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Bitkilerde Kurşun Toksisitesi ve Kurşun Toleransı

Yıl 2020, Cilt: 3 Sayı: 4, 329 - 339, 01.10.2020

Öz

Doğada kalıcı ve toksik bir kirletici olarak kurşunun canlı organizmalar için bilinen biyolojik bir fonksiyonu olmadığı gibi yüksek kurşun konsantrasyonları bitkiler için zararlıdır. Bitkiler tarafından kök yoluyla alınan kurşunun büyük kısmı köklerde tutulurken çok az bir kısmı bitkinin toprak üstü organlarına taşınır. Böylece kurşunun besin zincirine katılması kısıtlanmış olur. Kurşun bitkilerde aktif oksijen türlerinin birikim hızını artırarak oksidatif strese neden olmaktadır. Sonuçta tohum çimlenmesi, fide büyümesi, proteinler, fotosentez, solunum, mineral madde beslenmesi ve su ilişkileri üzerinde olumsuz etkilere neden olur. Bitkiler kurşunun dokularındaki dağılımını engelleyerek, özellikle vakuollerde depo ederek ve antioksidant sistemin çeşitli bileşenleri ile kurşun toksisitesine karşı tolerans göstermeye çalışır. Bu çalışmada kurşun toksisitesinin bitkilerde neden olduğu metabolik bozukluklar ve tolerans mekanizmaları tartışılmıştır.

Destekleyen Kurum

Sakarya Üniversitesi Bilimsel Araştırma Projeleri Koordinasyon Birimi

Proje Numarası

2011-50-01-026

Kaynakça

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Lead Toxicity and Lead Tolerance in Plants

Yıl 2020, Cilt: 3 Sayı: 4, 329 - 339, 01.10.2020

Öz

As a persistant and toxic pollutant in nature, lead does not have any known biological importance for living things and higher lead concentrations are harmful for plants. Lead enters plants mainly through the roots. A considerable amount of lead is sequestered in the roots while small amount is translocated to the leaves. Thus contamination of the food chain by lead is restricted. Lead causes oxidative stress in plants by accelerating the formation rate of active oxygen species. As a result, it leads to some noxious effects on plants such as germination, seedling growth, proteins, photosynthesis, respiration, mineral nutrition and water relations. Plants try to acquire tolerance by preventing translocation of lead, sequestering it in vacuoles and antioxidant system. In this study, metabolic anomalies caused by lead toxicity and tolerance mechanisms in plants are discussed.

Proje Numarası

2011-50-01-026

Kaynakça

  • Afify DG, Abdel-Satar AM. 2020. Risk assessment of heavy metal pollution in water, sediment and plants in the Nile River in the Cairo region, Egypt. Hydrobiol Studies, 49: 1-12.
  • Alamri SA, Siddiqui MH, Al-Khaishany MYY, Khan MN, Ali HM, Alaraidh IA, Alsahli AA, Al-Rabiah H, Mateen M. 2018. Ascorbic acid improves the tolerance of wheat plants to lead toxicity. J. Plant Int, 13(1): 409-419.
  • Alexander PD, Alloway BJ, Dourado AM. 2006. Genotypic variations in the accumulation of Cd, Cu, Pb and Zn exhibited by six commonly grown vegetables. Environ Pollut, 144: 736–745.
  • Andra SS, Datta R, Sarkar D, Sarkar D, Saminathan SK, Mullens CP, Bach SB. 2009. Analysis of phytochelatin complexes in the lead tolerant vetiver grass [Vetiveria zizanioides (L.)] using liquid chromatography and mass spectrometry. Environ Pollut, 157(7): 2173–2183.
  • Arazi T, Sunkar R, Kaplan B, Fromm H. 1999. A tobacco plasma membrane calmodulin-binding transporter confers Ni2+ tolerance and Pb2+ hypersensitivity in transgenic plants. Plant J, 20: 171–182.
  • Arias JA, Peralta-Videa JR, Ellzey JT, Ren M, Viveros MN, Gardea-Torresdey JL. 2010. Effects of Glomus deserticola inoculation on Prosopis: enhancing chromium and lead uptake and translocation as confirmed by X-ray mapping, ICP-OES and TEM techniques. Environ Exp Bot, 68(2): 139–148.
  • Arshad M, Silvestre J, Pinelli E, Kallerhoff J, Kaemmerer M, Tarigo A, Shahid M, Guiresse M, Pradere P, Dumat C. 2008. A field study of lead phytoextraction by various scented Pelargonium cultivars. Chemosphere, 71(11): 2187–2192.
  • Assche F, Clijsters H. 1990. Effects of metals on enzyme activity in plants. Plant Cell Environ, 13(3): 195–206.
  • Atici Ö, Agar G, Battal P. 2005. Changes in phytohormone contents in chickpea seeds germinating under lead or zinc stress. Biol Plantarum, 49(2): 215–222.
  • Barbosa J, Cabral T, Ferreira D, Agnez-Lima L, Batistuzzo de Medeiros S. 2010. Genotoxicity assessment in aquatic environment impacted by the presence of heavy metals. Ecotoxicol Environ Saf, 73(3): 320–325.
  • Barceló J, Poschenrieder C. 1990. Plant water relations as affected by heavy metal stress: a review. J Plant Nutr, 13(1): 1–37.
  • Barrutia O, Garbisu C, Hernández-Allica J, García-Plazaola JI, Becerril JM. 2010. Differences in EDTA-assisted metal phytoextraction between metallicolous and non-metallicolous accessions of Rumex acetosa L. Environ Pollut, 158(5): 1710–1715.
  • Bi X, Ren L, Gong M, He Y, Wang L, Ma Z. 2010. Transfer of cadmium and lead from soil to mangoes in an uncontaminated area, Hainan Island, China. Geoderma, 155(1–2): 115–120.
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  • Zaier H, Ghnaya T, Ben Rejeb K, Lakhdar A, Rejeb S, Jemal F. 2010. Effects of EDTA on phytoextraction of heavy metals (Zn, Mn and Pb) from sludge-amended soil with Brassica napus. Bioresour Technol, 101(11): 3978–3983.
  • Zhang Y, Deng B, Li Z. 2018. Inhibition of NADPH oxidase increases defense enzyme activities and improves maize seed germination under Pb stress. Ecotoxicol Environ Safety, 158: 187-192.
Toplam 106 adet kaynakça vardır.

Ayrıntılar

Birincil Dil Türkçe
Konular Yapısal Biyoloji
Bölüm Reviews
Yazarlar

Ali Doğru 0000-0003-0060-4691

Proje Numarası 2011-50-01-026
Yayımlanma Tarihi 1 Ekim 2020
Gönderilme Tarihi 15 Ocak 2020
Kabul Tarihi 1 Eylül 2020
Yayımlandığı Sayı Yıl 2020 Cilt: 3 Sayı: 4

Kaynak Göster

APA Doğru, A. (2020). Bitkilerde Kurşun Toksisitesi ve Kurşun Toleransı. Black Sea Journal of Agriculture, 3(4), 329-339.

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