Please cite this article in press as: Y. Ma, et al., Improvement of plant growth and nickel uptake by nickel resistant-plant-growth promoting
bacteria, J. Hazard. Mater. (2009), doi:10.1016/j.jhazmat.2008.12.018
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HAZMAT-9242; No. of Pages 8
Journal of Hazardous Materials xxx (2009) xxx–xxx
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Journal of Hazardous Materials
journal homepage: www.elsevier.com/locate/jhazmat
Improvement of plant growth and nickel uptake by nickel
resistant-plant-growth promoting bacteria
Ying Ma
∗
, Mani Rajkumar, Helena Freitas
Centre for Functional Ecology, Department of Botany, University of Coimbra, Coimbra 3000, Portugal
article info
Article history:
Received 14 July 2008
Received in revised form
10 November 2008
Accepted 2 December 2008
Available online xxx
Keywords:
PGPB
Nickel
Siderophores
IAA
Phytoremediation
abstract
In this study, among a collection of Ni-resistant bacterial strains isolated from the rhizosphere of Alyssum
serpyllifolium and Phleum phleoides grown on serpentine soil, five plant growth-promoting bacteria (PGPB)
were selected based on their ability to utilize 1-aminocyclopropane-1-carboxylate (ACC) as the sole N
source and promote seedling growth. All of the strains tested positive for indole-3-acetic acid (IAA)
production and phosphate solubilization. In addition, four of the strains exhibited significant levels
of siderophores production. Further, the efficiency of PGPB in enhancing Ni solubilization in soils was
analyzed. Compared with control treatment, inoculation of PGPB strains significantly increased the con-
centrations of bioavailable Ni. Furthermore, a pot experiment was conducted to elucidate the effects of
inoculating Ni-resistant PGPB on the plant growth and the uptake of Ni by Brassica juncea and B. oxyrrhina
in soil contaminated with 450 mg kg
-1
Ni. Psychrobacter sp. SRA2 significantly increased the fresh (351%)
and dry biomass (285%) of the B. juncea test plants (p < 0.05), whereas Psychrobacter sp. SRA1 and Bacillus
cereus SRA10 significantly increased the accumulation of Ni in the root and shoot tissues of B. juncea
compared with non-inoculated controls. This result indicates that the strains SRA1 and SRA10 facilitated
the release of Ni from the non-soluble phases in the soil, thus enhancing the availability of Ni to plants.
A significant increase, greater than that of the control, was also noted for growth parameters of the B.
oxyrrhina test plants when the seeds were treated with strain SRA2. This effect can be attributed to the
utilization of ACC, solubilization of phosphate and production of IAA. The results of the study revealed
that the inoculation of Ni mobilizing strains Psychrobacter sp. SRA1 and B. cereus SRA10 increases the effi-
ciency of phytoextraction directly by enhancing the metal accumulation in plant tissues and the efficient
PGPB, Psychrobacter sp. SRA2 increases indirectly by promoting the growth of B. juncea and B. oxyrrhina.
© 2008 Elsevier B.V. All rights reserved.
1. Introduction
Heavy metal pollution of soils is becoming one of the most severe
environmental hazards and has negative impact on human health
and agriculture. Elevated levels of heavy metals not only decrease
soil microbial activity, soil fertility and yield losses [1], but also
threaten human health through the food chain [2]. Phytoextraction
is emerging as a potential cost effective solution for the remediation
of heavy metal-contaminated soils in opposition to the conven-
tional chemical and physical remediation technologies that are
generally too costly and often harmful to soil characteristics [3,4].
Some plant species (identified as hyperaccumulators) growing in
heavy metal-contaminated sites have been found with the ability
to accumulate unusually high concentrations of heavy metals with-
out impacting on their growth and development [5]. However, most
hyperaccumulators identified so far are not suitable for field phy-
∗
Corresponding author. Tel.: +351 239 855243; fax: +351 239 855211.
E-mail address: cathymaying@yahoo.com.cn (Y. Ma).
toremediation applications due to their small biomass and slow
growth [6]. Moreover, the metals at elevated levels are generally
toxic to most plants impairing their metabolism and reducing plant
growth. These properties have an adverse impact on the poten-
tial for metal phytoextraction and restrict the employment of this
technology. Thus, the development of phytoremediation strategies
for heavy metal-contaminated soils is necessary. In this regard,
interactions among metals, rhizosphere microbes and plants have
attracted attention because of the biotechnological potential of
microorganisms for metal removal directly from polluted soils or
the possible transfer of accumulated metals to higher plants [7].
Further, the rhizosphere provides a complex and dynamic microen-
vironment where microorganisms, in association with roots, form
unique communities that have considerable potential for plant
growth promotion [8] and detoxification of hazardous waste com-
pounds [9,10]. In addition, certain metal resistant microorganisms
can affect on trace metal mobility and availability to the plants
through release of chelating agents, acidification, phosphate solubi-
lization and redox changes [11,12]. Therefore, improvement of the
interactions between plants and beneficial rhizosphere microbes
0304-3894/$ – see front matter © 2008 Elsevier B.V. All rights reserved.
doi:10.1016/j.jhazmat.2008.12.018