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Vischetti, C.;  Marini, E.;  Casucci, C.;  Bernardi, A.D. Nickel Toxicity Effects on Crop and Soil. Encyclopedia. Available online: https://encyclopedia.pub/entry/33948 (accessed on 01 July 2024).
Vischetti C,  Marini E,  Casucci C,  Bernardi AD. Nickel Toxicity Effects on Crop and Soil. Encyclopedia. Available at: https://encyclopedia.pub/entry/33948. Accessed July 01, 2024.
Vischetti, Costantino, Enrica Marini, Cristiano Casucci, Arianna De Bernardi. "Nickel Toxicity Effects on Crop and Soil" Encyclopedia, https://encyclopedia.pub/entry/33948 (accessed July 01, 2024).
Vischetti, C.,  Marini, E.,  Casucci, C., & Bernardi, A.D. (2022, November 10). Nickel Toxicity Effects on Crop and Soil. In Encyclopedia. https://encyclopedia.pub/entry/33948
Vischetti, Costantino, et al. "Nickel Toxicity Effects on Crop and Soil." Encyclopedia. Web. 10 November, 2022.
Nickel Toxicity Effects on Crop and Soil
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This entry is adapted from the peer-reviewed paper 10.3390/environments9100133

Low or moderate nickel concentrations in soils can cause environmental problems. The main effects of this potentially toxic element on the soil biota and the most common crop species are addressed.

nickel agricultural soils bioremediation

1. Introduction

Ni is an essential micronutrient for several biological functions in plants [1][2] and for selected microorganisms where it participates in various cellular processes [3].
The essentiality of this element for the animal kingdom is debated, as deficiencies rarely occur because it takes little to meet the biological functions; moreover, a metalloenzyme containing Ni has yet to be recovered [4].
Phipps et al. reported that there are no studies on the essentiality of Ni in invertebrates, but it probably acts as an enzymatic cofactor, as observed in vertebrates [5].
This element’s potential toxicity depends on many factors, such as its speciations, the way and time of exposure and concentrations. Different effects could occur at cellular and population levels when it exceeds the optimum intake level in organisms [6].

2. Effects on Crop

Nickel metabolism in plants is essential for some enzyme activities [7], maintaining the proper cellular redox state and various physiological [8] and growth responses [9].
Ni is considered an essential element for the growth of the majority of plant species with low concentrations (0.05–10 mg kg−1 d.w.) [10]; it is involved mainly in nitrogen metabolism, iron uptake and specific enzymatic activities such as urease, hydrogenase and superoxide dismutase [9].
Many authors [11][12][13][14] have studied Ni deficiency in plants, as reported in a recent review [15], but actually, cases of Ni deficiency are unusual in agricultural soils [16].
The critical level of Ni toxicity is higher than 10 mg kg−1 dry mass in sensitive species [17], more than 50 mg kg−1 dry mass in moderately tolerant species [18] and above 1000 mg kg−1 dry mass in Ni-hyperaccumulator plants [19]. Ni above certain limits can induce phytotoxicity at multiple levels [20], altering plants’ structural and anatomical dynamics [2]. However, it is difficult to establish a threshold of Ni concentration in soils that can be potentially toxic for cultivated plants.
Numerous authors have studied the effects of Ni on European crops such as tomato, spinach, oats, barley, wheat and corn. From the experiment conducted in Poland by Matraszek et al. [21] on cherry tomato (Lycopersicon esculentum), it was found that the plant yield (expressed in dry biomass) does not vary at low Ni concentrations (40 mg kg−1), while it decreased significantly at 100 mg kg−1. In another study on tomatoes, 40 mg kg−1 of Ni in the soil affected the plants’ development and yield [22].
Other authors found a strong decrease in cherry tomato yield at lower Ni doses caused by this PTE in plant nutrient media (from 5 to 30 mg L−1). Ni probably causes disturbances and imbalances in the absorption and accumulation of other nutrients [23]. More recently, the impact of Ni on Solanum lycopersicum was measured throughout the antioxidative enzyme ascorbate peroxidase (APX) when Ni was applied at 50 µM and 15 mg L−1 [24][25]. The augmented Ni doses caused a significant increase in APX activity. This effect was also observed in other plants subjected to Ni treatments, such as wheat [26], rice [27] and corn [28].
Poulik [29] studied the toxic effects of Ni on Avena sativa. Ni concentrations of 100 mg kg−1 resulted in yield depression, while doses higher than 150 mg kg−1 caused phytotoxicity and plant mortality. Kumar et al. [30] found that Ni applied to the soil at 10 mg kg−1 increased Hordeum vulgare yield parameters, but a significant reduction was observed beyond this level. Gupta et al. [31] found similar results in three cereal species (wheat, barley and oats) subjected to doses of 0, 2.5, 5, 10, 20 and 40 mg Ni kg−1. These authors found that the yield of all cereals increased significantly at 2.5–5.0 mg Ni kg−1 but decreased at higher levels. In corn plants, Amjad et al. [32] evaluated the mechanisms influencing the growth, physiology and nutrient dynamics after exposure to Ni treatments (0, 20 and 40 mg L−1) in hydroponic conditions. This experiment showed that all the antioxidant enzyme activity tested (SOD, CAT, GR, APX and POX) increased significantly compared to the control after Ni treatments.
Additional experiments [33][34] to test the activity of the antioxidant system in the cells of the spinach plant have shown that Ni doses applied at 50–100 and >25 mg kg−1 caused oxidative stress via increased synthesis of ascorbic acid in plant biomass. The author has suggested that ascorbic acid plays a defensive role in Ni stress.
Works regarding Ni toxicity on plant physiological processes almost always refer to laboratory studies with a contaminated solution at different concentrations [32][35][36], but only a few use contaminated soils, so it is difficult to establish when the soil concentration of Ni could be toxic for cultivated plants.

3. Effects on Soil Microorganisms and Earthworms

Exposure to excessive Ni concentration in soils could strongly affect living organisms such as microorganisms and soil invertebrates. Until now, the responses of soil organisms to long-term Ni pollution under field conditions has remained largely unknown.
Many microbial processes in the soil are altered by Ni presence at different concentrations, and such alterations are often identified by studying the soil enzymatic activities by the microorganisms that inhabit it. For example, in the study by Helaoui et al. [37], the enzymatic activities of the soil (urease, dehydrogenase, β-glucosidase, arylsulfatase, alkaline phosphatase and FDA) significantly decreased compared to the control at a Ni dose of 50 mg kg−1. However, the most negative effect appears at the high concentration of 500 mg kg−1. Similar results regarding enzymatic activities were previously found by Wyszkowska et al. [38], with maximum doses of 400 mg kg−1 of Ni applied.
Regarding the effect of Ni on soil microbial biomass, some studies showed a strong decrease at Ni doses of 100 and 200 mg kg−1 [39][40]. A similar trend was observed up to 250 mg kg−1, although an increase in microbial biomass at the higher dose of 500 mg kg−1 probably indicates an integrated defence system was observed [37].
Several authors have found that soil microbial respiration is stimulated at low Ni concentrations (50–150 mg kg−1) but declines with increasing Ni levels (> 200 mg kg−1) [39][41][42]. This tendency reflects a mechanism of “hormesis”, in which a small concentration of xenobiotics stimulates certain bodily functions [42].
In some neocaledonian soils with high levels of Ni (from 800 to 5000 mg kg−1), Héry et al. [43] found different Ni-resistant bacteria that adapted due to the long-time exposure to these high concentrations. The addition of NiCl2 at 30,000 mg kg−1 to these soils and a reference soil (20 mg kg−1 Ni) had an initial negative effect on bacterial growth, regardless of the soil or population considered, and this result was surprising, as the Caledonian soils had adapted to long-term exposure to high concentrations of Ni. However, the bacterial community of the reference soil was highly disturbed by the addition of Ni, while only a few changes occurred in the bacterial structure (shifts in the genetic profiles) of the neocaledonian soils, suggesting a good adaptation to Ni of these microorganisms.
In recent decades, some studies have been reported the effect of Ni concentrations (low, medium and high) on soil invertebrates such as earthworms. Scott-Fordsmand et al. [44] reported the toxic effects of Ni on the earthworm Eisenia veneta, in sandy-clay soil, at a concentration above 85 mg kg−1. Reproduction and lysosomal membrane stability showed a dose–response relationship and were already altered at 85 mg kg−1, while adult survival was reduced only at concentrations above 245 mg kg−1.
Lock and Janssen [45] examined the chronic toxicity of this metal at different concentrations, in OECD soil, for three soil invertebrates: Eisenia fetida, Folsomia candida and Enchytraesus albidus. At the highest Ni concentration of 1000 mg kg−1, no mortality occurred in E.fetida, while F.candida showed a mortality of 10%, and all E.albidus died. The reproduction test showed a significant effect on cocoons, and juvenile production in E.fetida started to be evident from a concentration of 320 mg kg−1.
E.fetida did not show an increased tolerance toward Ni despite being exposed to elevated levels for more than ten generations: worms exposed to Ni for several years showed an increased sensitivity towards this element [46].
Other authors [47] analysed the effects of the addition of nickel at concentrations ranging from 0 to 1000 mg kg−1 to 13 Chinese soils on growth, cocoon and juvenile production in the earthworm E.fetida. The body weight of E.fetida was insensitive to Ni until 320 mg kg−1, while a significant decrease in growth was observed at 560 and 1000 mg kg−1. Juvenile production, compared to cocoon output, was a more sensitive end-point for Ni, and the two parameters did not show a significant correlation with the properties of the 13 soils studied, probably due to the narrow range of properties of the selected soils.
More recently, a study examined the toxic effect of Ni-spiked farmland at concentrations from 0 to 800 mg kg−1 on E.fetida. A low mortality rate (10%) was observed only in earthworms exposed to the higher dose (800 mg kg−1) on day 14, while the avoidance response reached 100% at this concentration [48].
Depending on the end-point and substrate type, there is a broad range of Ni limit values, evidencing that the soil and substrate characteristics greatly influence Ni’s availability and toxicity [40][49][50], as well as those of other PTEs [51].

References

  1. Brown, P.H.; Welch, R.M.; Cary, E.E. Nickel: A Micronutrient Essential for Higher Plants. Plant Physiol. 1987, 85, 801–803.
  2. Shahzad, B.; Tanveer, M.; Rehman, A.; Cheema, S.A.; Fahad, S.; Rehman, S.; Sharma, A. Nickel; Whether Toxic or Essential for Plants and Environment—A Review. Plant Physiol. Biochem. 2018, 132, 641–651.
  3. Mulrooney, S.B.; Hausinger, R.P. Nickel Uptake and Utilization by Microorganisms. FEMS Microbiol. Rev. 2003, 27, 239–261.
  4. Goyer, R.A.; Clarkson, T.W. Toxic Effects of Metals. In Casarett and Doullis Toxicology: The Basic Science of Poisons; Klaassen, C.D., Ed.; Mc-Graw Hill: New York, NY, USA, 2001; Volume 81.
  5. Phipps, T.; Tank, S.L.; Wirtz, J.; Brewer, L.; Coyner, A.; Ortego, L.S.; Fairbrother, A. Essentiality of Nickel and Homeostatic Mechanisms for Its Regulation in Terrestrial Organisms. Environ. Rev. 2002, 10, 209–261.
  6. Begum, W.; Rai, S.; Banerjee, S.; Bhattacharjee, S.; Mondal, M.H.; Bhattarai, A.; Saha, B. A Comprehensive Review on the Sources, Essentiality and Toxicological Profile of Nickel. RSC Adv. 2022, 12, 9139–9153.
  7. Küpper, H.; Kroneck, P.M.H. Nickel in the Environment and Its Role in the Metabolism of Plants and Cyanobacteria. In Nickel and Its Surprising Impact in Nature; John Wiley & Sons: Hoboken, NJ, USA, 2007; Volume 2, ISBN 9780470028131.
  8. Yusuf, M.; Fariduddin, Q.; Hayat, S.; Ahmad, A. Nickel: An Overview of Uptake, Essentiality and Toxicity in Plants. Bull. Environ. Contam. Toxicol. 2011, 86, 1–17.
  9. Gupta, V.; Jatav, P.K.; Verma, R.; Kothari, S.L.; Kachhwaha, S. Nickel Accumulation and Its Effect on Growth, Physiological and Biochemical Parameters in Millets and Oats. Environ. Sci. Pollut. Res. 2017, 24, 23915–23925.
  10. Marschner, H. Mineral Nutrition of Higher Plants, 2nd ed.; Institute of Plant Nutrition University of Hohenheim: Stuttgart, Germany, 1995.
  11. Wood, B.W.; Reilly, C.C.; Nyczepir, A.P. Mouse-Ear of Pecan: A Nickel Deficiency. HortScience 2004, 39, 1238–1242.
  12. Ruter, J.M. Effect of Nickel Applications for the Control of Mouse Ear Disorder on River Birch. J. Environ. Hortic. 2005, 23, 17–20.
  13. Wood, B.W.; Reilly, C.C.; Nyczepir, A.P. Field Deficiency of Nickel in Trees: Symptoms and Causes. Acta Hortic. 2006, 721, 83–97.
  14. Bai, C.; Reilly, C.C.; Wood, B.W. Nickel Deficiency Disrupts Metabolism of Ureides, Amino Acids, and Organic Acids of Young Pecan Foliage. Plant Physiol. 2006, 140, 433–443.
  15. Hassan, M.U.; Chattha, M.U.; Khan, I.; Chattha, M.B.; Aamer, M.; Nawaz, M.; Ali, A.; Khan, M.A.U.; Khan, T.A. Nickel Toxicity in Plants: Reasons, Toxic Effects, Tolerance Mechanisms, and Remediation Possibilities—A Review. Environ. Sci. Pollut. Res. 2019, 26, 12673–12688.
  16. van der Pas, L.; Ingle, R.A. Towards an Understanding of the Molecular Basis of Nickel Hyperaccumulation in Plants. Plants 2019, 8, 11.
  17. Kozlov, M.V. Pollution Resistance of Mountain Birch, Betula Pubescens Subsp. Czerepanovii, near the Copper-Nickel Smelter: Natural Selection or Phenotypic Acclimation? Chemosphere 2005, 59, 189–197.
  18. Bollard, E.G. Involvement of Unusual Elements in Plant Growth and Nutrition. Encycl. Plant Physiol. New Ser. 1983, 15, 695–744.
  19. Kupper, H.; Lombi, E.; Zhao, F.; Wieshammer, G.; Mcgrath, S.P.; Küpper, H. Cellular Compartmentation of Nickel in the HA Alyssum Lesbiacum, Alyssum Bertolonii and Thlaspi Goesingense. J. Exp. Bot. 2001, 52, 2291–2300.
  20. Muhammad, B.H.; Shafaqat, A.; Aqeel, A.; Saadia, H.; Muhammad, A.F.; Basharat, A.; Saima, A.B.; Muhammad, B.G. Morphological, Physiological and Biochemical Responses of Plants to Nickel Stress: A Review. Afr. J. Agric. Res. 2013, 8, 1596–1602.
  21. Matraszek, R.; Szymańska, M.; Chomczyńska, M.; Soldatov, V.S. Productivity and Chemical Composition of Tomato and Cucumber Plants Growing in Nickel-Polluted Soils Fertilized with Biona-312. Commun. Soil Sci. Plant Anal. 2010, 41, 155–172.
  22. Rehman, F.; Khan, F.A.; Irfan, M.; Dar, M.I. Impact of Nickel on the Growth of Lycopersicon Esculentum Var. Navodaya. Int. J. Environ. Sci. 2016, 7, 100–106.
  23. Palacios, G.; Gómez, I.; Carbonell-Barrachina, A.; Navarro Pedreño, J.; Mataix, J. Effect of Nickel Concentration on Tomato Plant Nutrition and Dry Matter Yield. J. Plant Nutr. 1998, 21, 2179–2191.
  24. Kumar, P.; Rouphael, Y.; Cardarelli, M.; Colla, G. Effect of Nickel and Grafting Combination on Yield, Fruit Quality, Antioxidative Enzyme Activities, Lipid Peroxidation, and Mineral Composition of Tomato. J. Plant Nutr. Soil Sci. 2015, 178, 848–860.
  25. Subhani, M.A.; Amjad, M.; Iqbal, M.M.; Murtaza, B.; Imran, M.; Naeem, M.A.; Abbas, G.; Andersen, M.N. Nickel Toxicity Pretreatment Attenuates Salt Stress by Activating Antioxidative System and Ion Homeostasis in Tomato (Solanum Lycopersicon L.): An Interplay from Mild to Severe Stress. Environ. Geochem. Health 2022, 1–20.
  26. Gajewska, E.; Skłodowska, M.; Słaba, M.; Mazur, J. Effect of Nickel on Antioxidative Enzyme Activities, Proline and Chlorophyll Contents in Wheat Shoots. Biol. Plant. 2006, 50, 653–659.
  27. Maheshwari, R.; Dubey, R.S. Nickel-Induced Oxidative Stress and the Role of Antioxidant Defence in Rice Seedlings. Plant Growth Regul. 2009, 59, 37–49.
  28. Baccouch, S.; Chaoui, A.; El Ferjani, E. Nickel-Induced Oxidative Damage and Antioxidant Responses in Zea Mays Shoots. Plant Physiol. Biochem. 1998, 36, 689–694.
  29. Poulik, Z. The Danger of Cumulation of Nickel in Cereals on Contaminated Soil. Agric. Ecosyst. Environ. 1997, 63, 25–29.
  30. Kumar, O.; Singh, S.K.; Singh, A.P.; Yadav, S.N.; Latare, A.M. Effect of Soil Application of Nickel on Growth, Micronutrient Concentration and Uptake in Barley (Hordeum Vulgare L.) Grown in Inceptisols of Varanasi. J. Plant Nutr. 2017, 41, 50–66.
  31. Gupta, V.K.; Kala, R.; Gupta, S.P. Effect of Nickel on Yield and Its Concentration in Some Rabi Crops Grown on Typic Ustipsamment. J. Indian Soc. Soil Sci. 1996, 44, 348–349.
  32. Amjad, M.; Raza, H.; Murtaza, B.; Abbas, G.; Imran, M.; Shahid, M.; Asif Naeem, M.; Zakir, A.; Mohsin Iqbal, M. Nickel Toxicity Induced Changes in Nutrient Dynamics and Antioxidant Profiling in Two Maize (Zea Mays L.) Hybrids. Plants 2020, 9, 5.
  33. Younis, U.; Athar, M.; Malik, S.A.; Shah, H.R.; Mahmood, S. Biochar Impact on Physiological and Biochemical Attributes of Spinach Spinacia Oleracea (L.) in Nickel Contaminated Soil. Glob. J. Environ. Sci. Manag. 2015, 10, 245–254.
  34. Arasimowicz, M.; Wisniowska-Kielian, B.; Niemiec, M. Efficiency of Antioxidative System in Spinach Plants Growing in Soil Contaminated with Nickel. Ecol. Chem. Eng. A 2013, 20, 987–997.
  35. Molas, J. Changes of Chloroplast Ultrastructure and Total Chlorophyll Concentration in Cabbage Leaves Caused by Excess of Organic Ni(II) Complexes. Environ. Exp. Bot. 2002, 47, 115–126.
  36. Nie, J.; Pan, Y.; Shi, J.; Guo, Y.; Yan, Z.; Duan, X.; Xu, M. A Comparative Study on the Uptake and Toxicity of Nickel Added in the Form of Different Salts to Maize Seedlings. Int. J. Environ. Res. Public Health 2015, 12, 15075–15087.
  37. Helaoui, S.; Mkhinini, M.; Boughattas, I.; Alphonse, V.; Giusti-Miller, S.; Livet, A.; Banni, M.; Bousserrhine, N. Assessment of Changes on Rhizospheric Soil Microbial Biomass, Enzymes Activities and Bacterial Functional Diversity under Nickel Stress in Presence of Alfafa Plants. Soil Sediment Contam. 2020, 29, 823–843.
  38. Wyszkowska, J.; Kucharski, J.; Boros-Lajszner, E. Effect of Nickel Contamination on Soil Enzymatic Activity. Plant Soil Environ. 2005, 51, 523–531.
  39. Cai, X.; Qiu, R.; Chen, G.; Zeng, X.; Fang, X. Response of Microbial Communities to Phytoremediation of Nickel Contaminated Soils. Front. Agric. China 2007, 1, 289–295.
  40. Li, J.; Hu, H.W.; Ma, Y.B.; Wang, J.T.; Liu, Y.R.; He, J.Z. Long-Term Nickel Exposure Altered the Bacterial Community Composition but Not Diversity in Two Contrasting Agricultural Soils. Environ. Sci. Pollut. Res. 2015, 22, 10496–10505.
  41. Plekhanova, I.O.; Zarubina, A.P.; Plekhanov, S.E. Ecotoxicological Assessment of Nickel Pollution of Soil and Water Environments Adjacent to Soddy–Podzolic Soil. Mosc. Univ. Soil Sci. Bull. 2017, 72, 71–77.
  42. Xia, X.; Lin, S.; Zhao, J.; Zhang, W.; Lin, K.; Lu, Q.; Zhou, B. Toxic Responses of Microorganisms to Nickel Exposure in Farmland Soil in the Presence of Earthworm (Eisenia Fetida). Chemosphere 2018, 192, 43–50.
  43. Héry, M.; Nazaret, S.; Jaffré, T.; Normand, P.; Navarro, E. Adaptation to Nickel Spiking of Bacterial Communities in Neocaledonian Soils. Environ. Microbiol. 2003, 5, 3–12.
  44. Scott-Fordsmand, J.J.; Weeks, J.M.; Hopkin, S.P. Toxicity of Nickel to the Earthworm and the Applicability of the Neutral Red Retention Assay. Ecotoxicology 1998, 7, 291–295.
  45. Lock, K.; Janssen, C.R. Ecotoxicity of Nickel to Eisenia Fetida, Enchytraeus Albidus and Folsomia Candida. Chemosphere 2002, 46, 197–200.
  46. Maleri, R.A.; Reinecke, A.J.; Reinecke, S.A. A Comparison of Nickel Toxicity to Pre-Exposed Earthworms (Eisenia Fetida, Oligochaeta) in Two Different Test Substrates. Soil Biol. Biochem. 2007, 39, 2849–2853.
  47. Yan, Z.; Wang, B.; Xie, D.; Zhou, Y.; Guo, G.; Xu, M.; Bai, L.; Hou, H.; Li, F. Uptake and Toxicity of Spiked Nickel to Earthworm Eisenia Fetida in a Range of Chinese Soils. Environ. Toxicol. Chem. 2011, 30, 2586–2593.
  48. Wang, G.; Xia, X.; Yang, J.; Tariq, M.; Zhao, J.; Zhang, M.; Huang, K.; Lin, K.; Zhang, W. Exploring the Bioavailability of Nickel in a Soil System: Physiological and Histopathological Toxicity Study to the Earthworms (Eisenia Fetida). J. Hazard. Mater. 2020, 383, 121169.
  49. Bigorgne, E.; Cossu-Leguille, C.; Murtaza, B.; Abbas, G.; Imran, M.; Shahid, M.; Asif Naeem, M.; Zakir, A.; Mohsin Iqbal, M. Genotoxic Effects of Nickel, Trivalent and Hexavalent Chromium on the Eisenia Fetida Earthworm. Chemosphere 2010, 80, 1109–1112.
  50. Liu, Y.-R.; Li, J.; He, J.-Z.; Ma, Y.-B.; Zheng, Y.-M. Different Influences of Field Aging on Nickel Toxicity to Folsomia Candida in Two Types of Soil. Env. Sci. Pollut. Res. 2015, 22, 8235–8241.
  51. Liu, H.; Li, M.; Zhou, J.; Zhou, D.; Wang, Y. Effects of Soil Properties and Aging Process on the Acute Toxicity of Cadmium to Earthworm Eisenia Fetida. Env. Sci. Pollut. Res. 2018, 25, 3708–3717.
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Costantino Vischetti
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Enrica Marini
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Cristiano Casucci
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Arianna De Bernardi
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