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 inChemosphere (Oxford) Vol. 275; p. 129996
Main Authors Kumar, Amit, Jigyasu, Dharmendra K., Subrahmanyam, Gangavarapu, Mondal, Raju, Shabnam, Aftab A., Cabral-Pinto, M.M.S., Malyan, Sandeep K., Chaturvedi, Ashish K., Gupta, Dipak Kumar, Fagodiya, Ram Kishor, Khan, Shakeel A., Bhatia, Arti
Format Journal Article
LanguageEnglish
Published England Elsevier Ltd 01.07.2021
Subjects
Online AccessGet full text
ISSN0045-6535
1879-1298
1879-1298
DOI10.1016/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.
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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Keywords Ni essentiality
Human health
Nickel
Bioremediation
Toxicity
Contamination
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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
URI https://dx.doi.org/10.1016/j.chemosphere.2021.129996
https://www.ncbi.nlm.nih.gov/pubmed/33647680
https://www.proquest.com/docview/2495404139
https://www.proquest.com/docview/2524307103
Volume 275
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