Abstract
Microbially-assisted phytoremediation (MAP) is increasingly recognized as the feasible alternative for removing hazardous heavy metals (HMs) from contaminated environments. However, the dynamics of rhizobial-plant interactions during phytoremediation remain unclear. This study investigated the toxicity of some selected heavy metals (Cobalt, Nickel, and Manganese), the potential tolerance of Phaseolus vulgaris grown in the HMs-rich effluents, and the population dynamics of the associated Rhizobia within the Katsina metropolis. After 80 samples of P. vulgaris collected from Lambun Sarki garden were exposed to 10 mL of 0.5-2g/L of Ni and Co and 5-20 g/L Mn, respectively, in mesocosms, and the plants treated with 10 mL HMs solutions daily, for three weeks. Indices of HMs toxicity on seeds and plants (4 and 3, respectively) were monitored in all treatments. Weekly rhizobial counts on Congo Red Yeast Extract Mannitol Agar (CRYEMA) were taken to monitor rhizobial population dynamics. Pure isolates obtained after three iterations were identified biochemically. One-way ANOVA was employed for statistical analyses using AnalyStat (version 1.6.50). Generally, Ni exerts the highest toxicity, with Mn having less toxicity. Average rhizobial counts increased weekly, with high counts obtained in Ni and Mn treatments. However, they did not differ significantly between weeks (p = 0.061). Thus, longer time intervals (>2 weeks) are required to observe significant shifts in population dynamics. Moreover, HMs concentration did not affect the colony counts (p = 1.00). Metabolism profile of the preliminarily identified Rhizobium sp. and Sinorrhizobium melliloti evidenced HMs removal and plant growth promotion ability. The research demonstrated the phytoremediation ability of P. vulgaris and how rhizospheric population dynamics change during phytoremediation and contributed towards understanding HMs impact as environmental stressors on rhizospheric plant-microbe interactions. Future research targeting the hyperaccumulation capacity of the plants and heavy metals tolerance of the identified rhizobia are recommended, as this may help in knowing the BCF, TF, and BAC of the plants as well as the tolerable amount of the heavy metals to the bacteria
Publisher
Umaru Musa YarAdua University Katsina NG
Reference36 articles.
1. Abderrahmane, Z., Hishamuddin, O., Mohd, H. I. & Musihazli, M. (2018). Influence of lead on in vitro seed germination and early radicle development of Acacia auriculiformis Cunn. Ex Benth species. Annual Research & Review in Biology, 28(1), 1-12. https://doi.org/10.9734/ARRB/2018/43393
2. Abubakar, S., Latiff, A., Lawal, I. M., Jagaba, A. H. (2016). Aerobic treatment of kitchen wastewater using sequence batch reactor (SBR) and reuse for irrigation landscape purposes. American Journal of Engineering Research (AJER) 1, 23-31.
3. Ahmad, M.S.A., &Ashraf, M. (2012).Essential roles and hazardous effects of Nickel in plants. Springer, NewYork, 125-167. https://doi.org/10.1007/978-1-4614-0668-6_6
4. Ain, Q., Akhtar, J., Amjad, M., Haq, M.A., Saqib, Z.A. (2016). Effect of Enhanced Nickel Levels on Wheat Plant Growth and Physiology under Salt Stress. Communications in Soil Science and Plant Analysis. 47, 2538-2546. https://doi.org/10.1080/00103624.2016.1254796
5. Al-mamun, M., Poostforush, M., Mukul, S., Parvez, K., & Subhan, A. (2013). Biosorption of As (III) from aqueous solution by Acacia auriculiformis leaves. Iran Computer Science, Engineering & Electrical Engineering 20: 1871-1880.