The Role of the Vegetative Part in Some Plant Species to Uptake and Accumulate Lead Element from Polluted Air (an Applied Study in Baghdad /Karkh in Iraq)

Authors

  • Noor A. Khayoon Department of Biology, College of Education for Pure Sciences (Ibn- Al-Haitham), University of Baghdad
  • Ibrahim Mahdi A. Al-Salman Department of Biology, College of Education for Pure Sciences (Ibn- Al-Haitham), University of Baghdad

DOI:

https://doi.org/10.30526/36.1.2949

Keywords:

Plant species, Lead, Plant vegetation, Pollution, accumulators

Abstract

The current study was conducted to test the efficiency of the vegetative part (plant leaves) of plant species of shrubs and trees involved in forming semi-artificial vegetation in the city of Baghdad, Karkh, in the uptake and accumulating the lead element that pollutes the air in the city atmosphere. Five plant sampling sites were selected: Al-Kadhimiyah, Al-Mansour, Al-Ma'aml (Al-Salam district), Al-Adl, and Al-Ameriya district intersections (Al-Seklat), and symbols were given (A, B, C, D, E) respectively. The spread and distribution of plants vary in terms of human activities and pollution levels, affecting the five sites that recorded more than 20 species. For a real comparison between plant efficiency and the effect of the nature of the region, species of recurrent and non-recurring shrubs and trees were selected in their presence at the study sites and included (Conocarpus lancifolius, Ziziphus spina christi, Eucalyptus sp., Albizia lebbeck), and non-recurring (Nerium oleander, Dodonaea viscosa, Phoenix dactylifera, Olea europaea, Myrtus communis, Ficus nitida, Citrus aurantium). The study's results showed a variation in the ability of plant species in lead accumulators. The first site of the plants (Conocarpus lancifolius, Ziziphus spina christi, Albizia lebbeck, Eucalyptus sp., Nerium oleander, Dodonaea viscosa, Phoenix dactylifera, Olea europaea, Myrtus communis, Ficus nitida, and Citrus aurantium) was recorded at (0.46, 0.56, 0.36, 0.55, -, 0.68, -, -, 0.33, 0.29, 0.84) respectively. The second site of the same plants was (0.74, below the detection limit, 0.25, 0.57, -, -, 0.16, -, -, 0.31, -) respectively. The third site was (0.95, 0.65, 0.832, 0.831, 0.86, 1.02, -, -, -, 0.436, -, 0.532), respectively. The fourth site was (0.34, 0.95, 0.48, 0.40, -, 0.19, -, -, -, -), respectively. The fifth site was (0.48, 0.50, 0.49, 0.41, -, -, -, 1.45, -, -, -, -) ppm, respectively. The current study was conducted from October 2021 to May 2022

References

Donahue, N.M. Green Chemistry in Practice: Air Pollution and Air Quality. 2018,151-179.

Burroughs Peña, M S.; Rollins, A. Environmental Exposures and Cardiovascular Disease A Challenge for Health and Development in Low- and Middle-Income Countries. Cardiol. Clin., 2017, 35, 71-86.

Mannucci, P. M.; Franchini, M. Health Effects of Ambient Air Pollution in Developing Countries. Int. J. Environ. Res. Public Health, 2017, 14, 9, 1048

WHO. 7 million deaths annually linked to air pollution. Cent. Eur. J. Public Health, 2014, 22, 53–59.

Zhang, M; Pu, J. (2011). Mineral materials as feasible amendments to stabilize heavy metal in polluted urban soils. J. Environ. Sci., 2011, 23(4), 607-615.

Saxena, P. K., Krishnaraj, S., Dan, T., Perras, M. R., and Vettakkorumakankav, N. N. Phytoremediation of heavy metal contaminated and polluted soils, in Heavy Metal Stress in Plants: From Molecules to Ecosystems, eds M. N. V. Prasa and J. Hagemeyer (New York: Springer). 1999, 305–329.

Baudouin, C.; Charveron, M.; Tarroux R.; Gall, Y. Environmental pollutants and skin cancer. Cell Biol. Toxicol., 2002, 18, 5, 341–348.

Radulović, M.; Stanković, S.; Simić, Z.; Radaković, M. and Topuzović, M.The accumulation of metals in Polygonum aviculare L. in area of the Kraljevo city. Kragujevac J. Sci., 2014, 36, 175–184.

Aljewari , A.F.M.; Al-Salman, I.M.A (2022). The effect of human activities in the installation and quality of street dust components in Baghdad city (Applied study in Al-Zafaraniyah sector). Cincinnati, OH, United States,11th -12th April. 2022, AIP Conference Proceedings (ISSN:0094-243X). Accepted.

Khayoon, N.A.; Al-Salman, I.M.A. Variation in ability of recurring plants species in the vegetation to deposit dust in the atmosphere of Baghdad City (applied study in Al-Kurkh site). Cincinnati, OH, United States,11th -12th April. 2022, AIP Conference Proceedings (ISSN:0094-243X). Accepted.

Alhesnawi, A.S.; Al-Salman, I.M.; Najim, A. N. Some physical and chemical characteristic of dust falling on Karbala city-Iraq. J. Eng. Appl. Sci., 2019.14(Speci, issue 6), 9340-9344.

Saeed, M.; Abu Talib, A.; Al Thuwaini, M.N.; Kazem, A.H.; Al-Salman, I.M . Contribute to cleaning the environment by converting waste tires and rubber into rubber polymers. 4th Intern, Confer of the Society for the Protection of Genetic and Environmental Resources, 23-30/7/2016, Arab Republic of Egypt, 2016, Conf, Proce, Book, 480-489.

Jacob, J.M.; Karthik, C.; Saratale, R.G.; Kumar, S.S.; Prabakar, D.; Kadirvelu , K.; Pugazhendhi, A. Biological approaches to tackle heavy metal pollution: A survey of literature. J. Environ. Manag., 2018, 217, 56-70.

Zak, L. The Long-Term Effects of Lead on Human Health. Zota Professional training, Sept, 24, 2020. 5701Shingle Creek Parkway, Suite 500k, Brooklyn Center, MN554305

Kumar, A ; Cabral-Pinto M.M.S. ; Ashish K. C.; Aftab A.; Shabnam, A.A; Subrahmanyam , Mondal, G.; Gupta, D.K.; Malayan, S.; Kumar, S.S.; Khan, S.A.; Yadav, K.K. Lead Toxicity: Health Hazards, Influence on Food Chain, and Sustainable Remediation Approaches. Int. J. Environ. Res. Public Health. 2020, 17, 7, 2179.

Zak, L. The Long-Term Effects of Lead on Human Health. Zota Professional training, Sept, 24, 2020. 5701Shingle Creek Parkway, Suite 500k, Brooklyn Center, MN554305.

Ghelich, S.; Zarinkamar, F.; Niknam, V. Determination of Peroxidase Activity, Total Phenolic and Flavonoid Compounds Due to Lead Toxicity in Medicago sativa L. Adv. Environ. Biol. 2012, 6, 8, 2364-2012.

Ristić, M.; Perić-Grujić, A.; Antanasijević, D.; Ristić, M.;Urošević, M. A. & Tomašević, M.. Plants as monitors of lead air pollution. Pollutant Dis. Remed. Recycl. 2013,4, 387-431.

Norouzi, S. and Khademi, H. Source identification of heavy metals in atmospheric dust using Platanus orientalis L. leaves as bioindicator. Eurasian J. Soil Sci., 2015, 4, 3, 144-152.

Ali, M.; Singh, N.; Shohael, A.; Hahn, E.; Paek, K.-Y. Phenolics metabolism and lignin synthesis in root suspension cultures of Panax ginseng in response to copper stress. Plant Sci. 2006, 171, 1, 146-154.

Louis, H.; Maitera, O.N.; Boro, G and Barminas, J.T. Determination of Total Phenolic Content and Some Selected Metals in Extracts of Moringa oleifera, Cassia tora, Ocimum gratissimum, Vernonia baldwinii and Telfairia occidentalis Plant Leaves. World News Nat. Sci. 2017, 11, 11-18.

Amanat Baghdad. Department of Designs / Department of Jeffery Information). 2022.

Jawad, M.; Sousse, A. Baghdad Map Guide, First Edition - Al-Alamy Press.1958, Baghdad, Iraq.

Haswell, S. J. Atomic absorption spectrometry.1991,529.

JADIA, C.D. & FULEKAR, M.H. Phytoremediation of heavy metals;Recent Techniques. African Journal of Biotechnology, 2009, 8(6),921-928.

Codex Alimentarius, C. General standard for contaminants and toxins in food and feed. Codex stand. 2017, 193-1995. World Health Organization.

Ali, M.H.; Al-Qahtani, K.M. Assessment of some heavy metals in vegetables, cereals and fruits in Saudi Arabian markets. Egypt. J. Aquat. Res.2012, 38, 1, 31-37.

Downloads

Published

20-Jan-2023

Issue

Section

Biology

Publication Dates