Michihiko Ike

Biodegradation of Bisphenol A, Bisphenol F and Bisphenol S in Seawater

A group of compounds structurally similar to bis(4-hydroxyphenyl)propane (bisphenol A, BPA) are called bisphenols (BPs), and some of them can partially replace BPA in industrial applications. The production and consumption of BPs other than BPA, especially those of bis(4-hydroxyphenyl)methane (bisphenol F, BPF) and bis(4-hydroxyphenyl)sulfone (bisphenol S, BPS), have increased recently, leading to their detection as contaminants in the aquatic environment. The three compounds tested 100% positive for estrus response in 1936 and concerns about their health risks have been increasing. Abundant data on degradation of bisphenols (BPs) has been published, but results for biodegradation of BPs in seawater are lacking. However, several research groups have focused on this topic recently. In this study, the biodegradation behaviors of three BPs, namely BPA, BPF and BPS, in seawater were investigated using TOC Handai (TOC, potential test) and river (sea) die-away (SDA, simulation test) methods, which are both a kind of river-die-away test. The main difference between the tests is that indigenous microcosms remain in the sampled raw seawater for the SDA experiments, but they are removed through filtration and dispersed into artificial seawater for the TOC experiments. The BPs, except for BPS, were degraded using both methods. The SDA method produced better biodegradation results than the TOC method in terms of degradation time (both lag and degradation periods). Biodegradation efficiencies were measured at 75–100% using the SDA method and 13–63% using the TOC method. BPF showed better degradation efficiency than BPA, BPF was > 92% and BPA 83% depleted according to the SDA tests. BPS degradation was not observed. As a conclusion, the biodegradability of the three BPs in seawater could be ranked as BPF > BPA ≫ BPS. BPF is more biodegradable than BPA in seawater and BPS is more likely to accumulate in the aquatic environment. BPS poses a lower risk to human health and to the environment than BPA or BPF but it is not amenable to biodegradation and might be persistent and become an ecological burden. Thus other degradation methods need to be found for the removal of BPS in the environment.

Characterization of a Bioflocculant Produced by Citrobacter sp. TKF04 from Acetic and Propionic Acids

A bacterial strain, TKF04, capable of producing a bioflocculant from acetic and/or propionic acids was isolated from a biofilm formed in inside a kitchen drain. It was identified as a Citrobacter based on its morphological and physiological characteristics and the partial sequences of its 16S rRNA. TKF04 produced the bioflocculant during the logarithmic phase of growth, and the optimum temperature and pH for the bioflocculant production were 30 degrees C and 7.2-10.0, respectively. It could utilize some organic acids and sugars for its growth as the sole carbon sources when yeast extract was supplemented; however, only acetate and propionate were found to be good substrates for the bioflocculant production. The crude bioflocculant could be recovered from the supernatant of the culture broth by ethanol precipitation and dialysis against deionized water. It was found to be effective for flocculation of a kaolin suspension, when added at a final concentration of 1-10 mg/l, over a wide range of pHs (2-8) and temperatures (approximately 3-95 degrees C), while the co-presence of cations (Na+, K+, Ca2+, Mg2+, Fe2+, Al3+ or Fe3+) did not enhance the flocculating activity. It could efficiently flocculate a variety of inorganic and organic suspended particles, including kaolin, diatomite, bentonite, activated carbon, soil and activated sludge. It contained glucosamine as the major component, and the molecular weight was estimated to be between 232 and 440 kDa by gel filtration. The observation that the flocculating activity was completely lost following chitinase treatment and its analysis with a Fourier transform infrared spectrometer suggested that the bioflocculant is a biopolymer structurally-similar to chitin or chitosan.

Factors affecting soluble selenium removal by a selenate-reducing bacterium Bacillus sp. SF-1

High concentrations of soluble selenium, selenate and selenite, have acute and chronic toxicity toward living things. With the aim of developing a biological process for selenium removal, the effects of a variety of parameters on the reduction of soluble selenium by a Bacillus sp. strain SF-1, which is capable of reductively transforming selenate into selenite and, subsequently, into nontoxic insoluble elemental selenium, were studied. The bacterial strain could effectively reduce 20 mM of selenate to selenite and 2 mM of selenite to elemental selenium in the presence of an appropriate carbon source and in the absence of oxygen. The reduction rate of selenate to selenite was much higher than that of selenite to elemental selenium, resulting in the transient accumulation of selenite during selenate reduction. The selenate reduction rate increased with increases in the selenate concentration up to 20 mM, while the rate of selenite reduction decreased sharply at selenite concentrations of more than 2 mM. The elemental selenium transformed from selenate via selenite was found both inside and outside the cells. Bacillus sp. SF-1 was able to utilize a variety of organic acids or sugars as a carbon source in selenate reduction. Although the copresence of sulfate did not inhibit selenate reduction, it was completely inhibited by some other oxyanions, including nitrate. A model sequencing batch system using the bacterial strain was developed and exhibited good performance in the treatment of wastewater containing high concentrations of selenate.

Design of PCR primers and gene probes for the general detection of bacterial populations capable of degrading aromatic compounds via catechol cleavage pathways.

For the general detection of bacterial populations capable of degrading aromatic compounds, two PCR primer sets were designed which can, respectively, amplify specific fragments from a wide variety of catechol 1,2-dioxygenase (C12O) and catechol 2,3-dioxygenase (C23O) genes. The C12O-targeting primer set (C12O primers) was designed based on the homologous regions of 11 C12O genes listed in the GenBank, while the C23O-targeting one (C23O primers) was designed based on those of 17 known C23O genes. Oligonucleotide probes (C12Op and C23Op) were also designed from the internal homologous regions to identify the amplified fragments. The specificity of the primer sets and probes was confirmed using authentic bacterial strains known to carry the C12O and/or C23O genes used for the primer and probe design. Various authentic bacterial strains carrying neither C12O nor C23O genes were used as negative controls. PCR with the C12O primers amplified DNA fragments of the expected sizes from 5 of the 6 known C12O-carrying bacterial strains tested, and positive signals were obtained from 4 of the 5 amplified fragments on Southern hybridization with the C12Op. The C23O primers amplified DNA fragments of the expected size from all the 11 tested C23O-carrying bacterial strains used for their design, while the C23Op detected positive signals in the amplified fragments from 9 strains. On the other hand, no DNA fragments were amplified from the negative controls. To evaluate the applicability of the designed primers and probes for the general detection of aromatic compound-degrading bacteria, they were applied to wild-type phenol- and/or benzoate-degrading bacteria newly isolated from a variety of environments. The C12O and/or C23O primers amplified DNA fragments of the expected sizes from 69 of the 106 wild-type strains tested, while the C12Op and/or C23Op detected positive signals in the amplified fragments from 63 strains. These results suggest that our primer and probe systems can detect a considerable proportion of bacteria which can degrade aromatic compounds via catechol cleavage pathways.

Evaluation of wastewater reclamation technologies based on in vitro and in vivo bioassays

When municipal secondary effluent is used as the main supplementation water source for surface water bodies, its potential adverse ecological effects should not be neglected. The objective of this work was to investigate the effectiveness of several technologies, i.e. combination of coagulation and sand filtration (CSF), ultraviolet (UV) irradiation, chlorination, ozonation, ultrafiltration (UF) and reverse osmosis filtration (RO), on the removal of acute ecotoxicity, genotoxicity and retinoic acid receptor (RAR) agonist activity from the municipal secondary effluent. The effects of treated effluents on the development of Japanese medaka (Oryzias latipes) embryos were also evaluated. The secondary effluent exhibited a mutagenic effect on Salmonella typhimurium strain TA 1535/pSK1002, acute invertebrate toxicity to Daphnia magna, and weak RAR alpha activity. RO and ozonation demonstrated remarkable removals of the genotoxic effect, acute toxicity and RAR activity from secondary effluent, while chlorination could elevate both genotoxicity and acute toxicity. CSF, UV, UF, chlorination as well as RO could decrease the 4-day mortality of medaka embryos and accordingly increase the hatching success rate, comparing with the secondary effluent. Ozonation at 4 mg/l and higher doses, however, elicited significantly higher 4-day mortality, leading to the reduction of the hatching success rate.

The degradability of biodegradable plastics in aerobic and anaerobic waste landfill model reactors

Degradabilities of four kinds of commercial biodegradable plastics (BPs), polyhydroxybutyrate and hydroxyvalerate (PHBV) plastic, polycaprolactone plastic (PCL), blend of starch and polyvinyl alcohol (SPVA) plastic and cellulose acetate (CA) plastic were investigated in waste landfill model reactors that were operated as anaerobically and aerobically. The application of forced aeration to the landfill reactor for supplying aerobic condition could potentially stimulate polymer-degrading microorganisms. However, the individual degradation behavior of BPs under the aerobic condition was completely different. PCL, a chemically synthesized BP, showed film breakage under the both conditions, which may have contributed to a reduction in the waste volume regardless of aerobic or anaerobic conditions. Effective degradation of PHBV plastic was observed in the aerobic condition, though insufficient degradation was observed in the anaerobic condition. But the aeration did not contribute much to accelerate the volume reduction of SPVA plastic and CA plastic. It could be said that the recalcitrant portions of the plastics such as polyvinyl alcohol in SPVA plastic and the highly substituted CA in CA plastic prevented the BP from degradation. These results indicated existence of the great variations in the degradability of BPs in aerobic and anaerobic waste landfills, and suggest that suitable technologies for managing the waste landfill must be combined with utilization of BPs in order to enhance the reduction of waste volume in landfill sites.

Biodegradation of a polyvinyl alcohol-starch blend plastic film

Attempts were made to elucidate the degradation mechanism of a polyvinyl alcohol (PVA)-starch blend plastic. A part of the starch fraction of this plastic was dissolved into an aqueous phase in a control test. Treatment with a PVA-degrading bacterium or enzyme gave a maximal weight loss of approximately 70% and film breakage occurred. Since this plastic contains 40% PVA, it is apparent that not only the PVA fraction but also a considerable portion of the starch fraction was lost from the film by treatment with the PVA-degrading enzyme. As the PVA-degrading bacterium and enzyme used here showed no starch-degrading activity, loss of the starch fraction seems to depend on its dissolution with degradation of the PVA fraction. These experimental results indicated that the degradation of the PVA fraction is an important requisite for complete degradation or decomposition of this plastic film.

Isolation and Characterization of a Novel Selenate-Reducing Bacterium, Bacillus sp. SF-1

A gram-positive, facultatively anaerobic, rod-shaped bacterium was isolated from selenium-polluted sediment and identified as Bacillus sp. The bacterium, designated strain SF-1, grows with lactate as an electron donor and selenate as an electron acceptor in the absence of oxygen and presence of yeast extract (selenate respiration). There is a stoichiometric balance between the cell growth, lactate consumption and selenate reduction. Strain SF-1 can completely reduce up to 1 mM selenate to amorphous elemental selenium with transient accumulation of selenite. Although about 20 mM selenate can be converted to selenite, only a small portion of the accumulated selenite is further reduced to elemental selenium probably due to its inhibitory effect. The optimal pH and temperature for the selenate reduction of strain SF-1 are approximately 8.0 and 30°C, respectively. The presence of nitrate inhibits the selenate reduction, suggesting a relationship between the nitrate and selenate reduction mechanisms. As strain SF-1 possesses the ability to convert toxic soluble selenium, selenate and selenite to insoluble elemental selenium which can easily be removed from an aqueous phase, it seems useful for detoxification and/or removal of soluble selenium from selenium-contaminated wastewater.

A novel control method for nitritation: The domination of ammonia-oxidizing bacteria by high concentrations of inorganic carbon in an airlift-fluidized bed reactor.

A novel nitritation method based on the addition of inorganic carbon (IC) was verified using an airlift-fluidized bed reactor packed with sponge cubes. A continuous-treatment experiment demonstrated that the type of nitrification-nitrite or nitrate accumulation-could be controlled by the addition of different alkalinity sources (NaHCO(3) or NaOH, respectively). The maximum rate of ammonia oxidation at 30 degrees C was 2.47kg-N/(m(3) d), with nitrate formation of less than 0.5% of the converted ammonia. Nitrite accumulation of over 90% was maintained stably over 250 days at 30 degrees C and was achieved even at 19 degrees C. Qualitative and quantitative shifts of nitrifying bacteria in the biofilm were monitored by real-time PCR and T-RFLP analysis. Ammonia-oxidizing bacteria (AOB) were dominant but nitrite-oxidizing bacteria (NOB) were eliminated in the reactor when NaHCO(3) was used as the alkalinity source. From the kinetic data, we inferred that high IC concentrations drive stable nitritation by promoting a higher growth rate for AOB than for NOB.

Effects of Inoculation of a Genetically Engineered Bacterium on Performance and Indigenous Bacteria of a Sequencing Batch Activated Sludge Process Treating Phenol

Abstract A genetically engineered microorganism (GEM) Pseudomonas putida BH (pS10-45), which was designed to exhibit higher phenol-degrading activity than the wild strain, was inoculated into a model activated sludge process to improve its phenol-treatment performance. The model activated sludge process was operated as a 24-h-cycle sequencing batch reactor in a shake flask, into which phenol-containing wastewater (500 mg/ l ) was fed in the form of a shock loading three times at 7-d intervals and, subsequently, semi-continuously (at 100–200 mg/ l ). After the shock loadings, the phenol-removal efficiency of the GEM-inoculated activated sludge was much enhanced in comparison to that of a control process without GEM-inoculation for as long as the GEM population survived at a relatively high level. During the semi-continuous feedings, the GEM-inoculated activated sludge settled much better than that in the control process, though phenol was completely removed in both processes. The improvement in the settling properties was gradually lost as the GEM population declined. It was also observed that GEM-inoculation had a considerable effect on the behavior of the indigenous phenol-degrading bacterial population, indicating that inoculation of the GEM delayed the occurrence of indigenous phenol-degraders. These results suggest that GEM-inoculation can be a useful means of improving phenol-treating activated sludge processes.