- Original article
- Open Access
Sulfobacillus thermosulfidooxidans strain Cutipay enhances chalcopyrite bioleaching under moderate thermophilic conditions in the presence of chloride ion
© Bobadilla-Fazzini et al.; licensee Springer. 2014
- Received: 29 September 2014
- Accepted: 20 November 2014
- Published: 10 December 2014
Currently more than 90% of the world’s copper is obtained through sulfide mineral processing. Among the copper sulfides, chalcopyrite is the most abundant and therefore economically relevant. However, primary copper sulfide bioleaching is restricted due to high ionic strength raffinate solutions and particularly chloride coming from the dissolution of ores. In this work we describe the chalcopyrite bioleaching capacity of Sulfobacillus thermosulfidooxidans strain Cutipay (DSM 27601) previously described at the genomic level (Travisany et al. (2012) Draft genome sequence of the Sulfobacillus thermosulfidooxidans Cutipay strain, an indigenous bacterium isolated from a naturally extreme mining environment in Northern Chile. J Bacteriol 194:6327–6328). Bioleaching assays with the mixotrophic strain Cutipay showed a strong increase in copper recovery from chalcopyrite concentrate at 50°C in the presence of chloride ion, a relevant inhibitory element present in copper bioleaching processes. Compared to the abiotic control and a test with Sulfobacillus acidophilus DSM 10332, strain Cutipay showed an increase of 42 and 69% in copper recovery, respectively, demonstrating its high potential for chalcopyrite bioleaching. Moreover, a genomic comparison highlights the presence of the 2-Haloacid dehalogenase predicted-protein related to a potential new mechanism of chloride resistance in acidophiles. This novel and industrially applicable strain is under patent application CL 2013–03335.
- Chloride ion
- Chloride resistance
According to the Chilean Copper Commission (COCHILCO, ), Chile is the largest copper producer where hydrometallurgy represented 33% of the 2013 local copper production. Copper sulfides processing accounts for more than 90% of world’s production. Among the copper sulfides, chalcopyrite constitutes the vast majority of copper resources and reserves, and therefore represents a mineralogical species of great economical importance (Doebrich ).
Within the available hydrometallurgical technologies heap leaching is one of the most used, particularly for copper oxides and secondary copper sulfides. The detection and identification of microorganisms able to live and reproduce under the acidic conditions of the heap leaching process, and moreover the biotechnological innovations related to their potential use as catalysts for primary copper sulfide bioleaching, are topics of major interest. Different studies have shown the enhancing effect of mesophilic (Bobadilla Fazzini et al. ), moderate thermophilic (Stott et al. ) and thermophilic (Konishi et al. ) microorganisms for chalcopyrite dissolution compared to abiotic assays. However, most of these studies were performed under lab-scale ideal conditions, not taking into account industrial-scale process variables such as high ionic strength solutions.
The application of heap bioleaching for copper recovery is severely limited due to fresh-water scarcity as in northern Chile, or the saline drains in Western Australia, due to solutions of high ionic strength and concentrations of elements coming from the ore minerals dissolution such as atacamite (Cu2Cl(OH)3) that releases chloride ions, which are inhibitory for many acidophilic iron-oxidizing microbes. In our estimation, during 2013 about 700 million tons of ore with an average copper grade of 0.2% could not be bioleached worldwide due to the inhibitory effect of high ionic strength raffinate solutions over acidophiles. The most studied acidophilic species is Acidithiobacillus ferrooxidans, and its sensitivity to low chloride concentration has been described long before, attributed to the loss of the cell outer layer integrity (Lawson et al. ). In the case of the widely distributed acidophilic species Leptospirillum ferriphilum, ferrous ion biooxidation is completely inhibited by 12 g/L chloride (Gahan et al. ). Moreover, prolonged exposure to sodium chloride demonstrated no significant adaptation of mixed chemolithotrophic iron-oxidizing cultures, indicating the lack of an acquired resistance through adaptation (Shiers et al. ). Nevertheless, resistant species exist such as Thiobacillus prosperus, a halotolerant acidophile that requires chloride for growth (Nicolle et al. ) or the marine Sulfobacillus sp. TPY able to tolerate 2% (w/v) NaCl (Wang et al. ).
With respect to the biochemical mechanism of bacterial chloride resistance, few studies are available particularly on acidophiles. A recent study showed that NaCl stress in the moderate thermophiles Acidimicrobium ferrooxidans and Acidithiobacillus caldus is tackled by cell membrane adaptation and potential osmoprotectant aminoacid accumulation (Zammit et al. ), giving an insight on specific chloride resistance genes.
Based on these facts, a search for chloride resistant iron-oxidizing acidophilic strains is a relevant research topic. In this study we describe the chalcopyrite bioleaching capacity of Sulfobacillus thermosulfidooxidans strain Cutipay (DSM 27601) in the presence of chloride ion. Strain Cutipay was previously described with novel copper and arsenic resistance capacities at the genomic level (Travisany et al. ).
Strains and culture conditions
Sulfobacillus thermosulfidooxidans DSM 27601 strain Cutipay was isolated from an ore deposit in northern Chile. Sulfobacillus acidophilus DSM 10332 was obtained from the DSMZ collection. Both strains were cultivated in shake flasks at 50°C in 9 K medium at pH 1.6 (Bobadilla Fazzini et al. ), including the addition of 0.25 g/L yeast extract for mixotrophic growth on ferrous. Microorganisms were inoculated at 1% v/v. The cell number was determined by chamber counting under phase-contrast microscope (Thoma Chamber, depth 0.010 mm) with at least four replicate counts.
Minimum inhibitory concentration assays
Minimum inhibitory concentration assays (MIC) were performed in 6 well plates with 5 mL of 9 K medium at pH 1.6 for mixototrophic growth on ferrous, inoculated with 1,00E + 07 cells/mL for each strain separately. Assays were incubated with agitation at 50°C for 5 d with a top film to prevent evaporation. Different concentrations of chloride (tested as NaCl or KCl), Cu(II) (added as CuSO4) and As(III) (added as As2O3) were tested. The lowest concentration at which no growth or iron oxidation was observed corresponds to the MIC that were assayed at least in triplicate.
In silico determination of orthologous protein clusters
The genome sequences and annotation of the predicted proteomes for Sulfobacillus acidophilus DSM10332 (GenBank IDs:NC_016884.1 and NC_016888.1) and Sulfobacillus sp. TPY (GenBank ID:NC_015757.1) were obtained from the GenBank database. For Sulfobacillus thermosulfidooxidans strain Cutipay, predicted proteome sequence was obtained from an in-house annotation of its genome (GenBank ID: ALWJ01000000) as described previously (Travisany et al. ). Using these three predicted proteomes, orthologous protein clusters were determined using ORTHOMCL v1.4 (Li et al. ) with default parameters.
Bioleaching tests were done in shake flasks, as a minimum in duplicate. Each flask contained 100 mL 9 K medium (pH 1.6), as described above, and supplemented with 1.5 g/L Fe(III) and 2.5 g/L Fe(II) with 1% w/v 300 Tyler mesh sieved chalcopyrite concentrate (85.5% chalcopyrite representing more than 99% of total Cu in the assay (Additional file 1: Table S1)) and 3 g/L chloride (as sodium chloride). Each flask was inoculated with Sulfobacillus thermosulfidooxidans DSM 27601 or Sulfobacillus acidophilus DSM 10332 (1 × 107 cell/mL each). A non-inoculated control was included. Shake flasks were incubated for 27 d at 50°C with 120 rpm agitation. Each week cell number, Fe(II) by o-phenantroline method, total iron and Cu(II) by atomic absorption spectrometry were assayed. Sampling was performed allowing the suspended concentrate to settle, and filtering the supernatant to avoid any solids (Grade 5C filters, Advantec, Japan). Evaporation was compensated with pure water before each sampling time.
Minimum Inhibitory Concentrations (MIC) for inhibitory elements chloride, copper and arsenic
Moderate thermophilic species
Sulfobacillus thermosulfidooxidans Cutipay (DSM 27601)
Sulfobacillus acidophilus (DSM 10332)
The three strains have 2061 of coded proteins in common. An exclusive cluster of 22 proteins was shared between both chloride resistant strains. An interesting protein annotated as Haloacid dehalogenase (sequence identifier gi|339628570|ref|YP_004720213.1|) was recognized. This protein belongs to the haloacid dehalogenase-like (HAD) superfamily that includes the 2-Haloacid dehalogenase that catalyzes the dechlorination of small organic chloro-acids.
In this study a novel mixotrophic bacterium Sulfobacillus thermosulfidooxidans strain Cutipay (DSM 27601) was characterized for heavy metals and chloride resistance. Sodium and potassium chloride salts were separately used for chloride MIC testing, since the counter-ion (potassium or sodium) affects the inhibitory effect of anions (Suzuki et al. ) and therefore the MIC. These results are only partially in agreement with our previous genomic analyses (Travisany et al. ), supporting copper but not arsenic resistance. Sulfobacillus thermosulfidooxidans has been reported to be highly resistant to copper, nickel and zinc, while Sulfobacillus acidophilus to cobalt (Watling et al. ). Sulfobacillus thermosulfidooxidans DSM9293 isolated from an ore deposit in Eastern Kazakhstan has been tested for sodium chloride resistance, starting to show inhibition at 7 g/L (4 g chloride/L) (Zammit et al. ), while Sulfobacillus sp. TPY found in an hydrothermal vent in the Pacific Ocean grows in the presence of 20 g/L NaCl (12 g chloride/L) (Wang et al. ). In this study Sulfobacillus thermosulfidooxidans Cutipay from an ore deposit in Chile was completely inhibited at 21 and 8 g/L potassium and sodium chloride, respectively, having chloride resistance comparable to previous reports for the same species, but below the marine strain TPY.
Based on the genome comparison, the chloride-resistant representative species have the Haloacid dehalogenase coding gene. Therefore, a possible mechanism of chloride resistance in sulfobacilli may be related to the biodegradation of toxic small chloro-organic acids formed in the presence of chloride, which are produced from the dissolution of gangue material in hydrometallurgical processes (Dopson et al. ) that reacts with organic matter such as cell products or debris (Keppler et al. ). To our knowledge no chloride resistance mechanism nor related gene has been identified up to date in acidophiles, and therefore this finding may provide new insights into extremophilic microorganisms behavior. On this matter, previous studies have shown the role of membrane and/or amino acid biosynthesis, efflux transporters and CO2 fixation as multifunctional responses to chloride exposure in acidophilic species (Zammit et al. ). However these are general osmo-protection mechanisms observed in different microbial species (Zhou et al. ; Paul ).
Finally, the bioleaching tests showed that strain Cutipay resistance enhances chalcopyrite bioleaching at 50°C in the presence of chloride, based on its fast iron-oxidizing activity compared to the chloride sensitive strain Sulfobacillus acidophilus DSM 10332. Here, only in the case of strain Cutipay all the ferrous iron was completely oxidized. However, a major drop in total iron concentration was observed lowering from 4 to 1 g/L, due to the formation of iron precipitates such as jarosite, as visually observed only on strain Cutipay’s inoculated flasks (data not shown). No matter this precipitation and potential surface passivation, chalcopyrite bioleaching enhancement is clearly shown.
Summarizing, in this study a novel mixotrophic bacterium with resistance to chloride was presented, showing a genomic feature related to a potential new mechanism of chloride resistance and proven to enhance chalcopyrite bioleaching at 50°C in the presence of chloride, a relevant inhibitory element present in important industrial bioleaching processes.
This work was supported by BioSigma ‘S.A.’. The authors thank the company for authorizing the submission of the manuscript for publication. We are also grateful to Fondap Grant 15090007, Basal Grant Center for Mathematical Modeling UMI2807 UCHILE-CNRS and the CIRIC-INRIA Chile project.
- Bobadilla Fazzini RA, Levican G, Parada P: Acidithiobacillus thiooxidans secretome containing a newly described lipoprotein Licanantase enhances chalcopyrite bioleaching rate. Appl Microbiol Biotechnol 2011, 89: 771–780. doi:10.1007/s00253–010–3063–8 10.1007/s00253-010-3063-8PubMed CentralView ArticlePubMedGoogle Scholar
- Mining production database. 2014.Google Scholar
- Doebrich J: Copper–a metal for the ages: U.S. geological survey fact sheet 2009–3031. 2009.Google Scholar
- Dopson M, Halinen A, Rahunen N, Bostro D, Sundkvist J, Riekkola-vanhanen M, Kaksonen AH, Puhakka JA (2008) Silicate mineral dissolution during heap bioleaching. 99:811–820. doi:10.1002/bitGoogle Scholar
- Gahan CS, Sundkvist J-E, Dopson M, Sandström A: Effect of chloride on ferrous iron oxidation by a Leptospirillum ferriphilum-dominated chemostat culture. Biotechnol Bioeng 2010, 106: 422–431. doi:10.1002/bit.22709PubMedGoogle Scholar
- Keppler F, Eiden R, Niedan V, Pracht J, Schöler HF: Halocarbons produced by natural oxidation processes during degradation of organic matter. Nature 2000, 403: 298–301. 10.1038/35002055View ArticlePubMedGoogle Scholar
- Konishi Y, Asai S, Tokushige M, Suzuki T: Kinetics of the bioleaching of chalcopyrite concentrate by acidophilic thermophile acidianus brierleyi. Biotechnol Prog 1999, 15: 681–688. doi:10.1021/bp9900662 10.1021/bp9900662View ArticlePubMedGoogle Scholar
- Lawson EN, Nicholas CJ, Pellat H: The toxic effects of chloride ions on Thiobacillus ferrooxidans. In Biohydrometall. Process. vol I, Univ. Chile Edited by: Vargas T, Jerez CA, Wiertz JV, Toledo H. 1995, 165–174.Google Scholar
- Li L, Stoeckert CJ Jr, Roos DS: OrthoMCL : identification of ortholog groups for eukaryotic genomes. 2003.Google Scholar
- Nicolle JLC, Simmons S, Bathe S, Norris PR: Ferrous iron oxidation and rusticyanin in halotolerant, acidophilic “Thiobacillus prosperus”. Microbiology 2009, 155: 1302–1309. doi:10.1099/mic. 0.023192–0 10.1099/mic.0.023192-0View ArticleGoogle Scholar
- Paul D: Osmotic stress adaptations in rhizobacteria. J Basic Microbiol 2013, 53: 101–110. doi:10.1002/jobm.201100288 10.1002/jobm.201100288View ArticlePubMedGoogle Scholar
- Shiers DW, Blight KR, Ralph DE: Sodium sulphate and sodium chloride effects on batch culture of iron oxidising bacteria. Hydrometallurgy 2005, 80: 75–82. doi:10.1016/j.hydromet.2005.07.001 10.1016/j.hydromet.2005.07.001View ArticleGoogle Scholar
- Stott MB, Sutton DC, Watling HR, Franzmann PD: Comparative leaching of chalcopyrite by selected acidophilic bacteria and archaea. Geomicrobiol J 2003, 20: 215–230. doi:10.1080/01490450390206692 10.1080/01490450303875View ArticleGoogle Scholar
- Suzuki I, Lee D, Mackay B, Harahuc L, Oh JK: Effect of various ions, pH, and osmotic pressure on oxidation of elemental sulfur by Thiobacillus thiooxidans. Appl Environ Microbiol 1999, 65: 5163–5168.PubMed CentralPubMedGoogle Scholar
- Travisany D, Di Genova A, Sepúlveda A, Bobadilla-Fazzini RA, Parada P, Maass A: Draft genome sequence of the Sulfobacillus thermosulfidooxidans Cutipay strain, an indigenous bacterium isolated from a naturally extreme mining environment in Northern Chile. J Bacteriol 2012, 194: 6327–6328. doi:10.1128/JB.01622–12 10.1128/JB.01622-12PubMed CentralView ArticlePubMedGoogle Scholar
- Wang Y, Su L, Zhang L, Zeng W, Wu J, Wan L, Qiu G, Chen XZH: Bioleaching of chalcopyrite by defined mixed moderately thermophilic consortium including a marine acidophilic halotolerant bacterium. Bioresour Technol 2012, 121: 348–354. doi:10.1016/j.biortech.2012.06.114 10.1016/j.biortech.2012.06.114View ArticlePubMedGoogle Scholar
- Watling HR, Perrot FA, Shiers DW: Comparison of selected characteristics of Sulfobacillus species and review of their occurrence in acidic and bioleaching environments. Hydrometallurgy 2008, 93: 57–65. 10.1016/j.hydromet.2008.03.001View ArticleGoogle Scholar
- Zammit CM, Mangold S, Jonna VR, Mutch LA, Watling HR, Dopson M, Watkin ELJ: Bioleaching in brackish waters–effect of chloride ions on the acidophile population and proteomes of model species. Appl Microbiol Biotechnol 2012, 93: 319–329. doi:10.1007/s00253–011–3731–3 10.1007/s00253-011-3731-3View ArticlePubMedGoogle Scholar
- Zhou A, Baidoo E, He Z, Mukhopadhyay A, Baumohl JK, Benke P, Joachimiak MP, Xie M, Song R, Arkin AP, Hazen TC, Keasling JD, Wall JD, Stahl DA, Zhou J: Characterization of NaCl tolerance in Desulfovibrio vulgaris Hildenborough through experimental evolution. ISME J 2013, 7: 1790–1802. doi:10.1038/ismej.2013.60 10.1038/ismej.2013.60PubMed CentralView ArticlePubMedGoogle Scholar
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