Hua Yin

Biosorption of chromium from aqueous solution and electroplating wastewater using mixture of Candida lipolytica and dewatered sewage sludge

In this study, the objective was to investigate Cr removal from aqueous solutions, as well as Cr, Cu, Ni and Zn from electroplating wastewaters by the mixture of Candida lipolytica and sewage sludge. The bioreduction ratios of Cr(VI) and the removal ratios of total Cr showed that initial pH, biosorbent dosage and contact time were the important parameters for Cr biosorption. The range of optimal pH for the mixture (1-5) was wider than C. lipolytica (1-4) and sewage sludge (2-4), respectively. Biosorption and bioreduction potentials of living C. lipolytica were better than those of cell wall and cytoplasm. Bonded hydroxyl group, CH(2) asymmetric stretch, amide I, amide II, amide III, secondary amide, pyridine(I)beta(C-H) and pyridine(II)beta(C-H) were detected in the biosorbent and they were the functional groups for binding Cr. The effect of Cu and Zn in combination was significant on the removal of total Cr and the bioreduction of Cr(VI).

Biodegradation of anthracene by Aspergillus fumigatus

An anthracene-degrading strain, identified as Aspergillus fumigatus, showed a favorable ability in degradation of anthracene. The degradation efficiency could be maintained at about 60% after 5d with initial pH of the medium kept between 5 and 7.5, and the optimal temperature of 30 °C. The activity of this strain was not affected significantly by high salinity. Exploration on co-metabolism showed that the highest degradation efficiency was reached at equal concentration of lactose and anthracene. Excessive carbon source would actually hamper the degradation efficiency. Meanwhile, the strain could utilize some aromatic hydrocarbons such as benzene, toluene, phenol etc. as sole source of carbon and energy, indicating its degradation diversity. Experiments on enzymatic degradation indicated that extracellular enzymes secreted by A. fumigatus could metabolize anthracene effectively, in which the lignin peroxidase may be the most important constituent. Analysis of ion chromatography showed that the release of anions of A. fumigatus was not affected by addition of anthracene. GC-MS analysis revealed that the molecular structure of anthracene changed with the action of the microbe, generating a series of intermediate compounds such as phthalic anhydride, anthrone and anthraquinone by ring-cleavage reactions.

Removal of Cr(VI) and Ni(II) from aqueous solution by fused yeast: Study of cations release and biosorption mechanism

Biosorption of Cr(VI) and Ni(II) by a fused yeast from Candida tropicalis and Candida lipolytica under varying range of pH, initial metal concentration and reaction time was investigated. Net cation release and Cr removal reached 2.000 mmol/l and 81.37% when treating 20mg/l Cr(VI) at pH 2 with 25mg/l biomass for 30 min, while for Ni were 0.351 mmol/l and 64.60%, respectively. Trace metal elements such as Co, Cu, Mn, Mo, Se and Zn played active role in biosorption as important ingredients of functional enzymes. Cr(VI) was reduced to less toxic Cr(III) and chelated with extracellular secretions, and further accumulated inside the cells. For Ni biosorption, however, largely a passive uptake process influenced by ion gradient led to lower adsorption capacity and cations release. Fourier transform infrared (FTIR) spectrum analysis indicated that amide and pyridine on cells were involved in binding with Cr, but for Ni, bound-OH and nitro-compounds were the main related functional groups. Scanning electron microscopy (SEM) and atomic force microscopy (AFM) analysis confirmed that considerable amounts of metals precipitated on cell surface when dealing with high concentration metals.

Improvement of chromium biosorption by UV–HNO2 cooperative mutagenesis in Candida utilis

The present study focused on the improvement of chromium resistance and biosorption efficiency in Candida utilis CR-001 utilizing protoplast mutagenesis technology. Through ultraviolet (UV) radiation, HNO(2) treatment and chromium acclimatization, six preferred mutants of C. utilis CR-001 were screened out, namely, CRU132-26, CRC7-2, CRC2811-1, CRC2811-2, CRC2814-8 and CRY182-1. The removal efficiency of these mutants for 20mg/L Cr(VI) solutions were 85.6%, 95.2%, 87.0%, 82.5%, 94.7% and 82.7%, respectively, noticeably greater than that of the parent strain CR-001 (79.5%). Furthermore, CRC2811-1 exhibited outstanding application potential with high removal efficiency and low dosage over a wide range of pH. Cell surface and inner details of CRC2811-1 and its parent strain CR-001 were analyzed by scanning electron microscopy (SEM) and atomic force microscopy (AFM) in order to explore possible changes caused by inducement. The results showed that Cr-sorption of CR-001 mainly depended on intracellular accumulation, but for CRC2811-1, cell surface deposition was also involved in improving its chromium biosorption capacity.

Biodegradation of Benzo[a]pyrene by Arthrobacter oxydans B4

A bacterial strain, Arthrobacter oxydans (B4), capable of degrading benzo[a]pyrene (BaP) in water body, was isolated from a polycyclic aromatic hydrocarbons-contaminated site. Effects of different factors, such as reaction time, pH value, temperature and organic nutrients, on BaP biodegradation by the strain B4 were studied. After 5 d treatment, the concentration of BaP in mineral salts medium was reduced to 0.318 mg L−1, compared to the initial concentration of 1.000 mg L−1. There was a process of acid formation during the degradation with pH falling from initial 7.01 to 4.61 at 5 d, so keeping the water body under slightly alkaline condition was propitious to BaP degradation. Strain B4 efficiently degraded BaP at 20 to 37 °C with addition of organic nutrients. The biodegradation and transformation of BaP mainly occurred on cell surfaces, and extracellular secretions played an important role in these processes. Fourier transform infrared spectroscopy and gas chromatograph-mass spectrometer analyses of metabolites showed that ring cleavage occurred in the BaP degradation process and the resulting metabolically utilizable substrates were generated as sole carbon sources for B4 growth. Furthermore, mineralization extent of metabolites was verified by determining the total organic carbon and inorganic carbon in the degradation system.