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Phytoextraction of copper and lead from spiked soil using Acalypha wilkesiana (Copper leaf) and Polyscias fruticosa (Aralia)

Open access
Durumin Iya, N.I., Assim, Z.B., Omorinoye, O.A., Asare, E.A.·2022·Dutse Journal of Pure and Applied Sciences

Abstract

Soil contaminated with heavy metals industrially or anthropogenically is a major global concern. This study aimed at investigating the potential of Acalypha wilkesiana and Polyscias fruticosa plants to remove copper (Cu) and lead (Pb) from soil spiked with solutions of Cu and Pb. Information on the ability of both plants to uptake and accumulate Cu and Pb from spiked soil is insufficient. Plant cuttings were grown in a 2 kg soil spiked with heavy metals and kept at the greenhouse for the period of 240 days. Root, stem and leaf of the plants were analyzed for Cu and Pb using Atomic Absorption Spectrophotometer (AAS). Cu accumulation (2.58 -542.66 mg/kg) was appreciably higher than Pb accumulation (26.24 - 46.44 mg/kg) in A. wilkesiana, while Cu accumulation ranged 4.54 - 384.19 mg/kg was found to be lower than the Pb accumulation ranged 1.22-759.48 mg/kg in P. fruticosa. The maximum accumulation of Cu and Pb in the shoot were found to be 52.50 and 82.93 mg/kg in A. wilkesiana, while 38.26 and 123.98 mg/kg in P. fruticosa. Accumulation of Cu and Pb by both plants were correlated using the indices bioaccumulation, transfer factor and translocation index. The result is encouraging and suggests that both plants could be applied for phytoextraction of Cu and Pb from heavy metal spiked soil.

Overview

CoChat Summary

TL;DR

A 240-day greenhouse pot study tested *Acalypha wilkesiana* and *Polyscias fruticosa* for phytoextraction of Cu and Pb from spiked soil. Both plants survived and accumulated the metals, but neither met hyperaccumulator thresholds; *A. wilkesiana* removed more Cu (12.15%) and *P. fruticosa* more Pb (3.93%).

Key findings

  • Both species survived and grew in Cu/Pb-spiked soil without chlorosis, necrosis, or leaf death. Cu was mainly retained in roots (shoot/root ratio <1), while Pb was more mobile to shoots (shoot/root ratio >1 except at 60 days).
  • In *A. wilkesiana*, Cu accumulation ranged 2.58–542.66 mg/kg versus Pb 26.24–46.44 mg/kg; maximum shoot Cu and Pb were 52.50 and 82.93 mg/kg. In *P. fruticosa*, Cu ranged 4.54–384.19 mg/kg and Pb 1.22–759.48 mg/kg; maximum shoot Cu and Pb were 38.26 and 123.98 mg/kg.
  • Removal: *A. wilkesiana* removed 6.65–12.15% Cu and 2.27–3.39% Pb; *P. fruticosa* removed 0.98–8.09% Cu and 0.16–3.93% Pb. *A. wilkesiana* had higher bioaccumulation factors for both metals (Cu up to 5.51; Pb up to 7.79) than *P. fruticosa* (Cu up to 2.67; Pb up to 1.13).
  • Neither species was considered a hyperaccumulator: the paper notes a hyperaccumulator should exceed 1000 mg/kg Cu/Pb, and leaf concentrations did not reach the 100 mg/kg threshold for Cu or Pb.

Methods

  • Pot experiment in a greenhouse: top soil from Kuching, Sarawak, Malaysia; 48 polyethylene bags with ~2.0 kg soil each, spiked with Cu and Pb solution; unspiked controls; one cutting per bag; 240 days under 16 h light/22°C, 8 h dark/18°C, 59% humidity.
  • Root, stem, and leaf tissues were separated, dried, ashed, acid-digested, and analyzed for Cu and Pb by AAS; soil was characterized for pH, CEC, moisture, EC, N, P, K, Cu, and Pb.
  • Data analysis calculated transfer factor, translocation index, percentage removal, shoot/root concentration ratio, and bioaccumulation coefficient; plant values are reported as mean (n=3) in the tables.

Limitations

  • Stated by authors: no growth-promoting microorganisms or soil amendments were used; polyethylene bags may have restricted root spread; using more than one metal in the spiking solution may have caused uptake competition. They recommend further tests with single-metal spiked soil, amendments, or growth-promoting bacteria.
  • Evident from the text: this was a greenhouse pot study, not a field trial. Also, some reported values are inconsistent across abstract, conclusion, and tables (e.g., abstract states *A. wilkesiana* maximum shoot Cu of 52.50 mg/kg while Table 3 lists 56.50 mg/kg; conclusion reports *P. fruticosa* root Cu of 384.19 mg/kg while Table 2’s highest root Cu for *P. fruticosa* is 69.58 mg/kg).

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Registry

Crossref · 10.4314/dujopas.v8i2a.18

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Citations

Cites

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Research works printed but not linked: 9

  1. Ariyakanon, N., and Winaipanich, B. (2006). Phytoremediation of copper contaminated soil by Brassica juncea (L.), CZern and Bidens alba (L.) DC. Var. radiate. Journal of Scientific Research, 31(1), 49-56. Association of Official Analytical Chemists (AOAC). (1990). Protein (Crude) determination in animal feed: Copper Catalyst Kjeldahl Method. (984.13) Official Methods of Analysis, 15th Edition.
  2. Bhargava, A., Carmona, F. F., Bhargava, M., and Srivastava, S. (2012). Approaches for enhanced phytoextraction of heavy metals: Review. Journal of Environmental Management, 105, 103-120.
  3. Durumin Iya, N.I., Assim, Z.B., Ipor, I.B., Omolayo, A.O., Umaru, I.J., and Jume, B.H. (2018). Accumulation and translocation of heavy metals by Acalypha wilkesiana parts in the phytoextraction of contaminated soil. Indonesian Journal of Chemistry, 18 (3), 503 -513.
  4. Fati, A. (2011). Phytoremediation of Heavy Metal Contaminated Soil Using Chromolaena odorata and Lantana camara. Thesis of Master Degree. Kwame Nkrumah University of Science and Technology Kumasi.
  5. Grobelak, A., Kacprzak, M., and Fijalkowski, K. (2010). Phytoremediation -the underestimated potential of plants in the environment cleaning up. Journal of Ecology and Health, 14(6), 276-280.
  6. Paiva, H.N., Carvalho, J.G., and Siqueira, J. O. (2002). Translocation index of nutrients in cedro (Cedrela fissilis Vell.) and iperoxo (Tabebuia impetiginosa (Mart.) Standl.) seedlings submitted to increasing levels of cadmium, nickel and lead. Journal of Brazilian Forest Science (Revista Arvore), 26, 467-473.
  7. Paz-Alberto, A. M., Sigua, G. C., BauiB. G., and Prudente, J. A. (2007). Phytoextraction of Lead-Contaminated Soil Using Vetiver grass (Vetiveria zizanioides L.), Cogon grass (Imperata cylindrica L.) and Carabao grass (Pas-palum conjugatum L.). Environmental Science and Pollution Research, 14(7), 498-504.
  8. Rajoo, K. S., Ismail, A., Karam, D. S., and Muharam, F. M. (2016). Phytoremediation Studies on Soils Contaminated with Heavy Metals in Malaysia: A Review Article. American- Eurasian Journal of Agriculture and Environmental Science, 16(8), 1504-1514.
  9. Reynolds, S.G. (1971). The Alafua penetrometer for the measuring soil crust strength. Tropical Agriculture, 48(4), 365-366.

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Metadata

Authors
Durumin Iya, N. I., Assim, Z. B., Omorinoye, O. A., & Asare, E. A.
Affiliations
  • Universiti Malaysia Sarawak (MY)
  • University of Ilorin (NG)
Venue
Dutse Journal of Pure and Applied Sciences
Published
2022-06-25
Volume
8
Issue
2a
Pages
187-196
ISSN
  • 2476-8316 (ISSN-L)
  • 2635-3490
OpenAlex
W4283709491
Cited by
2
References
23
Citations by year
2025: 1 · 2023: 1
FWCI
0.12
Type
journal article
Language
en
Open access
Locations
Dutse Journal of Pure and Applied Sciences (publishedVersion)
Funders
Universiti Malaysia Sarawak
Topics
  • Physical Sciences › Environmental Science › Pollution › Heavy metals in environment
  • Physical Sciences › Chemistry › Analytical Chemistry › Heavy Metals in Plants
  • Physical Sciences › Environmental Science › Water Science and Technology › Heavy Metal Pollution Remediation
Keywords
phytoextraction, copper, lead, heavy metal-contaminated soil, Acalypha wilkesiana, Polyscias fruticosa, metal accumulation in plants, bioaccumulation index, transfer factor, translocation index, phytoremediation

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CoChat. (2026). Citation check: Phytoextraction of copper and lead from spiked soil using Acalypha wilkesiana (Copper leaf) and Polyscias fruticosa (Aralia). https://app.cochat.ai/papers/10.4314/dujopas.v8i2a.18
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Durumin Iya, N. I., Assim, Z. B., Omorinoye, O. A., & Asare, E. A. (2022). Phytoextraction of copper and lead from spiked soil using Acalypha wilkesiana (Copper leaf) and Polyscias fruticosa (Aralia). Dutse Journal of Pure and Applied Sciences. https://doi.org/10.4314/dujopas.v8i2a.18

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