Next Article in Journal
Confirmation of Maslow’s Hypothesis of Synergy: Developing an Acceptance of Selfishness at the Workplace Scale
Previous Article in Journal
Association of Polymorphisms in the Atrial Natriuretic Factor Gene with the Risk of Essential Hypertension: A Systematic Review and Meta-Analysis
Previous Article in Special Issue
Isolation and Characterization of Aquatic-Borne Klebsiella pneumoniae from Tropical Estuaries in Malaysia
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
IJERPH
Volume 13
Issue 5
10.3390/ijerph13050461
ijerph-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Use of Walnut Shell Powder to Inhibit Expression of Fe2+-Oxidizing Genes of Acidithiobacillus Ferrooxidans

by
Yuhui Li
1,
Yehao Liu
2,
Huifang Tan
1,
Yifeng Zhang
1 and
Mei Yue
1,*
1
Department of Biological and Environmental Engineering, Hefei University, Hefei 230601, China
2
School of Public Health, Anhui Medical University, Hefei 230032, China
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2016, 13(5), 461; https://doi.org/10.3390/ijerph13050461
Submission received: 14 February 2016 / Revised: 12 April 2016 / Accepted: 15 April 2016 / Published: 30 April 2016
(This article belongs to the Special Issue Water Microbial Pollution and Disinfection)
Browse Figures
Versions Notes

Abstract

:
Acidithiobacillus ferrooxidans is a Gram-negative bacterium that obtains energy by oxidizing Fe2+ or reduced sulfur compounds. This bacterium contributes to the formation of acid mine drainage (AMD). This study determined whether walnut shell powder inhibits the growth of A. ferrooxidans. First, the effects of walnut shell powder on Fe2+ oxidization and H+ production were evaluated. Second, the chemical constituents of walnut shell were isolated to determine the active ingredient(s). Third, the expression of Fe2+-oxidizing genes and rus operon genes was investigated using real-time polymerase chain reaction. Finally, growth curves were plotted, and a bioleaching experiment was performed to confirm the active ingredient(s) in walnut shells. The results indicated that both walnut shell powder and the phenolic fraction exert high inhibitory effects on Fe2+ oxidation and H+ production by A. ferrooxidans cultured in standard 9K medium. The phenolic components exert their inhibitory effects by down-regulating the expression of Fe2+-oxidizing genes and rus operon genes, which significantly decreased the growth of A. ferrooxidans. This study revealed walnut shell powder to be a promising substance for controlling AMD.

1. Introduction

Acid mine drainage (AMD), which results from the oxidation of sulfur minerals by air and water, is a worldwide environmental problem [1]. It generates an extreme environment characterized by low pH and high concentrations of heavy metals [2]. AMD is mainly generated by the dissolution of sulfide ores and the production of ferric iron and H+ by certain acidophilic and chemolithotrophic bacteria. Fe2+-oxidizing, acidophilic, and chemolithotrophic bacteria, such as Acidithiobacillus ferrooxidans, are regarded the main producers in AMD environments [3,4]. The generated AMD can remain in the environment for a very long time, and AMD remediation is generally difficult and costly [5,6]. Hence, developing novel approaches for the efficient control of AMD production is imperative.
Currently, the optimal strategy for controlling AMD is the prevention of sulfide oxidation. Although many techniques have been developed to mitigate AMD, most have significant limitations. For example, several physical and chemical strategies that prevent sulfide oxidation are not cost effective and thus cannot be widely applied [7]. Studies have investigated the control of AMD generation through the sterilization of AMD-producing bacteria [2,8]. Although the use of bactericides is simple and economical, it is not a viable strategy because it entails repetitive usage for inhibiting bacterial populations. Furthermore, bactericides are toxic to aquatic organisms [9]. Therefore, developing a low-cost, sustainable, and environment-friendly method for controlling AMD is crucial.
The application of agricultural residue for the removal of toxic contaminants is a recent development in environmental technology [10]. The major advantage of this technology over conventional methods includes its low cost as well as its high efficiency, the possibility of metal recovery, and the broad range of operational conditions. Moreover, some types of agricultural residue inhibit bacterial growth [11,12]. Walnut shell not only contains antibacterial substances, but can also absorb heavy metal ions such as Ni and Mn [13,14]. We screened many types of agricultural residues in a previous experiment. Agricultural residues, including walnut shell, tea seed shell, and orange peels, inhibited AMD production. Among them, walnut shell showed the highest inhibition. Hence, in this study, the active compound of walnut shell was isolated, and the mechanism responsible for the inhibition of A. ferrooxidans growth was studied.

2. Materials and Methods

2.1. Determination of Walnut Shell Composition

Walnuts (Juglandis hopeiensis Hu) were purchased from a local supermarket. The lignin, cellulose, phenolic, and flavonoid components of walnut shell were extracted using previously described methods with some modifications. The phenolic component fraction was extracted using the method of Torun et al. [15,16] with some modifications. In brief, first, acetonitrile/acetic acid (15 mL, 96:4, v/v) was added to 10 g of walnut shell powder in a centrifuge tube. The mixture was stirred for 1 h in the dark and centrifuged at 12,000 g for 10 min at room temperature. Subsequently, the solids were extracted two more times by using 10 mL of the aforementioned extraction solvent; this mixture was shaken for 15 min in the dark and centrifuged under the aforementioned conditions. Finally, the phenolic portion was isolated from the extracts by using high polar dimer 600 (HPD600) macroporous resin. The concentration of phenolic compounds isolated from the extract was determined using the Folin–Ciocalteau method [15] and expressed in milligrams gallic acid equivalents per gram of dry matter by comparison with a calibration curve plotted using a pure standard compound.
To isolate flavonoids [17], 15 g of walnut shell powder was mixed with 150 mL of aqueous ethanol solution (70%, v/v), refluxed three times (2 h each time), filtered, and evaporated to a constant volume of 100 mL. Flavonoids were extracted from this liquid using AB-8 macroporous resin.
To extract lignin [18], 10 g of walnut shell powder was mixed with 100 mL of 6 M aqueous HCl and vigorously stirred (at room temperature) to obtain a pH of 2.0. After acidification, the precipitated lignin was centrifuged at 4000 rpm for 10 min, thoroughly washed with acidified water (pH 2.0), and oven-dried at 60 °C for 16 h until a constant mass was obtained, which was stored in a desiccator. Further purification by redissolving and precipitating was performed to remove extraneous organic contaminants and to reduce the low-molecular-weight fractions.
To obtain high-quality cellulose [19], 10 g of walnut shell powder was mixed with 100 mL of acetic-nitric acid mixture (80:20, v/v) at 120 °C for 20 min. Subsequently, the cellulose produced was rinsed with distilled water until neutral and oven-dried.

2.2. Strains, Medium, and Culture Conditions

The strain used in this experiment was A. ferrooxidans SY23, which was isolated from AMD in our previous research [20]. All experiments were performed in triplicate in 250-mL flasks containing 100 mL of solution at 30 °C on a shaker at 150 rpm (at an initial PH of 2.0). A. ferrooxidans was cultured in 9 K medium [21]. The phenolic component-cultured A. ferrooxidans cells were cultured in 9 K medium supplemented with the phenolic component extracted from walnut shell. A. ferrooxidans cultured in 9 K medium without any walnut shell extracts was used as the control.

2.3. Analytical Methods for the Culture

PH was monitored using a digital pH meter (model PHS-3C, Shanghai Precision & Scientific Instrument Co. Ltd., Shanghai, China). Fe2+ and total iron levels were measured using a colorimetric method with 1,10-phenanthroline through standard methods [22]. The Fe3+ level was calculated on the basis of the difference between total iron and Fe2+ levels.

2.4. Total RNA Extraction and Real-Time Polymerase Chain Reaction

Bacteria cultured in 9K medium in the presence or absence of the phenolic component were harvested through centrifugation. The harvest times for cells in the early logarithmic phase were determined based on the growth curves. Total RNA of A. ferrooxidans was extracted and purified using the RNApure bacteria kit (CWbio, Beijing, China). Total RNA was used as the template to synthesize cDNA by using the SuperQuickRT cDNA kit (CWbio, Beijing, China), according to the manufacturer’s instructions. The relative expression of genes was determined using real-time polymerase chain reaction (PCR) with the UltraSYBR Mixture kit (CWbio, Beijing, China). The sequences of primers in this experiment are detailed in previous studies [3,23,24]. The ratio of gene expression was recorded as the fold change in expression between the treated samples and the control. The results were normalized to the alaS gene which encodes alanyl tRNA synthetase. Real-time PCR experiments were performed in triplicate and used cDNA synthesized from RNA samples obtained from three independent cultures.

2.5. Growth Curves of A. ferrooxidans in 9K Medium Containing Different Components of Walnut Shell

A single source of A. ferrooxidans bacterial cells was resuspended in 9K medium, and suspensions containing 1.2 × 107 cells·mL−1 were used as 10% (v/v) inoculum to ensure the same initial conditions. Bacterial cells were cultured in fresh 9K medium supplemented with walnut shell powder and its five isolated constituents (the concentrations used in this experiment were stated in results). Growth curves were plotted using the direct cell count determined in a Neubauer chamber.

2.6. Pyrite Bioleaching Solution Preparation and Bioleaching Experiment

A single source of A. ferrooxidans bacterial cells was resuspended in 0 K medium (containing 3.0 g (NH4)2SO4, 0.1 g KCl, 0.5 g K2HPO4, 0.5 g MgSO4·7H2O, and 0.01 g Ca(NO3)2 per 1000 mL H2O, pH 1.80), and suspensions containing 1.2 × 107 cells·mL−1 were used as 10% (v/v) inoculum to ensure the same initial conditions. Three types of pyrite bioleaching solutions (PBSs) were prepared as described in Table 1 and were used in the experiments.
All bioleaching experiments were performed in 250-mL flasks; each flask contained 100 mL of one type of the aforementioned media and 1.0 g of pyrite. For culturing A. ferrooxidans, each flask was incubated with 10% (v/v) inoculum at 25 °C with shaking at 150 rpm. Leaching characteristics were monitored by determining the iron ion concentration and pH. The iron ion was measured using atomic absorption spectroscopy. The pH of the bioleaching solution was measured using a pH probe. Triplicate leaches were performed under identical conditions to ensure the reproducibility of the bioprocess experiments.

3. Results and Discussion

3.1. Walnut Shell Powder Inhibited the Oxidative Activity of A. ferrooxidans

As shown in Figure 1, after 3-day incubation of A. ferrooxidans SY23, the Fe2+ concentration in the control decreased rapidly from 9.3 g·L−1 to 0.7 g·L−1. The culture turned from light green to reddish brown. Growth curves were plotted to show the cell number during incubation (Figure 2). The curves showed that A. ferrooxidans multiplied rapidly, and Fe2+ was continuously oxidized into Fe3+. When 1 g·L−1 walnut shell powder was added to the culture, the rate of Fe2+ oxidation decreased from 9.3 g·L−1 to 7.6 g·L−1 during days 1–4. However, from day 4 to day 7, the Fe2+ concentration decreased rapidly from 7.6 g·L−1 to 0 after the addition of 1 g·L−1 walnut shell powder. This phenomenon was attributed to the mass of newly produced A. ferrooxidans. When the concentration of walnut shell powder was increased to 3, 9, and 20 g·L−1, the Fe2+ concentration only fluctuated between 8 and 10 g·L−1 and did not significantly change during the experimental period. This observation might be because the growth of A. ferrooxidans was significantly suppressed by high concentrations of walnut shell powder, and only some Fe2+ was oxidized to Fe3+. These data strongly support our hypothesis that walnut shell powder can suppress the growth of A. ferrooxidans. A. ferrooxidans experienced more stress when the concentration of walnut shell powder increased. The growth of A. ferrooxidans could be partly inhibited when the concentration of walnut shell powder was as low as 1g·L−1. Moreover, the growth of A. ferrooxidans stopped completely, and the Fe2+ concentration remained unchanged when the concentration of walnut shell powder increased to 3 g·L−1 or higher.
As shown in Figure 3, the pH of the control showed a downward trend during the experimental period. Specifically, pH decreased rapidly from 2.8 to 1.9 within 3 days and stabilized at 1.6. However, when walnut shell powder was added at concentrations from 3 to 20 g·L−1, the pH of the cultures slowly decreased from 2.8 to 2.4 during the first 3 days and stabilized at approximately 2.1 during the experimental period. When walnut shell powder was added at 1 g·L−1, the final pH of the culture stabilized at 1.8, a value intermediate between the control and higher concentrations of walnut shell powder. These data indicated that the acidification caused by A. ferrooxidans was effectively alleviated by walnut shell powder, and the minimal concentration was 3 g·L−1.

3.2. Only the Phenolic Component Could Inhibit the Oxidative Activity of A. ferrooxidans

To determine the active substance(s) in walnut shell, the components listed in Table 2 were isolated. Because the minimal concentration of walnut shell was 3 g·L−1, as mentioned earlier, the concentration of the compounds used in this experiment was equivalent to their abundances in 3 g of walnut shell. These compounds were added individually to cultures inoculated with A. ferrooxidans, and pH and the Fe2+ concentration were measured as described earlier. As shown in Figure 4, the Fe2+ concentration in the cultures treated with walnut shell powder or the phenolic fraction supplement slowly decreased from 9.0 to 6.6. By contrast, Fe2+ was completely oxidized in the control and cultures with the cellulose, lignin, and flavonoids supplements. These results indicated that the oxidative activity of A. ferrooxidans was inhibited only by walnut shell and the phenolic components. A. ferrooxidans can produce H+ by oxidizing Fe2+ and inorganic sulfur compounds. Therefore, we also tested whether the H+-producing ability of A. ferrooxidans is suppressed by compounds isolated from walnut shell. As shown in Figure 5, the pH of the sample treated with walnut shell powder or the phenolic component slowly decreased from 2.9 to 2.2. However, the pH of the control and samples treated with cellulose, lignin, and flavonoids decreased from 2.9 to 1.6. These data also supported that only the phenolic fraction of walnut shell could suppress the oxidizing activity of A. ferrooxidans.
Many studies have demonstrated the antibacterial activity of the phenolic component. Kchaou et al. evaluated the antimicrobial and cytotoxic activities of the phenolic fraction extracted from dates [25]. Similarly, Mahboubi et al. demonstrated the antibacterial activity of the phenolic components extracted from Pleniflora flowers [26]. Moreover, many findings have indicated that phenolics exhibit broad-spectrum antibacterial activity [11,12]. Our results also indicate that the phenolic components extracted from walnut shell show antibacterial activity against A. ferrooxidans.

3.3. Relative Expression of Fe2+-Oxidizing Genes Was Inhibited by the Phenolic Components

Because the Fe2+-oxidizing activity of A. ferrooxidans was inhibited significantly after treatment with the phenolic components extracted from walnut shell, it was deduced that the genes related to Fe2+ oxidation might be suppressed.
The fundamental genes involved in Fe2+ oxidation are a part of the res and petI operons, and the Fe2+ oxidation regulators are encoded by regBA, ctaR, and fur. The results of real-time amplification are shown in Table 3. We found that the mRNA levels of Fe2+-oxidizing genes considerably decreased after treatment with the phenolic fraction. The Fe2+ oxidation regulators regB and resB decreased by 1.8-fold at least and 14.7-fold when compared with the control.
Quantification of target gene expression provided insight into the regulation of the Fe2+-oxidizing system. The gene expression profiles of A. ferrooxidans showed that all Fe2+-oxidizing genes shared similar regulation mechanisms. The genes of the res and petI operons were mainly regulated during bacterial growth, which is consistent with the role of these genes in electron transport, which is essential for growth in Fe2+-containing medium [27,28,29]. In our experiment, these genes were downregulated when the growth of A. ferrooxidans was delayed. The regBA and ctaR genes acted as inducers of the genes involved in the oxidation of Fe2+, such as those of the res and petI operons. Kucera et al. demonstrated that the expression profiles of these genes share a similar pattern [3], which is consistent with our results.

3.4. Expression of Rus Operon Genes Was Suppressed by the Phenolic Fraction

The proteins of the A. ferrooxidans respiratory chain are encoded by rus operon genes, which are arranged in the A. ferrooxidans genome as follows: cyc2, cyc1, ORF1, coxB, coxA, coxC, coxD, and rus [23]. The rus operon is dependent on the energetic substrate Fe2+ or S0 [30]. Because an excess of unoxidized Fe2+ was present in the culture after treatment with the phenolic components, we hypothesize that the expression of rus operon genes was suppressed. To test the hypothesis, the expression of eight rus operon genes was measured. As shown in Table 4, all transcripts of the rus operon genes were more abundant in the control than in cells cultured with the phenolic fraction by 5.8-fold (cyc2) to 22.1-fold (rus). In comparison with the expression of other genes, the rus gene showed the most abundant expression.
Yarzabal et al. demonstrated that the rus operon is involved in Fe2+ oxidation rather than in S0 oxidation [23]. The expression of the rus operon is induced by ferrous Fe2+, and its transcript level rapidly increases during the active phase of Fe2+ oxidation and bacterial growth. However, our results indicated that in the presence of the phenolic components, the transcript levels of the genes of the rus operon decreased significantly, even at a high concentration of Fe2+. This finding could be attributed to the suppression of expression of rus operon genes by the phenolic component. Recent studies have revealed that phenolic compounds can regulate the gene expression of microbes, particularly Gram-negative bacteria. Li et al. found that the plant phenolic compound p-coumaric acid could repress gene expression in the Dickeya dadantii type III secretion system [31]. One phenolic compound, phenolic acid, had appreciable effects against indoleacetic acid production in Pseudomonas fluorescens and significantly suppressed gene expression of the type III secretion system [32]. Therefore, the aforementioned results are consistent with our findings that the phenolic components isolated from walnut shell could suppress the expression of some genes.

3.5. A. ferrooxidans Growth Could Be Inhibited by Walnut Shell Powder and the Phenolic Components

As shown by the aforementioned findings, the phenolic fraction suppressed the oxidative activity and the expression of the rus operon of A. ferrooxidans. Hence, it was deduced that the growth of A. ferrooxidans could be delayed. As shown in Figure 6, the growth of A. ferrooxidans cultured in medium supplemented with walnut shell powder or the phenolic components was remarkably slower than the control, and the phenolics showed a higher inhibitory effect than walnut shell powder. Moreover, no difference was observed in the growth of A. ferrooxidans when the other three walnut shell constituents were added.
A. ferrooxidans obtains energy from Fe2+ or various reduced sulfur compounds. Some genes and the rus operon are critical for the survival of this bacterium [23,24]. In this study, we demonstrated that the growth rate of A. ferrooxidans decreased significantly when the expression of these critical genes was suppressed.

3.6. Result of Bioleaching Experiment Showed that the Phenolic Fraction Was the Active Ingredient

Figure 7 and Figure 8 illustrate the total Fe and pH changes during the bioleaching experiment. A. ferrooxidans significantly promoted pyritic sulfur oxidation in the control, and the concentration of total Fe increased to 4.1 g·L−1 at the end of the experiment. Compared with the control, the oxidation of pyritic sulfur was suppressed in the presence of walnut shell powder and the phenolic components, and the concentrations of total Fe were 1.65 and 0.9, respectively. Moreover, the phenolic fraction showed higher activity than walnut shell powder. By contrast, the changes in the pH value showed a trend similar to that for with total Fe during the bioleaching experiment. The pH of the control rapidly decreased from 2.63 to 1.27. However, the addition of walnut shell powder or the phenolic fraction could slow down the pH value decrease.
Bioleaching, as an eco-friendly and energy-saving process, is widely used in metallurgical processing. It is also utilized for in vitro studies of A. ferrooxidans [33,34]. In our bioleaching experiment, walnut shell powder and its phenolic constituents showed high efficiency for inhibiting the oxidation of pyrite. By contrast, the isolated phenolic component exhibited higher inhibitory effects than walnut shell powder. These results support our aforementioned conclusions.

4. Conclusions

This study discovered a promising method for controlling AMD formation through the suppression of the A. ferrooxidans energy system. The phenolic fraction isolated from walnut shell effectively inhibited Fe2+ oxidation and H+ production by A. ferrooxidans. Moreover, the same result was obtained with walnut shell powder. The phenolic components downregulated the expression of Fe2+-oxidizing genes and the rus operon. Hence, they caused a decrease in Fe2+ oxidation and H+ production. Thus, walnut shell powder represents an eco-friendly and economical substance with promising applications in controlling AMD.

Acknowledgments

This study is supported by the grants from National Natural Science Foundation of China (No. 41402303), Natural Science Foundation of Anhui Province (No.1408085MD71) and Higher Education Revitalization Plan of Anhui Province (No. 2013[189]).

Author Contributions

Yuhui Li and Mei Yue conceived and designed the experiments; Yuhui Li and Huifang Tan performed the experiments; Yifeng Zhang analyzed the data and contributed reagents/materials/analysis tools; Yuhui Li wrote the paper.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Vicente-Beckett, V.A.; Taylor McCauley, G.J.; Duivenvoorden, L.J. Metal speciation in sediments and soils associated with acid-mine drainage in Mount Morgan (Queensland, Australia). J. Environ. Sci. Health A Tox. Hazard. Subst. Environ. Eng. 2015, 51, 1–14. [Google Scholar] [CrossRef] [PubMed]
  2. Johnson, D.B.; Hallberg, K.B. Acid mine drainage remediation options: A review. Sci. Total Environ. 2005, 338, 3–14. [Google Scholar] [CrossRef] [PubMed]
  3. Kucera, J.; Bouchal, P.; Lochman, J.; Potesil, D.; Janiczek, O.; Zdrahal, Z.; Mandl, M. Ferrous iron oxidation by sulfur-oxidizing Acidithiobacillus ferrooxidans and analysis of the process at the levels of transcription and protein synthesis. Antonie Van Leeuwenhoek 2013, 103, 905–919. [Google Scholar] [CrossRef] [PubMed]
  4. Xie, X.; Xiao, S.; Liu, J. Microbial communities in acid mine drainage and their interaction with pyrite surface. Curr. Microbiol. 2009, 59, 71–77. [Google Scholar] [CrossRef] [PubMed]
  5. Alakangas, L.; Andersson, E.; Mueller, S. Neutralization/prevention of acid rock drainage using mixtures of alkaline by-products and sulfidic mine wastes. Environ. Sci. Pollut. Res. Int. 2013, 20, 7907–7916. [Google Scholar] [CrossRef] [PubMed]
  6. Sahoo, P.K.; Kim, K.; Equeenuddin, S.M.; Powell, M.A. Current approaches for mitigating acid mine drainage. Rev. Environ. Contam. Toxicol. 2013, 226, 1–32. [Google Scholar] [PubMed]
  7. DellaGreca, M.; Zarrelli, A.; Fergola, P.; Cerasuolo, M.; Pollio, A.; Pinto, G. Fatty acids released by chlorella vulgaris and their role in interference with pseudokirchneriella subcapitata: Experiments and modelling. J. Chem. Ecol. 2010, 36, 339–349. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  8. Brune, K.D.; Bayer, T.S. Engineering microbial consortia to enhance biomining and bioremediation. Front. Microbiol. 2012, 3, 203. [Google Scholar] [CrossRef] [PubMed]
  9. Roberts, D.W.; Roberts, J.F.; Hodges, G.; Gutsell, S.; Ward, R.S.; Llewellyn, C. Aquatic toxicity of cationic surfactants to daphnia magna. SAR QSAR Environ. Res. 2013, 24, 417–427. [Google Scholar] [CrossRef] [PubMed]
  10. Din, M.I.; Mirza, M.L. Biosorption potentials of a novel green biosorbent saccharum bengalense containing cellulose as carbohydrate polymer for removal of Ni (II) ions from aqueous solutions. Int. J. Biol. Macromol. 2013, 54, 99–108. [Google Scholar] [CrossRef] [PubMed]
  11. Mahboubi, A.; Kamalinejad, M.; Ayatollahi, A.M.; Babaeian, M. Total phenolic content and antibacterial activity of five plants of labiatae against four foodborne and some other bacteria. Iran. J. Pharm. Res. 2014, 13, 559–566. [Google Scholar] [PubMed]
  12. Morais-Braga, M.F.; Souza, T.M.; Santos, K.K.; Guedes, G.M.; Andrade, J.C.; Tintino, S.R.; Sobral-Souza, C.E.; Costa, J.G.; Saraiva, A.A.; Coutinho, H.D. Phenolic compounds and interaction between aminoglycosides and natural products of lygodium venustum SW against multiresistant bacteria. Chemotherapy 2012, 58, 337–340. [Google Scholar] [CrossRef] [PubMed]
  13. Ding, D.; Lei, Z.; Yang, Y.; Feng, C.; Zhang, Z. Selective removal of cesium from aqueous solutions with nickel (II) hexacyanoferrate (III) functionalized agricultural residue-walnut shell. J. Hazard. Mater. 2014, 270, 187–195. [Google Scholar] [CrossRef] [PubMed]
  14. Ding, D.; Zhao, Y.; Yang, S.; Shi, W.; Zhang, Z.; Lei, Z.; Yang, Y. Adsorption of cesium from aqueous solution using agricultural residue-walnut shell: Equilibrium, kinetic and thermodynamic modeling studies. Water Res. 2013, 47, 2563–2571. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  15. Giovanelli, G.; Buratti, S. Comparison of polyphenolic composition and antioxidant activity of wild Italian blueberries and some cultivated varieties. Food Chem. 2009, 112, 903–908. [Google Scholar] [CrossRef]
  16. Torun, M.; Dincer, C.; Topuz, A.; Sahin-Nadeem, H.; Ozdemir, F. Aqueous extraction kinetics of soluble solids, phenolics and flavonoids from sage (salvia fruticosa miller) leaves. J. Food Sci. Technol. 2015, 52, 2797–2805. [Google Scholar] [CrossRef] [PubMed]
  17. Ni, Q.; Xu, G.; Wang, Z.; Gao, Q.; Wang, S.; Zhang, Y. Seasonal variations of the antioxidant composition in ground bamboo sasa argenteastriatus leaves. Int. J. Mol. Sci. 2012, 13, 2249–2262. [Google Scholar] [CrossRef] [PubMed]
  18. Ross, K.; Mazza, G. Characteristics of lignin from flax shives as affected by extraction conditions. Int. J. Mol. Sci. 2010, 11, 4035–4050. [Google Scholar] [CrossRef] [PubMed]
  19. Al-Hoqbani, A.A.; Abdel-Halim, E.S.; Al-Deyab, S.S. Extraction of palm tree cellulose and its functionalization via graft copolymerization. Int. J. Biol. Macromol. 2014, 70, 275–283. [Google Scholar] [CrossRef] [PubMed]
  20. Li, Y.; Yue, M. Isolation and identification of acidophiles in acid mine drainage of tongling xinqiao coal mine. In Proceedings of the 3rd International Conference on Environmental Technology and Knowledge Transfer, Hefei, China, 22 January 2010; Nelles, M., Cai, J., Wu, K., Eds.; pp. 807–811.
  21. Silverman, M.P.; Lundgren, D.G. Studies on the chemoautotrophic iron bacterium ferrobacillus ferrooxidans: I: An improved medium and a harvesting procedure for securing high cell yields. J. Bacteriol. 1959, 77, 642–647. [Google Scholar] [PubMed]
  22. Yang, X.; Wang, S.; Liu, Y.; Zhang, Y. Identification and characterization of Acidithiobacillus ferrooxidans YY2 and its application in the biodesulfurization of coal. Can. J. Microbiol. 2015, 61, 65–71. [Google Scholar] [CrossRef] [PubMed]
  23. Yarzabal, A.; Appia-Ayme, C.; Ratouchniak, J.; Bonnefoy, V. Regulation of the expression of the Acidithiobacillus ferrooxidans rus operon encoding two cytochromes C, a cytochrome oxidase and rusticyanin. Microbiology (Reading Engl.) 2004, 150, 2113–2123. [Google Scholar] [CrossRef] [PubMed]
  24. Carlos, C.; Reis, F.C.; Vicentini, R.; Madureira, D.J.; Ottoboni, L.M. The rus operon genes are differentially regulated when Acidithiobacillus ferrooxidans LR is kept in contact with metal sulfides. Curr. Microbiol. 2008, 57, 375–380. [Google Scholar] [CrossRef] [PubMed]
  25. Kchaou, W.; Abbes, F.; Mansour, R.B.; Blecker, C.; Attia, H.; Besbes, S. Phenolic profile, antibacterial and cytotoxic properties of second grade date extract from Tunisian cultivars (Phoenix dactylifera L.). Food Chem. 2016, 194, 1048–1055. [Google Scholar] [CrossRef] [PubMed]
  26. Mahboubi, A.; Asgarpanah, J.; Sadaghiyani, P.N.; Faizi, M. Total phenolic and flavonoid content and antibacterial activity of Punica granatum L. var. Pleniflora flowers (Golnar) against bacterial strains causing foodborne diseases. BMC Complement. Altern. Med. 2015, 15, 366. [Google Scholar] [CrossRef] [PubMed]
  27. Liljeqvist, M.; Rzhepishevska, O.I.; Dopson, M. Gene identification and substrate regulation provide insights into sulfur accumulation during bioleaching with the psychrotolerant acidophile Acidithiobacillus ferrivorans. Appl. Environ. Microbiol. 2013, 79, 951–957. [Google Scholar] [CrossRef] [PubMed]
  28. Bruscella, P.; Appia-Ayme, C.; Levican, G.; Ratouchniak, J.; Jedlicki, E.; Holmes, D.S.; Bonnefoy, V. Differential expression of two BC1 complexes in the strict acidophilic chemolithoautotrophic bacterium Acidithiobacillus ferrooxidans suggests a model for their respective roles in iron or sulfur oxidation. Microbiology (Reading Engl.) 2007, 153, 102–110. [Google Scholar] [CrossRef] [PubMed]
  29. Quatrini, R.; Appia-Ayme, C.; Denis, Y.; Jedlicki, E.; Holmes, D.S.; Bonnefoy, V. Extending the models for iron and sulfur oxidation in the extreme acidophile Acidithiobacillus ferrooxidans. BMC Genomics 2009, 10, 394. [Google Scholar] [CrossRef] [PubMed]
  30. Rohwerder, T.; Gehrke, T.; Kinzler, K.; Sand, W. Bioleaching review part A: Progress in bioleaching: Fundamentals and mechanisms of bacterial metal sulfide oxidation. Appl. Microbiol. Biotechnol. 2003, 63, 239–248. [Google Scholar] [CrossRef] [PubMed]
  31. Li, Y.; Peng, Q.; Selimi, D.; Wang, Q.; Charkowski, A.O.; Chen, X.; Yang, C.H. The plant phenolic compound p-coumaric acid represses gene expression in the dickeya dadantii type III secretion system. Appl. Environ. Microbiol. 2009, 75, 1223–1228. [Google Scholar] [CrossRef] [PubMed]
  32. Myszka, K.; Schmidt, M.T.; Olejnik-Schmidt, A.K.; Leja, K.; Czaczyk, K. Influence of phenolic acids on indole acetic acid production and on the type III secretion system gene transcription in food-associated Pseudomonas fluorescens KM05. J. Biosci. Bioeng. 2014, 118, 651–656. [Google Scholar] [CrossRef] [PubMed]
  33. Zhou, J.; Chen, K.M.; Zhi, D.J.; Xie, Q.J.; Li, H.Y. Effects of pyrite bioleaching solution of Acidithiobacillus ferrooxidans on viability, differentiation and mineralization potentials of rat osteoblasts. Arch. Pharm. Res. 2015, 38, 2228–2240. [Google Scholar] [CrossRef] [PubMed]
  34. Hong, F.F.; He, H.; Liu, J.Y.; Tao, X.X.; Zheng, L.; Zhao, Y.D. Comparison analysis of coal biodesulfurization and coal’s pyrite bioleaching with Acidithiobacillus ferrooxidans. Sci. World J. 2013, 2013. [Google Scholar] [CrossRef] [PubMed]
Ijerph 13 00461 g001 1024
Figure 1. Inhibitory effect of different concentrations of walnut shell powder on Fe2+ oxidization.
Figure 1. Inhibitory effect of different concentrations of walnut shell powder on Fe2+ oxidization.
Ijerph 13 00461 g001
Ijerph 13 00461 g002 1024
Figure 2. Growth curves of A. ferrooxidans with different concentrations of walnut shell powder.
Figure 2. Growth curves of A. ferrooxidans with different concentrations of walnut shell powder.
Ijerph 13 00461 g002
Ijerph 13 00461 g003 1024
Figure 3. Inhibitory effect of different concentrations of walnut shell powder on H+ production.
Figure 3. Inhibitory effect of different concentrations of walnut shell powder on H+ production.
Ijerph 13 00461 g003
Ijerph 13 00461 g004 1024
Figure 4. Inhibitory effect of walnut shell powder (a) and its isolated components (b) on Fe2+ oxidization.
Figure 4. Inhibitory effect of walnut shell powder (a) and its isolated components (b) on Fe2+ oxidization.
Ijerph 13 00461 g004
Ijerph 13 00461 g005 1024
Figure 5. Inhibitory effect of walnut shell powder (a) and its isolated components (b) on H+ production.
Figure 5. Inhibitory effect of walnut shell powder (a) and its isolated components (b) on H+ production.
Ijerph 13 00461 g005
Ijerph 13 00461 g006 1024
Figure 6. Growth curves of A. ferrooxidans with walnut shell powder and its five constituents.
Figure 6. Growth curves of A. ferrooxidans with walnut shell powder and its five constituents.
Ijerph 13 00461 g006
Ijerph 13 00461 g007 1024
Figure 7. Effect on total Fe concentration after treatment with pyrite bioleaching solutions.
Figure 7. Effect on total Fe concentration after treatment with pyrite bioleaching solutions.
Ijerph 13 00461 g007
Ijerph 13 00461 g008 1024
Figure 8. Effect on pH after treatment with pyrite bioleaching solutions.
Figure 8. Effect on pH after treatment with pyrite bioleaching solutions.
Ijerph 13 00461 g008
Table
Table 1. Pyrite bioleaching solutions used in this study.
Table 1. Pyrite bioleaching solutions used in this study.
GroupsMediumThe Walnut Shell Component Added
Control (Bacteria)0 K + pyriteNone
Bacteria + walnut shell powder0 K + pyriteWalnut shell powder
Bacteria + phenolic fraction0 K + pyritePhenolics
Table
Table 2. Composition of walnut shell.
Table 2. Composition of walnut shell.
ComponentContent (g·kg−1 Walnut Shell)The Dosage Used in the Experiments (g)
Cellulose350.7 ± 10.51.05
Lignin314.7 ± 8.50.94
Phenolics16.9 ± 1.90.051
Flavonoids3.7 ± 0.50.011
Values are expressed as means ± standard deviations. The dosage of the compounds used in the experiment was equivalent to their abundances in 3 g of walnut shell.
Table
Table 3. Quantification of Fe2+-oxidizing genes by real-time PCR.
Table 3. Quantification of Fe2+-oxidizing genes by real-time PCR.
Operon NameGeneControlPhenolic FractionRatio of Control to Total Phenolics
res operonhyp20.3 ± 2.47.5 ± 0.22.7
resC11.4 ± 1.34.1 ± 0.82.8
resB16.2 ± 2.11.1 ± 0.214.7
petI operonpetC-17.2 ± 1.13.2 ± 0.42.3
petB-116.2 ± 2.14.2 ± 0.23.9
petA-126.2 ± 3.18.3 ± 0.63.2
sdrA-117.9 ± 1.61.5 ± 0.111.9
cycA-126.9 ± 3.212.1 ± 1.12.2
iron regulatorsregA6.2 ± 1.92.8 ± 0.72.2
regB30.8 ± 2.716.8 ± 1.91.8
ctaR17.2 ± 2.23.5 ± 0.44.9
fur5.4 ± 1.11.2 ± 0.34.5
All values are expressed as n-fold relative to the reference gene. Values shown are the mean of three independent experiments ± standard deviation.
Table
Table 4. Quantification of rus transcripts by real-time PCR.
Table 4. Quantification of rus transcripts by real-time PCR.
GeneControlTotal PhenolicsRatio of Control to Total Phenolics
cyc227.3 ± 2.24.7 ± 0.35.8
orf80.1 ± 7.67.5 ± 0.210.7
cyc110.4 ± 0.90.6 ± 0.0417.3
coxB142.9 ± 8.38.7 ± 0.916.4
coxA75.6 ± 6.68.1 ± 0.59.3
coxC57.3 ± 4.39.4 ± 0.66.1
coxD155.4 ± 7.313.6 ± 1.311.4
rus227.5 ± 13.710.3 ± 0.522.1
All values are expressed as n-fold relative to the reference gene. Values shown are the mean of three independent experiments ± standard deviation.

Share and Cite

MDPI and ACS Style

Li, Y.; Liu, Y.; Tan, H.; Zhang, Y.; Yue, M. Use of Walnut Shell Powder to Inhibit Expression of Fe2+-Oxidizing Genes of Acidithiobacillus Ferrooxidans. Int. J. Environ. Res. Public Health 2016, 13, 461. https://doi.org/10.3390/ijerph13050461

AMA Style

Li Y, Liu Y, Tan H, Zhang Y, Yue M. Use of Walnut Shell Powder to Inhibit Expression of Fe2+-Oxidizing Genes of Acidithiobacillus Ferrooxidans. International Journal of Environmental Research and Public Health. 2016; 13(5):461. https://doi.org/10.3390/ijerph13050461

Chicago/Turabian Style

Li, Yuhui, Yehao Liu, Huifang Tan, Yifeng Zhang, and Mei Yue. 2016. "Use of Walnut Shell Powder to Inhibit Expression of Fe2+-Oxidizing Genes of Acidithiobacillus Ferrooxidans" International Journal of Environmental Research and Public Health 13, no. 5: 461. https://doi.org/10.3390/ijerph13050461

APA Style

Li, Y., Liu, Y., Tan, H., Zhang, Y., & Yue, M. (2016). Use of Walnut Shell Powder to Inhibit Expression of Fe2+-Oxidizing Genes of Acidithiobacillus Ferrooxidans. International Journal of Environmental Research and Public Health, 13(5), 461. https://doi.org/10.3390/ijerph13050461

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop