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Brazilian Archives of Biology and Technology

Print version ISSN 1516-8913

Braz. arch. biol. technol. vol.55 no.5 Curitiba Sept./Oct. 2012

https://doi.org/10.1590/S1516-89132012000500018 

ENVIRONMENTAL SCIENCES

 

Evaluation of microorganisms with sulfidogenic metabolic potential under anaerobic conditions

 

 

Isabel Kimiko Sakamoto*; Sandra Imaculada Maintinguer; Julia Sumiko Hirasawa; Maria Angela Tallarico Adorno; Maria Bernadete Amâncio Varesche

Departamento de Hidráulica e Saneamento; Escola de Engenharia de São Carlos; Universidade de São Paulo; Av. João Dagnone, 1100; 13563-120; São Carlos - SP - Brasil

 

 


ABSTRACT

The aim of this work was to identify groups of microorganisms that are capable of degrading organic matter utilizing sulfate as an electron acceptor. The assay applied for this purpose consisted of running batch reactors and monitoring lactate consumption, sulfate reduction and sulfide production. A portion of the lactate added to the batch reactors was consumed, and the remainder was converted into acetic, propionic and butyric acid after 111 hours of operation These results indicate the presence of sulfate-reducing bacteria (SRB) catalyzing both complete and incomplete oxidation of organic substrates. The sulfate removal efficiency was 49.5% after 1335 hours of operation under an initial sulfate concentration of 1123 mg/L. The SRB concentrations determined by the most probable number (MPN) method were 9.0x107 cells/mL at the beginning of the assay and 8.0x105 cells/mL after 738 hours of operation.

Key words: sulfate-reducing bacteria, lactate, Most Probable Number, organic acids


 

 

INTRODUCTION

The sulfate ion is the most stable form of sulfur compound that exists in nature and is present in sanitary sludge and various types of industrial wastewater at varying concentrations. Under anaerobic conditions, sulfate-reducing bacteria (SRB) convert sulfate ions (SO4-2) into sulfide (S-2). These SRB are capable of utilizing different substrates, including some hydrocarbons, such as phenols, which makes it possible to use SRB for wastewater treatment and bioremediation of areas contaminated by chemicals such as petroleum.

In the absence of an electron acceptor, SRB are capable of growing via acetogenesis or fermentation using pyruvate, lactate or ethanol as an organic substrate. In mixed cultures containing sulfate, such as those found in bioreactors, SRB compete with acidogenic bacteria, hydrogenotrophic methanogenic archaea and acetoclastics for the available substrates. This competition determines the amount of methane and sulfide produced and what type of end product is obtained from the anaerobic conversion of organic matter (Lens et al. 1998).

According to Colleran (1994), there are theoretically four different metabolic processes that involve SRB: a) complete oxidation of the products of acidogenesis to form carbon dioxide and reduce sulfate to sulfide; b) incomplete oxidation of acidogenesis products to form acetate; c) syntrophic degradation of intermediate compounds, such as organic acids and alcohols, by acetogenic bacteria that are associated with SRB and utilize hydrogen; and d) fermentative growth of SRB in the presence of propionate and ethanol. In the absence of sulfate, a syntrophic association occurs with acetoclastic and hydrogenotrophic bacteria.

O'Reilly and Colleran (2006) studied the effect of the different COD/sulfate ratios (16, 8, 4 and 2) on the syntrophic and competitive interactions between various microbial groups. SRB species were unable to out-compete methane-producing archaea species for acetate at influent COD/SO4(-2) ratios as low as 2. The SRB were observed to play a more significant role in the conversion of hydrogen but did not become completely dominant. Hydrogenotrophic methanogenic archaea were responsible for hydrogen utilization at an influent COD/sulfate ratio of 16 and were still dominant when the ratio was reduced to 4. Hydrogenotrophic SRB assumed a more influential role only when the COD/sulfate ratio was reduced to 2. SRB species were the dominant population responsible for the degradation of propionate at all of the COD/sulfate ratios examined.

Lactate is currently employed as an excellent organic substrate enabling the enrichment, isolation and enumeration of and identification of proper culture conditions for bacteria similar to Desulfovibrio sp. and Desulfotomaculum sp. This substrate can be completely oxidized by several types of sulfate-reducing bacteria.

The study of these bacteria is of great interest to various industries, especially the navigation and petroleum industries, given that they are the most affected by the corrosion caused by SRB (Ilhan-Sungur et al. 2007). These microorganisms may also be used in the bioremediation of areas contaminated by petroleum and hydrocarbons due to their nutritional versatility.

The aim of this work was to identify groups of microorganisms involved in the degradation of organic matter using sulfate as an electron acceptor. Sodium lactate was used as a carbon source in an assay to determine the sulfidogenic metabolic potential. The experiments measured lactic acid consumption, sulfate reduction and sulfide production. We conducted microscopic examinations and quantified SRB using the most probable number (MPN) at the beginning and the end of the experiment.

 

MATERIALS AND METHODS

The experiments were carried out using anaerobic granular sludge from an Upflow Anaerobic Sludge Blanket (UASB) that treats poultry slaughterhouse wastewater (Dakar Poultry S/A, SP-Brazil).

Batch reactors were prepared in triplicate in 2 L Duran® flasks filled with 1 L of reaction medium and 10% (v/v) inoculum, then sealed under an N2/CO2 (70:30%) atmosphere. The reactors were incubated at 30ºC ± 1ºC, with agitation at 120 rpm. The mineral medium (Zinder et al. 1984) consisted of the following chemicals dissolved in distilled water: NH4Cl, 0.5 g/L; K2HPO4, 0.4 g/L; MgCl2.6H2O, 0.1 g/L; CaCl2. 2H2O, 0.05 g/L; rezasurin, 0.001 g/L; a trace-metal solution, 10 mL/L (Zinder and Koch 1984); and sodium bicarbonate (1 g/L), a vitamin solution (1 mL/L) (Touzel and Albagnac 1983), sodium lactate (2.24 g/L) and sodium sulfate (1.12 g/L). Sodium sulfide (0.5 g/L) was used as a reducing agent. The COD/sulfate ratio was 1.3.

The organic acids present in the reactors (lactic, acetic, propionic and butyric acids) were analyzed via HPLC in a Shimadzu system, as described by Lazaro et al. (2008).

Analyses of sulfate, sulfide, COD and total volatile solids (TVS) were performed according to APHA-AWWA-WEF (2005).

SRB were quantified using the multiple tubes technique (Most Probable Number, MPN) at the beginning of the experiment and after 738 hr. The same media and lactate concentration described above were used for the MPN assay. The concentration of sodium sulfide was 0.04 g/L.

SRB were detected by collecting a 0.5 mL sample, diluting it serially and adding it to a tube with 1.0 mL of ferrous sulfate (1 g/L). The presumed SRB population was positive in tests that measure ferrous sulfide (black precipitate). The SRB population was identified using a combination of positive (black precipitate) and negative (no black precipitate) tests, according to APHA-AWWA-WEF (2005).

The morphologies of various bacteria observed in the sulfidogenic assay and MPN samples were examined via phase contrast microscopy (Olympus BX60-FLA microscope), and images were captured with a digital camera (Evolution QE, Media Cybernetics Inc., USA). Image Pro-Plus 4.5 software was used for image analysis.

 

RESULTS AND DISCUSSION

A portion of the lactic acid added to the batch reactors was consumed and converted into organic acids, such as acetic, propionic and butyric acid, which indicated the presence of SRB catalyzing the complete and incomplete oxidation of the organic substrate. The temporal variation of the production of organic acids (over 111 hours of operation) is presented in Figure 1. The data indicated that as lactic acid decreased, the amounts of other acids (mainly acetic acid) increased. Propionic and butyric acid were detected after 40 hours. After 72 hours of operation, propionic acid was not detected, whereas the percentages of acetic and butyric acid increased from 62% and 2.1% to 92% and 8.4%, respectively.

According to Lens et al. (1998), for each 96 g of sulfate present in wastewater, 64 g of COD are consumed (COD/sulfate ratio of 0.67). Therefore, there is theoretically sufficient sulfate to completely remove the organic matter present via sulfidogenesis. At COD/sulfate ratios of less than 0.67, the amount of organic matter is insufficient for complete reduction of sulfate to be achieved, and an external source of carbon must therefore be added if the goal of the treatment is sulfate removal. For wastewater with a COD/sulfate ratio higher than 0.67, the complete removal of organic matter will be achieved only if methanogenesis occurs along with the reduction of sulfate (Lens et al. 1998).

The COD/sulfate ratio used in this work was 1.3. The reactors were operated for 1335 hours, with initial and final CODs of 1515 mg/L and 634 mg/L, respectively, with 58% of efficiency. The initial and final sulfate concentrations were 1123 mg/L and 567 mg/L, respectively. Therefore, 49.5% sulfate removal efficiency was achieved. The initial and final values of total volatile solids (TVS) were 16 g/L and 21 g/L, respectively, which indicated biomass growth over the 1335 hours of operation. However, at 738 hours of operation, the TVS value was 16.2 g/L, which represented almost no change since the beginning of the assay. This result may be related to the storage time of the sludge granules (± 10 months) under refrigeration at 4ºC. These findings indicated that the biomass required a long period of adaptation to the new feeding conditions.

Sarti (2007) used batch reactors fed with mineral medium, as described by Zinder and Koch (1984), with added sodium lactate, sodium acetate, ethanol and sodium sulfate to obtain initial COD/sulfate ratios of 1.1 to 1.5. This author achieved a COD removal efficiency of 87 to 89% and a sulfate consumption of 57 to 77%. Under these conditions, the preferential substrate of the SRB was lactate, instead of ethanol or acetate.

The sulfate consumption was greater in the early hours of the assay (Fig. 2). This finding is attributed to the presence of organic substrates such as lactate, acetate, propionate and butyrate. After consumption of these compounds, the remaining sulfate may have been reduced via hydrogenotrophic SRB metabolism, which can utilize carbon dioxide and or other organic acids produced during cell death. However, sulfate reduction under these conditions occurs more slowly.

Figure 2 shows that the sulfide concentration increased as the sulfate concentration was reduced. However, this result may be due to the difficulty involved in measuring sulfide gas and to the loss that may occur during sample collection. The sulfide analysis performed in this study employed liquid samples.

According to O'Flaherty et al. (1998), SRB use sulfate as a terminal electron acceptor when it is available during the oxidation of organic matter, resulting in the production of hydrogen sulfite (H2S). The SRB can be divided into two main groups: those that can completely oxidize organic matter to H2S and CO2 and those that carry out incomplete oxidation, usually forming acetate.

The reactors fed with lactate plus sulfate contained 9.0 x 107 cells/mL and 8.0 x 105 cells/mL at the beginning of the experiment and after 738 hours of operation, respectively (Fig.3), indicating that these bacteria were reduced over time in the reactors. Although the values of TVS remained essentially the same over this period of time, the MPN quantification indicated that other microorganisms (anaerobic bacteria) were maintained along with the reduction of SRB. This SRB reduction was most likely due to the absence of an external source of carbon, given that was nearly entirely consumed by 111 hours.

Sarti (2007) also found that the SRB population decreased over time, from 27.9% to 19.5%, despite an observed sulfate consumption of 77.5%. The author observed that methanogenic archaea were predominant (52.6%) at the end of the assay.

According to Widdel (1988), SRB compete with methanogenic archaea for hydrogen (H2), carbon dioxide (CO2) and acetate and with syntrophic bacteria for substrates such as propionate, butyrate and ethanol, which are key intermediates in the overall process of anaerobic digestion.

Domingues et al. (2004) used 2 L Duran® flasks containing media with lactate (1.8 g/L) plus sulfate (1.1 g/L) incubated at 55 ± 1ºC and observed SRB concentrations of 3.0 x 1011 cells/mL initially and 9.0 x 1012 cells/mL after 55 days of operation.

Sakamoto (1996) utilized 100-mL serum flasks filled with mineral medium, as described by Zinder and Koch (1984), with added sodium acetate and increasing amounts of sodium sulfate, which resulted in carbon/sulfate ratios from 0.36 to 1.35. They obtained 2.29 x 104 cells/mL and 1.51 x 1012 cells/mL for carbon/sulfate ratios of 0.45 and 0.67, respectively.

In this work, we used mineral medium as described by Zinder and Koch (1984) with added sodium lactate and sodium sulfate. The quantities of SRB found by Sakamoto (1996) were higher than were found in the present study, most likely because of the addition of external carbon sources and the decreasing sulfate concentrations during the assay, which may have promoted selection for SRB.

The bacteria observed in the granular sludge sample (inoculum) displayed various morphologies, including filaments similar to Methanosaeta sp., coccobacilli, diplococci, curved rods, rods and segmented filaments (Fig. 4a). Ribas et al. (2005) observed similar morphologies in granular sludge collected from an UASB. Additionally, a horizontal-flow anaerobic immobilized biomass (HAIB) reactor treating domestic sewage was found to contain rods, cocci, spirochetes, filaments, fluorescent rods and cocci as well as Methanosaeta sp.-like archaeal cells (Lima et al. 2005).

Hirasawa (2003) analyzed the granular sludge used in this work via FISH using the EUB338 and ARC915 probes and found that they detected 44.8% and 59.5% of the sample, respectively. These results were similar to the quantification performed by Sarti (2007) using the EUB338, ARC915 and BRS385 probes, which corresponded to 49.8 %, 56.7% and 27.9% of the sample, respectively. Therefore, based on these studies, the inoculum contained a greater proportion of methanogenic archaea than SRB.

Although the granular sludge (inoculum) was predominately methanogenic, several other works have used this sludge to obtain a cellular population capable of removing sulfate (Damianovic et al. 2006; Hirasawa 2007; Sarti 2007). The morphologies observed in the sample obtained at the end of the sulfidogenic assay included rods, curved rods and coccobacilli (Fig. 4b). The morphologies observed in the final MPN sample (10-4 dilution) corresponded to coccobacilli, curved rods and rods (Fig. 4c).

 

CONCLUSIONS

The organic substrate added in the assay described herein was entirely consumed in 111 hours and was partially converted to other types of acids, such as acetic, propionic and butyric acid. This conversion indicated the existence of the activity of SRB performing both complete and incomplete oxidation of organic substrates.

The batch reactors fed with lactate plus sulfate contained 9.0 x 107 cells/mL at the beginning of the experiment and 8.0 x 105 cells/mL after 738 hours of operation, which indicated a decrease in the number of these bacteria in the reactors, possibly due to the lack of an external carbon source, as it was essentially consumed in 111 hours.

 

ACKNOWLEDGMENTS

This research was financially supported by the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) and the Financiadora de Estudos e Projetos (FINEP).

 

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Received: September 16, 2011;
Revised: March 9, 2012;
Accepted: July 19, 2012.

 

 

* Author for correspondence: sakamoto@sc.usp.br

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