co-occurring species in met al-rich soils. Redroot pigweed (Amaranthus retroflexus L.) is a serious weed, which affects common bean production. Amaranthus retroflexus and Amaranthus spinosus are known as metal accumulators. We hypothesized that in contaminated fields, the effects of heavy metals on crop growth may be modified by the presence of a metal accumulator weed such as redroot pigweed.
 
Materials and Methods
To investigate copper uptake and accumulation of mineral nutrients by common bean in association with redroot pigweed under excessive copper conditions, a factorial experiment based on a completely randomized design with four replications was carried out in a research greenhouse of Bu-Ali Sina University in 2016. Experimental factors were three Cu doses of 1 (control), 25 and 50µM CuSO4 and five replacement intercropping ratios of bean (B) and redroot pigweed (P) (1B: 0P, 0.75B: 0.25P, 0.5B: 0.5P, 0.25B: 0.75P, 0B:1P). The experiment was carried out in a hydroponic condition. 15 days after seedling establishment, the seedlings of both plants were transferred to the hydroponic conditions with a Hoagland solution, and Cu doses were applied in the Hoagland solution. 30 days after growing the plants in above condition, biomass dry weight and concentration of Cu, K, P and Mg in the leaves and roots of both plants as well as copper translocation factor were determined.
 
Results and Discussion
The results showed that under three doses of copper, the highest concentration of copper in bean was obtained in sole crops, and with increasing replacement intercropping ratios of pigweed, the copper concentration was decreased in bean. In pigweed, the highest concentration of copper was observed in 0.75B: 0.25P proportion. At 1µM CuSO4, potassium concentration in the roots and the leaves of bean in 0.25B: 0.75P proportion, was decreased by 7 percentage in comparison with that of the sole crops, and at 25 µM CuSO4, by 10 percentage and at 50 µM CuSO4, by 15 percentage were increased compared to the sole crops, respectively. At 25 µM CuSO4, phosphorus and magnesium concentration in the roots of bean in 0.25B: 0.75P proportion was increased by 17 and 18 percentage, and at 50 µM CuSO4, by 21 and 26 percentage, respectively in comparison with the sole crops, respectively. Association of pigweed to the bean, decreased Cu pollution in bean plants, which could be related to the balance of nutrient elements uptake by bean under excessive copper conditions. Under excessive copper conditions, the higher copper uptake by pigweed, improved the growth of bean.
 
Conclusion
The results of this study showed the facilitative effects of pigweed plant in decreasing the Cu toxicity stress effects to the bean and indicated that pigweed could be as a potential Cu accumulator to improve bean plant growth under the Cu stress. Here we showed that the presence of some heavy met al accumulator plants such as pigweed in common bean farms, might be a useful practice in contaminated soils. In addition, these facilitation effects of such weeds, emphasize ecological management of weeds rather than weed eradication.

کلیدواژه‌ها [English]

  • Heavy metals
  • Nutrient elements
  • Weed
  1. Adrees, M., Ali, S., Rizwan, M., Ibrahim, M., Abbas, F., Farid, M., Zia-ur-rehman, M., Irshad, M.K. and Bharwana, S.A. 2015. The effect of excess copper on growth and physiology of important food crops: overview. Environmental Science Pollution Research 22: 8148-8162.
  2. Arduini, I., Godbold, D.L., and Onnis, A. 1994. Cadmium and copper change root growth and morphology of Pinuspinea and Pinuspineaster seedling. Physiologia Plantarum 92: 675-680.
  3. Ashrafi, A., Zahedi, M., and Soleimani, M. 2015. Effect of co planted purslane (Portulacaoleracea L.) on Cd accumulation by sunflower in different levels of Cd contamination and salinity: a pot study. International Journal of Phytoremediation 17: 853-860.
  4. Barman, S.C., Sahu, R.K., Bhargava, S.K., and Chaterjee, C. 2000. Distribution of heavy metals in wheat, mustard and weed grown in field irrigated with industrial effluents. Bulletin of Environmental Contamination and Toxicology 64: 489-496.
  5. Bigaliev, A., Boguspaev, K., and Znanburshin, E. 2003. Phytoremediation potential of amaranthus sp. for heavy metals contaminated soil of oil production territory. 10th Annual International Petroleum Environmental Conferen. Houston, Al-Farabi Kazakh.
  6. Bouazizi, H., Jouili, H., Geitmann, A., and Ferjani, E.E. 2010. Copper toxicity in expanding leaves of Phaseolusvulgaris L.: Antioxidant enzyme response and nutrient element uptake. Ecotoxicology and Environmental Safety 73: 1304-1308.
  7. Bravin, M.N., Garnier, C., Lenoble, V., Gerard, F., Dudal, Y., and Hinsinger, P. 2012. Root-induced changes in pH and dissolved organic matter binding capacity affect copper dynamic speciation in the rhizosphere. Geochimicaet Cosmochimica Acta 84: 256-268.
  8. Bruce, E.P. 2001. Phytoremediation of Contaminated Soil and Groundwater at Hazardous Waste Sizes. EPA ORD Ground Water Issue, EPA/540/S-01/500.
  9. Brun, L.A., Maillet, J., Hinsinger, P., and Pepin, M. 2001. Evaluation of copper availability to plants in copper-contaminated vineyard soils. Environmental Pollution 111: 293-302.
  10. Callaway, R.M., Brooker, R.W., Choler, P., Kikvidze, Z., Lortie, C.J., Michalet, R., Paolini, L., Pugnaire, F.I., Newingham, B., Aschehoug, E.T., Armas, C., Kikodze, D., and Cook, B.J. 2002. Positive interactions among alpine plants increase with stress. Nature 417: 844-848.
  11. Cambrolle, J., Garcia, J.L., Ocete, R., Figueroa, M.E., and Cantos, M. 2013. Growth and photosynthetic response to copper in wild grapevine. Chemosphere 93: 294-301.
  12. Devi Chinmayee, M., Mahesh, B., Pradesh, S., Mini, I., and Swapna, T.S. 2012. The assessment of phytoremediation potential of invasive weed Amaranthus spinosus L. Applied Biochemistry and Biotechnology 167: 1550-1559.
  13. Dresler, S., Hanaka, A., Bednarek, W., and Maksymeric, W. 2014. Accumulation of low-molecular-weight organic acids in roots and leaf segments of Zea mays plants treated with cadmium and copper. Acta Physiologiae Plantarum 36: 1565-1575.
  14. Gaetke, L.M., and Chow, C.K. 2003. Copper toxicity, oxidative stress, and antioxidant nutrients. Toxicology 189: 147-163.
  15. Gajewska, E., and Sklodowska, M. 2010. Differential effect of equal Copper, Cadmium and Nickel concentration on biochemical reactions in wheat seedlings. Ecotoxicology and Environmental Safety 73: 996-1003.
  16. Galal, T.M., and Shehata, H.S. 2015. Bioaccumulation and translocation of heavy metals by Plantago major L. grown in contaminated soils under the effect of traffic pollution.Ecological Indicators 48: 244-251.
  17. Hall, J.L. 2002. Cellular mechanisms for heavy met al detoxification and tolerance. Journal of Experimental Botany 53: 1-11.
  18. Hoffman, D.W., and Lavy, T.L. 1978. Plant competition for atrazin. Weed Science 26: 94-99.
  19. Horak, M.J., and Loughin, T.M. 2000. Growth analysis of four Amaranthus species. Weed Science 48: 347-355.
  20. Ke, W., Xiong, Z., Chen, S., and Chen, J. 2007. Effect of copper and mineral nutrition on growth, copper accumulation and mineral element uptake in two Rumex japonicus populations from a copper mine and an uncontaminated filed sites. Environmental and Experimental Botany 59: 59-67.
  21. Kopittke, P.M., and Menzies, N.W. 2006. Effect of Cu toxicity on growth of cowpea (Vignaunguiculata). Plant and Soil 279: 287-296.
  22. Kramer, U., Talke, I.N., and Hanikenne, M. 2007. Transition met al transport. FEBS Lett. 581: 2263-2272.
  23. Lequeux, H., Hermans, C., Lutts, S., and Verbruggen, N. 2010. Response to copper excess in Arabidopsis thaliana: Impact on the root system architecture, hormone distribution, lignin accumulation and mineral profile. Plant Physiology and Biochemistry 48: 673-682.
  24. Li, Z.A., Peng, S.L., Rae, D.J., and Zhou, G.Y. 2001. Litter decomposition and nitrogen mineralization of soils in subtropical plantation forests of southern China, with special attention to comparisons between legumes and non- legumes. Plant and Soil 229: 105-116.
  25. Li, N.Y., Li, Z.A., Zhuang, P., Zou, B., and McBirde, M. 2009. Cadmium uptake from soil by maize with intercrops. Water, Air & Soil Pollution 199: 45-56.
  26. Lortie, C.J., and Callaway, R.M. 2006. Re-analysis of meta-analysis: support for the stress-gradient hypothesis. Journal of Ecology 94: 7-16.
  27. Maathuis, F.J.M. 2009. Physiological functions of mineral macronutrient. Current Opinion in Plant Biology 12: 250-258.
  28. Michaud, A.M., Bravin, M.N., Galleguillos, M., and Hinsinger, P. 2007. Copper uptake and phytotoxicity as assessed in situ for durum wheat (Triticum turgidum durum L.) cultivated in Cu- contaminated former vineyard soils. Plant and Soil 298: 99-111.
  29. Mico, C., Recatala, L., Peris, M., and Sanchez, J. 2006. Assessing heavy metal sources in agricultural soils of an European Mediterranean area by multivariate analysis. Chemosphere 65: 863-872.
  30. Oorts, K. 2013. Copper. In: B.J. Alloway (Ed.). Heavy metals in soils. Trace metals and metalloids in soils and their bioavailability. Springer, Dordrecht, pp. 367-394.
  31. Ouzounidou, G., Elefteriou, E.P., and Karataglis, S. 1992. Ecophysiological and ultrastructural effects of copper in Thlaspiochroleucum (Cruciferae). Canadian Journal of Botany 70: 947-957.
  32. Su, D.C., Lu, X.X., and Wong, J.W.C. 2008. Could co-cropping or successive cropping with Cd accumulator oilseed rape reduce Cd uptake of sensitive Chinese cabbage? Practice Periodical of Hazardous Toxic and Radioactive Waste Management 12: 224-228.
  33. Tyler, G. 1976. Heavy metal pollution, phosphatase activity and mineralization of organic phosphorous in forest soil. Soil Biology and Biochemistry 8: 327-332.
  34. Wei, S.H., and Zhou, Q.X. 2006. Phytoremediation of cadmium-contaminated soil by Rorippaglobosa using two-phase planting. Environmental Science and Pollution Research 13: 151-155.
  35. Whiting, S.N., Leake, J.R., McGrath, S.P., and Baker, A.J.M. 2001. Hyper accumulation of Zn by Thlaspi caerulescens can ameliorate Zn toxicity in the rhizosphere of cocropped Thlaspi arvense. Environmental Science & Technology 35: 3237-3241.
  36. Woolhouse, H.W. 1983. Toxicity and tolerance in the responses of plant to metals. In: Q.L. Lange, P.S. Nobel, C.B. Osmond and H. Ziegler (Eds.). Encyclopedia of Plant Physiology 12C. New Series. Springer Verla, Berlin, pp. 245-300.
  37. Wuana, R.A., and Okieimen, F.E. 2011. Heavy Metals in Contaminated Soils: A Review of Sources. Chemistry, Risks and Best Available Strategies for Remediation. ISRN Ecol. Article ID 402647. 20 p.
  38. Xue, J.H., and Fei, Y.X. 2006. Effects of intercropping Cunninghamia lanceolata in tea garden on content and distribution of heavy metals in soil and tea leaves. Journal of Ecology and Rural Environment 22: 71-73.
  39. Zaheer, I.E., Ali, S., Rizwan, M., Fraid, M., Shakoor, M.B., Gill, R.A., Najeeb, U., Iqbal, N., and Ahmad, R. 2015. Citric acid assisted phytoremediation of copper by Brassicanapus L. Ecotoxicology and Environmental Safety 120: 310-317.
  40. Zhao, G.Q., Ma, B.L., and Ren, C.Z. 2007. Growth, gas exchange, chlorophyll fluorescence, and ion content of naked oat in response to salinity. Crop Science 47: 123-131.
  41. Zimdahl, R.L. 2007. Fundamentals of Weed Science. 3rded. Academic Press, CA, USA.
CAPTCHA Image