Nickel in terrestrial biota: Comprehensive review on contamination, toxicity, tolerance and its remediation approaches
Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g−1 in plants and 75–150 μg g−1 in soil. Litreature review indicates that Ni concent...
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Published in | Chemosphere (Oxford) Vol. 275; p. 129996 |
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Main Authors | , , , , , , , , , , , |
Format | Journal Article |
Language | English |
Published |
England
Elsevier Ltd
01.07.2021
|
Subjects | |
Online Access | Get full text |
ISSN | 0045-6535 1879-1298 1879-1298 |
DOI | 10.1016/j.chemosphere.2021.129996 |
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Abstract | Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g−1 in plants and 75–150 μg g−1 in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg−1 in terrestrial, and 0.2 mg L−1 in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08–0.26 and 0.03–0.16 mg kg−1. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches.
•Nickel can be essential or toxic in terrestrial ecosystem based on its concentration.•Low Ni in plant embryonic tissues ensures high reproductive success.•PGPBs required filed optimization for successful Ni bioremediation.•Short duration low-frequency microwave irradiation enhances seed germination.•Microbes use Ni efflux systems, for regulating Ni toxicity. |
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AbstractList | Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g
in plants and 75-150 μg g
in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg
in terrestrial, and 0.2 mg L
in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08-0.26 and 0.03-0.16 mg kg
. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches. Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g-1 in plants and 75-150 μg g-1 in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg-1 in terrestrial, and 0.2 mg L-1 in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08-0.26 and 0.03-0.16 mg kg-1. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches.Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g-1 in plants and 75-150 μg g-1 in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg-1 in terrestrial, and 0.2 mg L-1 in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08-0.26 and 0.03-0.16 mg kg-1. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches. Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g⁻¹ in plants and 75–150 μg g⁻¹ in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg⁻¹ in terrestrial, and 0.2 mg L⁻¹ in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08–0.26 and 0.03–0.16 mg kg⁻¹. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches. Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in terrestrial biota. In general, the safer limit of Ni is 1.5 μg g−1 in plants and 75–150 μg g−1 in soil. Litreature review indicates that Ni concentrations have been estimated up to 26 g kg−1 in terrestrial, and 0.2 mg L−1 in aquatic resources. In case of vegetables and fruits, mean Ni content has been reported in the range of 0.08–0.26 and 0.03–0.16 mg kg−1. Considering, Ni toxicity and its potential health hazards, there is an urgent need to find out the suitable remedial approaches. Plant vascular (>80%) and cortical (<20%) tissues are the major sequestration site (cation exchange) of absorbed Ni. Deciphering molecular mechanisms in transgenic plants have immense potential for enhancing Ni phytoremediation and microbial remediation efficiency. Further, it has been suggested that integrated bioremediation approaches have a potential futuristic path for Ni decontamination in natural resources. This systematic review provides insight on Ni effects on terrestrial biota including human and further explores its transportation, bioaccumulation through food chain contamination, human health hazards, and possible Ni remediation approaches. •Nickel can be essential or toxic in terrestrial ecosystem based on its concentration.•Low Ni in plant embryonic tissues ensures high reproductive success.•PGPBs required filed optimization for successful Ni bioremediation.•Short duration low-frequency microwave irradiation enhances seed germination.•Microbes use Ni efflux systems, for regulating Ni toxicity. |
ArticleNumber | 129996 |
Author | Cabral-Pinto, M.M.S. Gupta, Dipak Kumar Bhatia, Arti Shabnam, Aftab A. Fagodiya, Ram Kishor Subrahmanyam, Gangavarapu Mondal, Raju Malyan, Sandeep K. Jigyasu, Dharmendra K. Khan, Shakeel A. Chaturvedi, Ashish K. Kumar, Amit |
Author_xml | – sequence: 1 givenname: Amit orcidid: 0000-0002-6073-0860 surname: Kumar fullname: Kumar, Amit organization: School of Hydrology and Water Resources, Nanjing University of Information Science and Technology, Nanjing, Jiangsu, 210044, China – sequence: 2 givenname: Dharmendra K. orcidid: 0000-0003-4916-7437 surname: Jigyasu fullname: Jigyasu, Dharmendra K. email: jigyasudk.csb@gov.in organization: Central Muga Eri Research and Training Institute, Central Silk Board, Jorhat, Assam, 785700, India – sequence: 3 givenname: Amit orcidid: 0000-0003-1956-0174 surname: Kumar fullname: Kumar, Amit email: amitkumar.csb@gov.in organization: Central Muga Eri Research and Training Institute, Central Silk Board, Jorhat, Assam, 785700, India – sequence: 4 givenname: Gangavarapu surname: Subrahmanyam fullname: Subrahmanyam, Gangavarapu email: subrahmanyamg.csb@gov.in organization: Central Muga Eri Research and Training Institute, Central Silk Board, Jorhat, Assam, 785700, India – sequence: 5 givenname: Raju orcidid: 0000-0001-7526-1940 surname: Mondal fullname: Mondal, Raju email: rmcrijaf@yahoo.in organization: Central Sericultural Germplasm Resources Centre (CSGRC), Central Silk Board, Ministry of Textiles, Thally Road, Hosur, Tamil Nadu, 635109, India – sequence: 6 givenname: Aftab A. orcidid: 0000-0001-9355-9126 surname: Shabnam fullname: Shabnam, Aftab A. email: aftab.csb@gov.in organization: Central Muga Eri Research and Training Institute, Central Silk Board, Jorhat, Assam, 785700, India – sequence: 7 givenname: M.M.S. surname: Cabral-Pinto fullname: Cabral-Pinto, M.M.S. email: marinacp@ua.pt organization: Department of Geosciences, Geobiotec Research Centre, University of Aveiro, 3810-193 Aveiro, Portugal – sequence: 8 givenname: Sandeep K. orcidid: 0000-0003-1759-8902 surname: Malyan fullname: Malyan, Sandeep K. email: sandeepkmalyan@gmail.com organization: Research Management and Outreach Division, National Institute of Hydrology, Jalvigyan Bhawan, Roorkee, Uttarakhand, 247667, India – sequence: 9 givenname: Ashish K. orcidid: 0000-0001-9541-0931 surname: Chaturvedi fullname: Chaturvedi, Ashish K. email: ashispc@cwrdm.org organization: Land and Water Management Research Group, Centre for Water Resources Development and Management, Kozhikode, Kerala, 673571, India – sequence: 10 givenname: Dipak Kumar surname: Gupta fullname: Gupta, Dipak Kumar email: deepak.gupta@icar.gov.in organization: ICAR-Central Arid Zone Research Institute Regional Research Station Pali Marwar, Rajasthan, 342003, India – sequence: 11 givenname: Ram Kishor orcidid: 0000-0001-7275-2306 surname: Fagodiya fullname: Fagodiya, Ram Kishor email: ram.iari4874@gmail.com organization: Division of Irrigation and Drainage Engineering, ICAR-Central Soil Salinity Research Institute, Karnal, Haryana, 132001, India – sequence: 12 givenname: Shakeel A. orcidid: 0000-0002-2926-6078 surname: Khan fullname: Khan, Shakeel A. email: shakeel.khan@icar.gov.in organization: Centre for Environment Science and Climate Resilient Agriculture, ICAR-Indian Agricultural Research Institute, New Delhi, 110012, India – sequence: 13 givenname: Arti surname: Bhatia fullname: Bhatia, Arti email: abensc@gmail.com organization: Centre for Environment Science and Climate Resilient Agriculture, ICAR-Indian Agricultural Research Institute, New Delhi, 110012, India |
BackLink | https://www.ncbi.nlm.nih.gov/pubmed/33647680$$D View this record in MEDLINE/PubMed |
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Snippet | Nickel (Ni) has been a subject of interest for environmental, physiological, biological scientists due to its dual effect (toxicity and essentiality) in... |
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SubjectTerms | bioaccumulation Biodegradation, Environmental Bioremediation Biota cation exchange Contamination decontamination food chain Human health Humans Ni essentiality Nickel Nickel - analysis Nickel - toxicity phytoremediation Soil Soil Pollutants - analysis Soil Pollutants - toxicity systematic review Toxicity transportation |
Title | Nickel in terrestrial biota: Comprehensive review on contamination, toxicity, tolerance and its remediation approaches |
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