Hydrogen sulfide removal by immobilized autotrophic and heterotrophic bacteria in the bioreactors

Summary Autotrophic Thiobacillus sp. CH11 and heterotrophic Pseudomonas putida CH11 were isolated from piggery waste water. Extensive tests, including removal action, removal efficiency, removal capacity, and adaptability to perturbed conditions were conducted on autotrophic and heterotrophic biofilters. The results clearly demonstrate the application potential of autotrophic and heterotrophic biofilters for the continuous H₂S removal under different perturbed conditions.     

Bacterial desulfurization of the H2S-containing biogas

Summary A Packed-bubble tower was used as absorber to treat 1000m³ biogas per day. A Biofilm reactor was used as the regeneration equipment in whichThiobacillus ferrooxidans was employed to oxidize Fe(II) to Fe(III). More than 95% H₂S removal could be obtained when the inlet H₂S concentration of the biogas ranged from 1.0 to 2.5 g/m³ and the maximum Fe(II) oxidation rate of bioreactor was 1170.87mg/L.h.     

Conversion of sodium cyanide to carbon dioxide and ammonia by immobilized cells ofPseudomonas putida

Summary Pseudomonas putida, isolated from contaminated industrial wastewaters and soil sites, was found to utilize sodium cyanide (NaCN) as a sole source of carbon and nitrogen. Cells, immobilized in calcium alginate beads (1–2 mm diameter) were aerated in air-uplift-type fluidized batch bioreactor containing 100–400 ppm of NaCN. Degradation of NaCN was monitored for 168 h by analyzing gaseous and dissolved ammonia (NH₃), CO₂, pH and optical density. The results indicated that the alginate-immobilized cells ofP. putida were able to degrade NaCN into NH₃ and CO₂ in a time-dependent manner.     

Chemotactic responses ofThiobacillus thioparus

A capillary assay was employed to quantify chemotactic responses in the chemoautotrophic bacterium,Thiobacillus thioparus. NH₄Cl, KNO₃, and Na₂S₂O₃ were strong attractants. The minimum concentration of each of these inorganic chemicals needed to elicit an observable response was approximately 10^–4 M.T. thioparus did not respond to carbohydrates or amino acids.     

Taxonomic relationships ofThiobacillus halophilus,T. aquaesulis,and other species ofThiobacillus,as determined using 16S rDNA sequencing

Total base sequences of the 16S rRNA genes ofThiobacillus halophilus andThiobacillus aquaesulis show that these bacteria fall into the gamma- and beta-subdivisions, respectively of the Proteobacteria. The closest relative ofT. halophilus isThiobacillus hydrothermalis (with 98.7% similarity), and the closest relative ofT. aquaesulis isThiobacillus thioparus (93.2% similarity). Physiological properties and mol% G+C content of their DNA serve to confirm that these four organisms are all distinct species. It is reiterated that the species currently assigned to the genusThiobacillus are clearly so diverse that they need reclassification into several genera. The type species,T. thioparus, is unequivocally placed in the beta-subdivision of the Proteobacteria, thus requiring that the use of the genus nameThiobacillus be restricted to the chemolithoautotrophic species falling into that group.T. aquaesulis andT. thioparus may thus be regarded as true species ofThiobacillus. The relatively large number of obligately chemolithoautotrophicThiobacillus species falling in the gamma-subdivision of the Proteobacteria need further study in order to assess the case for reclassification into one or more new or different genera.     

Characteristics of H2S oxidizing bacteria inhabiting a peat biofilter

Bacteria associated with H₂S oxidization were isolated from a peat biofilter to which various concentrations of H₂S gas were supplied. After acclimation of the peat, a facultative autotrophic bacterium, Thiobacillus itnermedius, was primarily responsible for H₂S oxidation. The cell number isolates increased at above pH 3, but decreased when pH fell below 3, in which range breakthrough of H₂S was finally observed. When pH was controlled at around 3, constant removal of H₂S continued without a decline of the cell number. The specific H₂S uptake rate of the autotrophic bacterium was determined as 1.4 × 10⁻¹³ g-H₂S-S/h/cells. The cell number of the bacteria during steady state H₂S removal was proportional to the inlet H₂S concentration, verifying the kinetic equation derived previously.     

Phylogenetic assessment of culture collection strains of Thiobacillus thioparus, and definitive 16S rRNA gene sequences for T. thioparus, T. denitrificans, and Halothiobacillus neapolitanus

The 16S rRNA gene sequences of 12 strains of Thiobacillus thioparus held by different culture collections have been compared. A definitive sequence for the reference type strain (Starkey; ATCC 8158^T) was obtained. The sequences for four examples of the Starkey type strain were essentially identical, confirming their sustained identity after passage through different laboratories. One strain (NCIMB 8454) was reassigned as a strain of Halothiobacillus neapolitanus, and a second (NCIMB 8349) was a species of Thermithiobacillus. These two strains have been renamed in their catalog by the National Collection of Industrial and Marine Bacteria. The 16S rRNA gene sequence of the type strain of Halothiobacillus neapolitanus (NCIMB 8539^T) was determined and used to confirm the identity of other culture collection strains of this species. The reference sequences for the type strains of Thiobacillus thioparus and Halothiobacillus neapolitanus have been added to the online List of Prokaryotic Names with Standing in Nomenclature. Comparison of the 16S rRNA gene sequences available for strains of Thiobacillus denitrificans indicated that the sequence for the type strain (NCIMB 9548^T) should always be used as the reference sequence for new and existing isolates.     

Nonadaptive Growth Responses of Tetrahymena pyriformis Grown on Single Bacterial Species*

SYNOPSIS. Turbidity changes caused by ingestion of bacterial cell suspensions by Tetrahymena pyriformis W were used to measure feeding capabilities. Tetrahymena was grown on washed killed cells of Aerobacter aerogenes, Azotobacter agile, Arthrobacter sp., Bacillus megaterium, Mycobacterium lacticola, Pseudomonas fragi, Sarcinia lutea, Serratia marcescens, and Thiobacillus thioparus for 6 months with serial transfers. After this time the rate of feeding on each bacterium gave no indication of an adaptation to the food bacterium.     

H2S degradation is reflected by both the activity and composition of the microbial community in a compost biofilter

In this study, 16S rRNA- and rDNA-based denaturing gradient gel electrophoresis (DGGE) were used to study the temporal and spatial evolution of the microbial communities in a compost biofilter removing H₂S and in a control biofilter without H₂S loading. During the first 81 days of the experiment, the H₂S removal efficiencies always exceeded 93% at loading rates between 4.1 and 30 g m⁻³ h⁻¹. Afterwards, the H₂S removal efficiency decreased to values between 44 and 71%. RNA-based DGGE analysis showed that H₂S loading to the biofilter increased the stability of the active microbial community but decreased the activity-based diversity and evenness. The most intense band in both the RNA- and DNA-based DGGE patterns of the H₂S-degrading biofilter represented the sulfur oxidizing bacterium Thiobacillus thioparus. This suggested that T. thioparus constituted a major part of the bacterial community and was an important primary degrader in the H₂S-degrading biofilter. The decreasing H₂S removal efficiencies near the end of the experiment were not accompanied by a substantial change of the DGGE patterns. Therefore, the decreased H₂S removal was probably not caused by a failing microbiology but rather by a decrease of the mass transfer of substrates after agglutination of the compost particles.     

Isolation and characterization of ethylbenzene degrading <Emphasis Type="Italic">Pseudomonas putida</Emphasis> E41

Pseudomonas putida E41 was isolated from oil-contaminated soil and showed its ability to grow on ethyl-benzene as the sole carbon and energy source. Moreover, P. putida E41 show the activity of biodegradation of ethylbenzene in the batch culture. E41 showed high efficiency of biodegradation of ethylbenzene with the optimum conditions (a cell concentration of 0.1 g wet cell weight/L, pH 7.0, 25°C, and ethylbenzene concentration of 50 mg/L) from the results of the batch culture. The maximum degradation rate and specific growth rate (μ_max) under the optimum conditions were 0.19+0.03 mg/mg-DCW (Dry Cell Weight)/h and 0.87+0.13 h⁻¹, respectively. Benzene, toluene and ethylbenzene were degraded when these compounds were provided together; however, xylene isomers persisted during degradation by P. putida E41. When using a bioreactor batch system with a binary culture with P. putida BJ10, which was isolated previously in our lab, the degradation rate for benzene and toluene was improved in BTE mixed medium (each initial concentration: 50 mg/L). Almost all of the BTE was degraded within 4 h and 70–80% of m-, p-, and o-xylenes within 11 h in a BTEX mixture (initial concentration: 50 mg/L each). In summary, we found a valuable new strain of P. putida, determined the optimal degradation conditions for this isolate and tested a mixed culture of E41 and BJ10 for its ability to degrade a common sample of mixed contaminants containing benzene, toluene, and xylene.     

C<Subscript>1</Subscript> compounds as auxiliary substrate for engineered <Emphasis Type="Italic">Pseudomonas putida</Emphasis> S12

The solvent-tolerant bacterium Pseudomonas putida S12 was engineered to efficiently utilize the C₁ compounds methanol and formaldehyde as auxiliary substrate. The hps and phi genes of Bacillus brevis, encoding two key steps of the ribulose monophosphate (RuMP) pathway, were introduced to construct a pathway for the metabolism of the toxic methanol oxidation intermediate formaldehyde. This approach resulted in a remarkably increased biomass yield on the primary substrate glucose when cultured in C-limited chemostats fed with a mixture of glucose and formaldehyde. With increasing relative formaldehyde feed concentrations, the biomass yield increased from 35% (C-mol biomass/C-mol glucose) without formaldehyde to 91% at 60% relative formaldehyde concentration. The RuMP-pathway expressing strain was also capable of growing to higher relative formaldehyde concentrations than the control strain. The presence of an endogenous methanol oxidizing enzyme activity in P. putida S12 allowed the replacement of formaldehyde with the less toxic methanol, resulting in an 84% (C-mol/C-mol) biomass yield. Thus, by introducing two enzymes of the RuMP pathway, co-utilization of the cheap and renewable substrate methanol was achieved, making an important contribution to the efficient use of P. putida S12 as a bioconversion platform host.     

Enhanced removal efficiency of malodorous gases in a pilot-scale peat biofilter inoculated with Thiobacillus thioparus DW44

A newly isolated autotrophic bacterium, Thiobacillus thioparus DW44, which is capable of degrading sulfur-containing gases, was inoculated into a pilot-scale peat biofilter to treat the exhaust gas from a night soil treatment plant. Hydrogen sulfide (H₂S), methanethiol (MT), dimethyl sulfide (DMS) and dimethyl disulfide (DMDS) in the exhaust gas were efficiently removed for six months. Average removal ratios were 99.8% for H₂S, 99.0% for MT, 89.5% for DMS and 98.1% for DMDS at a space velocity of 46 h⁻¹ during the period of operation. No acclimation period was needed to reach such a high efficiency in the removal of the gases, indicating that the ability of this bacterium to remove these gases was occurred immediately after its inoculation to the peat. Ammonia (NH₃) in the exhaust gas was neutralized with SO₄²⁻, which is the final product of the oxidation of H₂S, MT, DMS and DMDS by the bacterium. No remarkable decline of pH, which often causes a deterioration in bacterial activity, was observed, mainly because of the reaction of SO₄²⁻ with NH₃. This study is the first report on the application of an isolated microorganism to a practical deodorizing system. The inoculation of T. thioparus DW44 into the pilot-scale peat biofilter could overcome such disadvantages of the conventional peat biofilter as a long acclimation period to reach a constant gas removability and the low removability of DMS, and resulted in enhanced removal efficiency of malodorous gases.     

Pyrite oxidation in acid sulphate soils: The role of miroorganisms

Summary A study has been made of microbial processes in the oxidation of pyrite in aicd sulphate soil material. Such soils are formed during aeration of marine muds rich in pyrite (FeS₂). Bacteria of the type ofThiobacillus ferrooxidans are mainly responsible for the oxidation of pyrite, causing a pronounced acidification of the soil. However, becauseThiobacillus ferrooxidans functions optimally at pH values bellow 4.0, its activity cannot explain the initial pH drop from approximately neutral to about 4. This was shown to be a non-biological process, in which bacteria play an insignificant part. AlthoughThiobacillus thioparus andThiobacillus thiooxidans were isolated from the acidifying soil, they did not stimulate oxidation of FeS₂, but utilized reduced sulphur compounds, which are formed during the non-biological oxidation of FeS₂.Ethylene-oxide-sterilized and dry-sterilized soil inoculated with pure cultures of mixtures of various thiobacilli or with freshly sampled acid sulphate soil soil did not acidify faster than sterile blanks.Thiobacillus thiooxians. Thiobacillus thioparus. Thiobacillus intermedius andThiobacillus perometabolis increased from about 10⁴ to 10⁵ cells/ml in media with FeS₂ as energy source. However, FeS₂ oxidation in the inoculated media was not faster than in sterile blanks.Attempts to isolate microorganisms other thanThiobacillus ferrooxidans, like metallogenium orLeptospirillum ferrooxidans, which might also be involved in the oxidation of FeS₂ were not successful.Addition of CaCO₃ to the soil prevented acidification but did not stop non-biological oxidation of FeS₂.     

A microbial biosensor for hydrogen sulfide monitoring based on potentiometry

In this study, a microbial biosensor for hydrogen sulfide (H₂S) detection based on Thiobacillus thioparus immobilized in a gelatin matrix was developed. The T. thioparus was immobilized via either surface adsorption on the gelatin matrix or entrapment in the matrix. The bacterial and gelatin concentration in the support were then varied in order to optimize the sensor response time and detection limit for both methods. The optimization was conducted by a statistical analysis of the measured biosensor response with various bacterial and polymer concentrations. According to our experiments with both immobilization methods, the optimized conditions for the entrapment method were found to be a gelatin concentration of 1% and an optical density of 82. For the surface adsorption method, 0.6% gelatin and an optical density of 88 were selected as the optimal conditions. A statistical model was developed based on the extent of the biosensor response in both methods of immobilization. The maximum change in the potential of the solution was 23.16 mV for the entrapment method and 34.34 mV for the surface absorption method. The response times for the entrapment and adsorption methods were 160 s and 105 s, respectively. The adsorption method is more advantageous for the development of a gas biosensor due to its shorter response time.     

Biofiltration of reduced sulphur compounds and community analysis of sulphur-oxidizing bacteria

The present work aims to use a two-stage biotrickling filters for simultaneous treatment of hydrogen sulphide (H₂S), methyl mercaptan (MM), dimethyl sulphide (DMS) and dimethyl disulphide (DMDS). The first biofilter was inoculated with Acidithiobacillus thiooxidans (BAT) and the second one with Thiobacillus thioparus (BTT). For separate feeds of reduced sulphur compounds (RSC), the elimination capacity (EC) order was DMDS > DMS > MM. The EC values were 9.8 g_MM-S/m³/h (BTT; 78% removal efficiency (RE); empty bed residence time (EBRT) 58 s), 36 g_DMDS-S/m³/h (BTT; 94.4% RE; EBRT 76 s) and 57.5 g_H2S-S/m³/h (BAT; 92% RE; EBRT 59 s). For the simultaneous removal of RSC in BTT, an increase in the H₂S concentration from 23 to 293 ppmv (EBRT of 59 s) inhibited the RE of DMS (97-84% RE), DMDS (86-76% RE) and MM (83-67% RE). In the two-stage biofiltration, the RE did not decrease on increasing the H₂S concentration from 75 to 432 ppmv.     

Nitrate-Controlled Anaerobic Oxidation of Pyrite by Thiobacillus Cultures

Nitrate-dependent pyrite oxidation is an important process as it may prevent pollution by nitrate from agriculture. Anaerobic oxidation of pyrite with nitrate as an electron acceptor was studied in cultures of Thiobacillus denitrificans and Thiobacillus thioparus. Both strains reduced nitrate, with pyrite added as sole electron donor, but T. thioparus reduced nitrate to nitrite only. Accumulation of nitrite, however, was prevented in co-cultures of T. denitrificans and T. thioparus. Furthermore, pyrite oxidation rates were dependent on pyrite pretreatment, which results in different specific surface areas of pyrite. Initial nitrate concentration or pyrite origin did not affect the pyrite oxidation rate.     

Conversion of hydrogen sulphide by acidophilic bacteria

Conversion of hydrogen sulphide (H₂S) by the bacterium Thiobacillus thiooxidans to sulphur or sulphate was demonstrated in a continuous column contacter using a countercurrent flow of gas and liquid medium. The initial conversion to sulphur was much faster than subsequent oxidation to sulphate, allowing for removal of elemental sulphur. The rate of H₂S removal increased with available surface area in the column bed and with time. The number of bacteria in the column increased very slowly with time, placing great importance on the initial concentration of bacteria in the column. Correspondence to: H. M. Lizama     

Response of Plant-Colonizing Pseudomonads to Hydrogen Peroxide

Colonization of plant root surfaces by Pseudomonas putida may require mechanisms that protect this bacterium against superoxide anion and hydrogen peroxide produced by the root. Catalase and superoxide dismutase may be important in this bacterial defense system. Stationary-phase cells of P. putida were not killed by hydrogen peroxide (H₂O₂) at concentrations up to 10 mM, and extracts from these cells possessed three isozymic bands (A, B, and C) of catalase activity in native polyacrylamide gel electrophoresis. Logarithmic-phase cells exposed directly to hydrogen peroxide concentrations above 1 mM were killed. Extracts of logarithmic-phase cells displayed only band A catalase activity. Protection against 5 mM H₂O₂ was apparent after previous exposure of the logarithmic-phase cells to nonlethal concentrations (30 to 300 μM) of H₂O₂. Extracts of these protected cells possessed enhanced catalase activity of band A and small amounts of bands B and C. A single form of superoxide dismutase and isoforms of catalase were apparent in extracts from a foliar intercellular pathogen, Pseudomonas syringae pv. phaseolicola. The mobilities of these P. syringae enzymes were distinct from those of enzymes in P. putida extracts.     

Removal and recovery of Cu(II) from industrial effluent by immobilized cells of Pseudomonas putida II-11

A copper [Cu(II)]-accumulating strain, Pseudomonas putida II-11, isolated from electroplating effluent removed a significantly high amount of Cu(II) from growth medium and buffer. A laboratory-scale fixed bed reactor with cells of P. putida II-11 immobilized in polyacrylamide gel was constructed. The adsorption of Cu(II) by the immobilized cells was pH-dependent. Maximum removal of Cu(II) by the immobilized cells was at pH 8.0. The presence of Cr(IV), Ni(II) and Zn(II) did not significantly inhibit Cu(II) uptake whereas the presence of Pb(II) reduced Cu(II) uptake by fivefold. The presence of borate, carbonate, chloride and sulphate did not significantly inhibit Cu(II) uptake. The Cu(II) removal capacity of the bioreactor with immobilized cells did not change significantly when operated at retention times greater than 3 min. More than 90% of Cu(II) adsorbed on immobilized cells could be recovered by eluting with 0.1 m HCl. The bioreactor could be used for at least five loading-elution cycles without loss of Cu(II) removal capacity. The feasibility of using this bioreactor to remove and recover Cu(II) from electroplating effluent is discussed. Correspondence to: P. K. Wong