Copper uptake in Typha latifolia as affected by iron and manganese plaque on the root surface

2001 ◽  
Vol 79 (3) ◽  
pp. 314-320 ◽  
Author(s):  
Z H Ye ◽  
K C Cheung ◽  
M H Wong

The effects of iron (Fe) and manganese (Mn) plaque on the accumulation of copper (Cu) in Typha latifolia L. were investigated under laboratory conditions in nutrient solution cultures. Seedlings with and without Fe plaque on their roots, induced with 15 or 60 µg·mL–1 Fe, were exposed to 0.04, 0.12, or 0.36 µg·mL–1 Cu solutions, and seedlings with and without Mn plaque, induced with 15 or 60 µg·mL–1 Mn, were exposed to 0.12 or 0.36 µg·mL–1 Cu solutions for 24 days, respectively. In all cases, the amount and proportion of Cu adsorbed on the root surface increased with a higher concentration of Cu in the solutions. In the presence of Fe or Mn, T. latifolia adsorbed more Cu and had a higher proportion of Cu on its roots, especially the roots with heavy Mn or Fe plaque. Although more Fe than Mn accumulated on the roots in the form of plaque, the Mn plaque adsorbed more Cu. The data suggest that root plaque can act as a Cu reservoir, depending on the amount of Fe or Mn on the roots and the amount of Cu in the environment.Key words: wetland plant, heavy metal uptake, cattail, iron plaque, manganese plaque.

1981 ◽  
Vol 3 (1-4) ◽  
pp. 139-151 ◽  
Author(s):  
C. R. Lee ◽  
T. C. Sturgis ◽  
M. C. Landin

Author(s):  
Haochun Chi ◽  
Lu Yang ◽  
Wenjing Yang ◽  
Yuanyuan Li ◽  
Ziwu Chen ◽  
...  

The survival of wetland plants in iron, sulfur and heavy metals-rich mine tailing ponds has been commonly attributed to the iron plaque (IP) on the root surface that acts as a protective barrier. However, the contribution of bacteria potentially regulates the iron-sulfur cycle and heavy metal exclusion at the root surface has not been studied in depth, particularly from a microbial ecology perspective. In this study, a pot experiment using Typha latifolia, a typical wetland plant, in non-polluted soil (NP) and tailing soil (T) was conducted. Samples from four zones, comprising non-rhizosphere soil (NR), rhizosphere soil (R) and internal (I) and external (E) layers of iron plaque, were collected from the NP and T and analyzed by 16S rRNA sequencing. Simpson index of the genus level showed greater diversities of bacterial community in the NP and its I zone is the most important part of the rhizosphere. PICRUSt predicted that the I zones in both NP and T harbored most of the functional genes. Specifically, functional genes related to sulfur relay and metabolism occurred more in the I zone in the T, whereas those related to iron acquisition and carbon and nitrogen circulation occurred more in the I zone in the NP. Analysis of dominant bacterial communities at genus level showed highest abundance of heavy metal resistant genus Burkholderia in the E zones in both soils, indicating that heavy metal resistance of Typha latifolia driven by Burkholderia mainly occurred at the external layer of IP. Moreover, many bacterial genera, such as Acidithiobacillus, Ferritrophicum, Thiomonas, Metallibacterium and Sideroxydans, involved in iron and sulfur metabolisms were found in the T and most showed higher abundance in the I zone than in the other zones. This work, as the first endeavor to separate the iron plaque into external and internal layers and investigate the variations of the bacterial communities therein, can provide an insight for further understanding the survival strategy of wetland plants, e.g., Typha latifolia, in extreme environment.


1996 ◽  
Vol 34 (5-6) ◽  
pp. 267-272 ◽  
Author(s):  
Ken Fukushi ◽  
Duk Chang ◽  
Sam Ghosh

The objective of this research was to investigate the feasibility of developing improved activated sludge cultures capable of removing heavy metals. Cystine, peptone, and β-glycerophosphate (BGP) stimulated metal uptake without the significant reduction of culture viability otherwise experienced in the absence of these chemicals. The cystine-peptone-BGP-grown culture exhibited the highest removal of copper and cadmium of 5.67 and 2.53 mM/g protein, respectively.


1999 ◽  
Vol 7 (1) ◽  
pp. 81-90 ◽  
Author(s):  
G. Vallini ◽  
F. Vaccari ◽  
A. Pera ◽  
M. Agnolucci ◽  
S. Scatena ◽  
...  

2003 ◽  
Vol 33 (4) ◽  
pp. 877-894
Author(s):  
El- Sebaie O ◽  
Abd El-Monem M ◽  
Ahmed M ◽  
Ahmed A

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