با همکاری انجمن علمی منظر ایران

نوع مقاله : مقالات پژوهشی

نویسندگان

1 گروه گیاهان دارویی، دانشکده گیاهان و مواد اولیه دارویی، دانشگاه شهید بهشتی تهران، تهران، ایران

2 گروه تولیدات گیاهی، دانشکده کشاورزی بردسیر، دانشگاه شهید باهنر کرمان، کرمان، ایران

چکیده

آلودگی به فلزات سنگین یکی از معضلات اصلی زیست‌محیطی و کشاورزی در دهه­های اخیر است. مطالعه حاضر به بررسی پاسخ­های رشدی و بیوشیمیایی گیاه دارویی مرزنجوش بستانی (Origanom marjoram) در برابر تنش عناصر سنگین کادمیوم و سرب پرداخته است. این مطالعه در طرح فاکتوریل و در قالب بلوک کامل تصادفی با چهار تکرار در گلخانه دانشگاه شهید باهنر مرکز آموزش عالی کشاورزی بردسیر در سال 1400 انجام شد. فاکتور اول شامل کادمیوم در چهار سطح (صفر، 6، 12 و 24 میلی ­گرم در کیلوگرم خاک) و فاکتور دوم شامل سرب در چهار سطح ( صفر، 150، 300 و 450 میلی­ گرم در کیلوگرم خاک) در نظر گرفته شد. وزن خشک اندام هوایی و ریشه، غلظت سرب و کادمیوم در اندام هوایی و ریشه، پراکسیداسیون لیپیدها (MDA)، فلاونوئید، آنتوسیانین، فنول کل، پرولین، پروتئین، آنتی‌اکسیدانت­های آنزیمی شامل، گایاکول پراکسیداز (GPX)، آسکوربات پراکسیداز (APX) و کاتالاز (CAT) اندازه‌گیری شدند. نتایج تجزیه واریانس نشان داد که کلیه صفات مذکور تحت تأثیر اثرات ساده سرب و کادمیوم قرار گرفتند. اثر متقابل کادمیوم × سرب روی پرولین، پروتئین، GPX، پلی فنل، فلاونوئید و آنتوسیانین معنی‌دار نبود. وزن خشک اندام هوایی و ریشه در حضور کادمیوم و سرب کاهش و غلظت عناصر سرب و کادمیوم، افزایش پیدا کرده است، بااین‌حال، این آسیب در حضور کادمیوم بیشتر از سرب بود. حضور کادمیوم در محیط حاوی سرب اثر بازدارندگی در جذب سرب توسط گیاه داشت و بالعکس. بیشترین میزان MDA در ترکیب غلظت سرب 450 و کادمیوم 24 میلی­ گرم بر کیلوگرم گزارش شد. بررسی فعالیت سه آنزیم نشان داد که حداکثر فعالیت آنزیم کاتالاز در ترکیب کادمیوم 6 و سرب 450 میلی­ گرم بر کیلوگرم به‌میزان 0/066 و کمترین آن در شاهد 27/0 واحد جذب بر گرم وزن تر بود. همچنین، بیشترین فعالیت APX در ترکیب غلظت 24 کادمیوم و صفر سرب 3/21 و کمترین آن در شاهد 0/97 واحد جذب بر گرم وزن تر گیاه گزارش شد. استفاده از کادمیوم و سرب در بالاترین سطح مصرفی نسبت به شاهد، به‌ترتیب سبب افزایش فعالیت GPX به‌میزان 204 و 40 درصد گردید. در بررسی فنول کل، فلاونوئید و آنتوسیانین و پروتئین، با افزایش غلظت کادمیوم از صفر به 24 میلی­ گرم بر کیلوگرم، به‌ترتیب 52، 42، 208 و 81 درصد و برای پروتئین 39 درصد کاهش نشان داد. این صفات با افزایش سرب از صفر به 450، به‌ترتیب، 14، 14، 58 و 40 درصد افزایش و برای پروتئین 24 درصد کاهش نشان داد. با توجه به نتایج موجود به نظر می‌رسد که با افزایش عناصر سنگین متابولیت‌های ثانویه افزایش یافته و به دنبال آن مقاومت به فلز سنگین نیز افزایش می­یابد.

کلیدواژه‌ها

موضوعات

عنوان مقاله [English]

Investigating Growth and Biochemical Responses of Marjoram (Origanum majorana) to Cadmium and Lead

نویسندگان [English]

  • Mohammad Bagher Razavinia 1
  • Nasibeh Pourghasemian 2
  • Farzad Najafi 1

1 Department of Agriculture, Medicinal Plants and Drugs Research Institute, Shahid Beheshti, Tehran, Iran

2 Department of Plant Productions, Agricultural Faculty of Bardsir, Shahid Bahonar University of Kerman, Kerman, Iran

چکیده [English]

 
Introduction
Heavy metals, like cadmium, lead, and arsenic, harm air, soil, agriculture, and human health. Plants suffer from reduced growth, chlorophyll production, and enzyme activity due to heavy metal exposure. Reactive oxygen species are produced, damaging biological molecules. However, plants have developed resistance mechanisms, including antioxidant stimulation. Flavonoids, complex compounds in plants, enhance resistance to heavy metals. Medicinal plants, rich in secondary metabolites like flavonoids, phenolic compounds, and alkaloids, show resistance to heavy metals. Origanum majorana as a medicinal plant, contains compounds that contribute to its heavy metal resistance. Based on limited studies, medicinal plants, particularly marjoram, have shown greater resistance to environmental stresses due to their secondary metabolites and the ability to produce uncontaminated essential oils in response to heavy metals like cadmium and lead. This study aimed to investigate the biochemical responses and growth of marjoram plants when exposed simultaneously to cadmium and lead, as well as the mutual effects of these two elements on marjoram behavior.
 
Materials and Methods
A factorial randomized complete block design experiment with four replications was used to study the effect of Cd in four concentrations (0, 6, 12 and 24 mg.kg-1 soil) as well as Pb in four concentrations (0, 150 300 and 450 mg. Kg-1 soil). The concentrations were determined based on previous reports and a preliminary experiment. Soil was prepared with appropriate amounts of cadmium chloride and lead chloride were added according to the desired concentrations. The contaminated soil was then incubated at field capacity moisture for two months. Seeds have been sown in germination trays. Seedlings at the three to four leaf stage were transferred to pots containing the contaminated soil. Plant harvest took place 42 to 52 days after the transfer to pots, specifically when the plants had just entered the flowering stage. The aboveground parts of the plants were harvested separately, and the roots were carefully removed from the soil. Half of the plants were dried at 105 °C for 24 h to determine the dry weight, Pb and Cd concentrations. The other half of the plants were used to measure biochemical traits including flavonoids, anthocyanins, malondialdehyde, protein, proline and some enzymatic antioxidants. The data was analyzed using a two-way analysis of variance (ANOVA), and the means were compared using the LSD test. A significance level of 95% was applied using SAS 9.2.
 
Results and Discussion
In this study, various parameters were measured including the dry weight of aerial parts and roots, concentrations of lead and cadmium in the aerial parts and roots, lipid peroxidation (MDA), flavonoids, anthocyanins, total phenols, proline, protein, and antioxidant enzymes including guaiacol peroxidase (GPX), ascorbate peroxidase (APX), and catalase (CAT). The results of the analysis of variance showed that all the mentioned traits were influenced by the individual effects of lead and cadmium. However, there was no significant interaction between cadmium and lead on proline, protein, GPX, polyphenols, flavonoids, and anthocyanins. The dry weight of aerial parts and roots decreased in the presence of cadmium and lead, while the concentrations of lead and cadmium increased. However, this damage was more pronounced in the presence of cadmium compared to lead. The presence of cadmium in a lead-containing environment had an inhibitory effect on lead uptake by the plant, and vice versa. The highest level of MDA was reported in the combination of lead and cadmium concentrations of 450 and 24 mg/kg, respectively. The analysis of enzyme activity showed that the maximum catalase activity was observed in the combination of 6 and 450 mg/kg of cadmium and lead, respectively, while the minimum activity was found in the control group. Similarly, the highest APX activity was reported in the combination of 24 mg/kg of cadmium and zero lead, while the lowest activity was observed in the control group. The use of cadmium and lead at the highest consumption level compared to the control group resulted in a 204% and 40% increase in GPX activity, respectively. In the analysis of total phenols, flavonoids, anthocyanins, and protein, an increase in cadmium concentration from zero to 24 mg/kg led to a decrease of 52%, 42%, 208%, and 81%, respectively, while protein decreased by 39%. These traits showed an increase of 14%, 14%, 58%, and 40%, respectively, with an increase in lead concentration from zero to 450 mg/kg, while protein decreased by 24%. Based on the results, it appears that the increase in secondary metabolites with the increase in heavy metals has accompanied the plant's response to the prevailing conditions.
 
Conclusion
The study found that both cadmium and lead negatively affect the dry weight of plants, with cadmium having a greater impact. This reduction is particularly noticeable in photosynthesis, pigments, electron transport chain, and energy production. The highest concentrations of lead and cadmium (24-450 mg/kg) show the maximum decrease. As the concentrations of these elements increase in the growth medium, their concentration in the plants also increases. Lead has lower mobility and tends to accumulate in the roots compared to cadmium. Interestingly, the presence of cadmium inhibits the uptake of lead by the plant, and vice versa. This leads to an average inhibition of 39% for lead uptake by cadmium and 35% for cadmium uptake by lead in the aerial parts. The study also observed an increase in secondary metabolites, which act as antioxidants and help the plant cope with the stresses caused by cadmium and lead. These metabolites may also contribute to osmotic regulation along with the increase in proline. Based on these findings, it seems that these plants can be used in green spaces contaminated with moderate to low levels of cadmium and lead, particularly in mining areas.

کلیدواژه‌ها [English]

  • Antioxidant
  • Antocyanin
  • Flavonoid
  • Phenol
  • Proline

©2024 The author(s). This is an open access article distributed under Creative Commons Attribution 4.0 International License (CC BY 4.0).

  • Abdel-Salam, A.A., Salem, H.M., & Seleiman, M.F. (2015). Phytochemical Removal of Heavy Metal-Contaminated Soils. Heavy Metal Contamination of Soils,Chapter 16, pp. 299-309. https://doi.org/10.1007/978-3-319-14526-6_16
  • Aebi, M., Furter, R., & Prand, F. (1984). Structure and function of the TRP3 gene of Saccharomyces cerevisiae: Analysis of transcription, promoter sequence, and sequence coding for a glutamine amidotransferase. Current Genetics, 8, 165-172. https://doi.org/10.1007/BF00417812
  • Alipour Darvari, H., Zare Mayvan, H., & Sharifi, M. (2009). Peroxidase activity in Raphanus sativus and its
  • relationship to the amount of heavy metals in soil. Journal of Science, 1, 35-37.
  • Azizi, M., Tafreshi, G., Mirmistafaei, S. (2015). Breeding of medicinal plants. Publication, Nakhost. 401. (In Persian)
  • Behtash, F., Tabatabaie, S.J., Malakoti, M.H., & Ostan, S. (2015). The effect of Co and Cd on growth, chlorophyll content, photosynthesis, and cadmium concentration in sugar beet. Iranian Journal of Soil Research, 24(1), 32-41.
  • Bermejo, B.A. (1999). Study of illicit cocaine seizure classification by pattern recognition techniques applied to matal data. Journal of Forensic Science, 44(2), 270-274.
  • Chen, S., Wang, Q., Lu, H., Li, J., Yang, D., Liu, J., & Yan, C. (2019). Phenolic metabolism and related heavy metal tolerance mechanism in Kandelia Obovat under Cd and Zn stress. Ecotoxicology and Environmental Safety, 169, 134-143. https://doi.org/:10.1016/j.econv.2018.11.004
  • Castañeda-Ovando, A., Lourdes Pacheco-Hernández, M., Páez-Hernández, M.E., Rodríguez, J.A., & Galán-Vidal, C.A. (2009). Chemical studies of anthocyanins: A review. Food Chemistry, 113, 859–871.
  • Dezi, F., Carbonari, S., & Leoni, G. (2009). A model for the 3D kinematic interaction analysis of pile groups in layered soils. Earthquake Engineering & Structural Dynamics, 38(11),1281-1305
  • Dotaniya, M.L., Rajendiran, S., Coumar, V., Meena, V.D., Saha, J.K., Kundu, S., Kumar, A., & Patra, A.K. (2017). Interactive effect of cadmium and zinc on chromium uptake in spinach grown in Vertisol of Central India. International Journal of Environmental Science and Technology, 15(1), 341-352. https://doi.org/:10.1007/s13762-017-1396-x
  • Fidalgo, F., Freitas, R., Ferreira, R., Pessoa, A.M., & Teixeira, J. (2011). Solanum nigrum L. antioxidant defense system isozymes are regulated transcriptionally and post-translationally in Cd-induced stress. Environmental and Experimental Botany, 72, 312-319. https://doi.org/10.1016/j.envexpbot.2011.04.007
  • Gao, J.Z., Gray, D.B., Motheram, R., & Hussain, M.A. (2000). Importance of inlet air velocity in fluid bed drying of a granulation prepared in a high shear granulator. The AAPS Journal, 1
  • Ghada, M. (2017). Efficacy of some Sudanese medicinal plants extracts to remove heavy metals from water. Australian Journal of Basic and Applied Sciences, 11(3), 51-55.
  • Glick, B.R. (2010). Using soil bacteria to facilitate phytoremediation. Biotechnology Advances, 28(3), 367-374. https://doi.org/10.1016/j.biotechadv.2010.02.001
  • Gonzaga, M.I.S., Santos, J.A.G., & Ma, L.Q. (2006). Arsenic phytoextraction and hyperaccumulation by fern species. Scientia Agricola, 63, 90-101. https://doi.org/10.1590/S0103-90162006000100015
  • Ghorbani, H., Heydari, M., & Ghafari, M. (2016). The effect of different levels of salinity and heavy metals lead and cadmium on the growth of photosynthetic pigments and the amounts of sodium and potassium in spinach. Soil andPlant Interaction, 7(24), 15-23. (In Persian)
  • Heath, R.L., & Packer, L. (1968). Photoperoxidation in isolated chloroplasts. I. Kinetics and stoichiometry of fatty acid peroxidation. Archives of Biochemistry and Biophysics, 125, 189–198. https://doi.org/10.1016/0003-9861(68)90654-1
  • Hernandez, I., Alegre, L., Breusegem, F.V., & Munne-Bosch, S. (2009). How relevant are flavonoids as antioxidants in plants? Trends in Plant Science, 14, 125–132. https://doi.org/10.1016/j.tplants.2008.12.003
  • John, R., Ahmad, P., Gadgil, K., & Sharma, S. (2009). Heavy metal toxicity: Effect on plant growth, biochemical parameters metal accumulation by Brassica juncea International Journal of Plant Production, 3(3), 65-76.
  • Kaur, J., Yadav, S., & Singh, Z. (2012). Orbital dimensions - A direct measurement study using dry skulls. Journal of Academic and Industrial Research, 1(6), 293-295.
  • Keilig, K., & Ludwig-Müller, J. (2009). Effect of flavonoids on heavy metal tolerance in Arabidopsis thaliana Botanical Studies, 50(3), 311.
  • Kováčik, J., Klejdus, B., Hedbavny, J., Štork, F., & Bačkor, M. (2009). Comparison of cadmium and copper effect on phenolic metabolism, mineral nutrients and stress-related parameters in Matricaria chamomilla Plant and Soil, 320-231. https://doi.org/10.1007/s11104-009-9889-0
  • Liu, X., Yang, C., Zhang, L., Li, L., Liu, S., Yu, J., You, L., Zhou, D., Xia, C., Zhao, J., & Wu, H. (2011). Metabolic profiling of cadmium-induced effects in one pioneer intertidal halophyte Suaeda salsa by NMR-based metabolomics. Ecotoxicology, 20, 1422-1431. https://doi.org/10.1007/s10646-011-0699-9
  • Malecka, A., Piechalak, A., Mensinger, A., Hanc, D., Baralkiewicz, D., & Tomaszewska, B. (2012). Antioxidative defense system in Pisum sativum roots exposed to heavy metals (Pb, Cu, Cd, and Zn). Polish Journal of Environmental Studies, 21(6), 1721-1730.
  • Márquez-García, B., Fernández, M.Á., & Córdoba, F. (2009). Phenolics composition in Erica differentially exposed to metal pollution in the Iberian Southwestern Pyritic Belt. Bioresource Technology, 100(1), 446-451. https://doi.org/10.1016/j.biortech.2008.04.070
  • McGrath, S.P., Chaudri, A.M., & Giller, K.E. (1995). Long-term effects of metals in sewage sludge on soils, microorganisms, and plants. Journal of Industrial Microbiology and Biotechnology, 14(2), 94-104. https://doi.org/10.1007/BF01569890
  • Mishra, S., Srivastava, S., Tripathi, R.D., Kumar, R., Seth, C.S., & Gupta, D.K. (2006). Lead detoxification by coontail (Ceratophyllum demersum L.) involves induction of phytochelatins and antioxidant system in response to its accumulation. Chemosphere, 65, 1027-1039. https://doi.org/10.1016/j.chemosphere.2006.03.033
  • Morales, M., & Munné-Bosch, S. (2019). Malondialdehyde: Facts and artifacts. Plant Physiology, 180(3), 1246–1250. https://doi.org/10.1104/pp.19.00405
  • Naderi, N., Mirzamasoumzadeh, B., & Aghaei, A. (2013). Effects of different levels of Lead (Pb) on physiological characteristics of sugar beet. International Journal of Agriculture and Crop Sciences, 5(10), 1154-1157.
  • Nieboer, E., & Richardson, D.H.S. (1980). The replacement of the nondescript term "heavy metals" by a biologically and chemically significant classification of metal ions. Environmental Pollution, 1, 3-26. https://doi.org/10.1016/0143-148X(80)90017-8
  • Pandey, R.K., Herrera, W.A.T., Pendleton, J.W., & Villegas. A.N. (1984). Drought response of grain legumes under irrigation gradient. Agronomy Journal, 76, 557-560.
  • Peter, E., & Gbadegesin, A. (2011). Spatial relationships of urban land use, soils and heavy metal concentrations in Lagos Mainland area. Journal of Applied Science and Environmental Management, 15(2), 391–399. https://doi.org/10.4314/jasem.v15i2.68533
  • Pourghasemian, N., Landberg, T., Ehsanzadeh, P., & Gregerb, M. (2019). Different response to Cd stress in domesticated and wild safflower (Carthamus ). Ecotoxicology and Environmental Safety, 171, 321–328. https://doi.org/10.1016/j.ecoenv.2018.12.052
  • Pourrut, B., Shahid, M., Dumat, C., Winterton, P., & Pinelli, E. (2011). Lead uptake, toxicity, and detoxification in plants. Reviews of Environmental Contamination and Toxicology, 213, 113-136.
  • Rashid, A., Schutte, J., Ulery, A., Deyholos, M.K., Sanogo, S., Lehnhoff, E., & Beck, L. (2023). Heavy metal contamination in agricultural soil: Environmental pollutants affecting crop health. Agronomy https://doi.org/10.3390/13061521
  • Sakihama, Y., Cohen, M.F., Grace, S.C., & Yamasaki, H. (2002). Plant phenolic antioxidant and prooxidant activities: Phenolics-induced oxidative damage mediated by metals in plants. Toxicology, 177(1), 67-80. https://doi.org/10.1016/S0300-483X(02)00196-8
  • Seung, A.B, Taejun, H, Soon-Kil, A., Hara, K, Myung, R., Suk-Chan, L., & Kyung-Hoan, I. (2012). Effects of heavy metals on plant growths and pigment contents in Arabidopsis thaliana .Plant Pathology of Journal, 28(4), 446-452.
  • Sharma, P., Jha, A.B., Dubey, R.S., & Pessarakli, M. (2012). Reactive oxygen species, oxidative damage, and antioxidant defence mechanism in plants under stressful conditions. Journal of Botany, 217037. https://doi.org/10.1155/2012/217037
  • Siddique, M.N.I., & Wahid, Z.A. (2018). Achievements and perspectives of anaerobic co-digestion: A review. Journal of Cleaner Production, 194, 359-371. https://doi.org/10.1016/j.jclepro.2018.05.155
  • Stroinski A, & Kozlowska M. (1997). Cadmium-induced oxidative stress in potato tuber. Acta Societatis Botanicorum Poloniae, 66, 189–195.
  • Taamalli, M., D’Alessandro, A., Marrocco, C., Gevi, F., Timperio, A.M., & Zolla, L. (2015). Proteomic and metabolic profiles of Cakile maritima Sea rocket grown in the presence of cadmium. Molocloar BioSystem, 11, 1096-1109.
  • Wanger, G.J. (1979) Content and vacuole/extra vacuole distribution of neutral sugars, free amino acids, and anthocyanins in protoplast. Plant Physiology, 64, 88-93.
  • Zhao, F.J., & Wang, P. (2020). Arsenic and cadmium accumulation in rice and mitigation strategies. Plant Soil, 446, 1–21. https://doi.org/10.1007/s11104-019-04374-6

 

CAPTCHA Image