Removal of tetrachlorobisphenol A and the effects on bacterial communities in a hybrid sequencing biofilm batch reactor-constructed wetland system

Xiaohui Wang , Shuai Du , Tao Ya , Zhiqiang Shen , Jing Dong , Xiaobiao Zhu

Front. Environ. Sci. Eng. ›› 2019, Vol. 13 ›› Issue (1) : 14

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Front. Environ. Sci. Eng. ›› 2019, Vol. 13 ›› Issue (1) : 14 DOI: 10.1007/s11783-019-1097-4
RESEARCH ARTICLE
RESEARCH ARTICLE

Removal of tetrachlorobisphenol A and the effects on bacterial communities in a hybrid sequencing biofilm batch reactor-constructed wetland system

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Abstract

SBBR-CW system was proposed to effectively treat wastewater containing TCBPA.

CW unit contributed more than SBBR to the removal of TCBPA.

TCBPA changed the composition and structure of bacterial community in the system.

GAOs massively grew in SBBR, but did not deteriorate TP removal efficiency.

Tetrachlorobisphenol A (TCBPA) released into the sewage may cause environmental pollution and health risk to human beings. The objective of this study was to investigate the removal of TCBPA and bacterial community structures in a laboratory-scale hybrid sequencing biofilm batch reactor (SBBR)-constructed wetland (CW) system. The results showed that the removal efficiency of chemical oxidation demand (COD), ammonia, total nitrogen and total phosphorus in the SBBR-CW system was 96.7%, 97.3%, 94.4%, and 88.6%, respectively. At the stable operation stage, the system obtained a 71.7%±1.8% of TCBPA removal efficiency with the influent concentration at 200 mg/L. Illumina MiSeq sequencing of 16S rRNA gene revealed that the presence of TCBPA not only reduced the bacterial diversity in the SBBR-CW system, but also altered the composition and structure of bacterial community. After the addition of TCBPA, Proteobacteria increased from 31.3% to 38.7%, while Acidobacteria and Parcubacteria decreased greatly in the SBBR. In contrast, Acidobacteria replaced Proteobacteria as the dominant phylum in the upper soils of CW. The results indicated that TCBPA stimulated the growth of GAOs in the SBBR without deteriorating the phosphorus removal due to the presence of sufficient carbon sources. The ammonia oxidizing bacteria, Nitrosomonas, and denitrification bacteria, Hyphomicrobium and Pseudomonas, were inhibited by TCBPA, resulting in a decreasing the removal efficiency of TN and ammonia.

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Keywords

SBBR / Constructed wetland / Tetrachlorobisphenol A / Microbial community structure

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Xiaohui Wang, Shuai Du, Tao Ya, Zhiqiang Shen, Jing Dong, Xiaobiao Zhu. Removal of tetrachlorobisphenol A and the effects on bacterial communities in a hybrid sequencing biofilm batch reactor-constructed wetland system. Front. Environ. Sci. Eng., 2019, 13(1): 14 DOI:10.1007/s11783-019-1097-4

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References

[1]

APHA AWWA, WEF (1998). Standard methods for the examination of water and wastewater. 20th ed. Washington: American Public Health Association

[2]

Arias D M, Uggetti E, García-Galán M J, García J (2017). Cultivation and selection of cyanobacteria in a closed photobioreactor used for secondary effluent and digestate treatment. Science of the Total Environment, 587-588: 157–167

[3]

Aruoja V, Sihtmäe M, Dubourguier H C, Kahru A (2011). Toxicity of 58 substituted anilines and phenols to algae Pseudokirchneriella subcapitata and bacteria Vibrio fischeri: Comparison with published data and QSARs. Chemosphere, 84(10): 1310–1320

[4]

Carvalheira M, Oehmen A, Carvalho G, Eusébio M, Reis M A M (2014a). The impact of aeration on the competition between polyphosphate accumulating organisms and glycogen accumulating organisms. Water Research, 66: 296–307

[5]

Carvalheira M, Oehmen A, Carvalho G, Reis M A M (2014b). Survival strategies of polyphosphate accumulating organisms and glycogen accumulating organisms under conditions of low organic loading. Bioresource Technology, 172: 290–296

[6]

Chang B V, Liu J H, Liao C S (2014). Aerobic degradation of bisphenol-A and its derivatives in river sediment. Environmental Technology, 35(1-4): 416–424

[7]

Chen M, Fan Z, Zhao F, Gao F, Mu D, Zhou Y, Shen H, Hu J (2016). Occurrence and maternal transfer of chlorinated bisphenol A and nonylphenol in pregnant women and their matching embryos. Environmental Science & Technology, 50(2): 970–977

[8]

Crocetti G R, Banfield J F, Keller J, Bond P L, Blackall L L (2002). Glycogen-accumulating organisms in laboratory-scale and full-scale wastewater treatment processes. Microbiology, 148(Pt 11): 3353–3364

[9]

Ge G, Zhao J, Chen A, Hu B, Chen Y, Gao K, Li X, Ding X (2018). Nitrogen removal and nitrous oxide emission in an anaerobic/oxic/anoxic sequencing biofilm batch reactor. Environmental Engineering Science, 35(1): 19–26

[10]

Horikoshi S, Miura T, Kajitani M, Horikoshi N, Serpone N (2008). Photodegradation of tetrahalobisphenol-A (X= Cl, Br) flame retardants and delineation of factors affecting the process. Applied Catalysis B: Environmental, 84(3–4): 797–802

[11]

Hu Z, Ferraina R A, Ericson J F, Mackay A A, Smets B F (2005). Biomass characteristics in three sequencing batch reactors treating a wastewater containing synthetic organic chemicals. Water Research, 39(4): 710–720

[12]

Mao Y, Xia Y, Zhang T (2013). Characterization of Thauera-dominated hydrogen-oxidizing autotrophic denitrifying microbial communities by using high-throughput sequencing. Bioresource Technology, 128: 703–710

[13]

McIlroy S, Seviour R J (2009). Elucidating further phylogenetic diversity among the Defluviicoccus-related glycogen-accumulating organisms in activated sludge. Environmental Microbiology Reports, 1(6): 563–568

[14]

McIlroy S J, Albertsen M, Andresen E K, Saunders A M, Kristiansen R, Stokholm-Bjerregaard M, Nielsen K L, Nielsen P H (2014). ‘Candidatus Competibacter’-lineage genomes retrieved from metagenomes reveal functional metabolic diversity. ISME Journal, 8(3): 613–624

[15]

Miao L, Zhang Q, Wang S, Li B, Wang Z, Zhang S, Zhang M, Peng Y (2018). Characterization of EPS compositions and microbial community in an Anammox SBBR system treating landfill leachate. Bioresource Technology, 249: 108–116

[16]

Molina-Molina J M, Amaya E, Grimaldi M, Sáenz J M, Real M, Fernández M F, Balaguer P, Olea N (2013). In vitro study on the agonistic and antagonistic activities of bisphenol-S and other bisphenol-A congeners and derivatives via nuclear receptors. Toxicology and Applied Pharmacology, 272(1): 127–136

[17]

Philips J, Haest P J, Springael D, Smolders E (2013). Inhibition of Geobacter dechlorinators at elevated trichloroethene concentrations is explained by a reduced activity rather than by an enhanced cell decay. Environmental Science & Technology, 47(3): 1510–1517

[18]

Riu A, le Maire A, Grimaldi M, Audebert M, Hillenweck A, Bourguet W, Balaguer P, Zalko D (2011). Characterization of novel ligands of ERa, Erb, and PPARg: the case of halogenated bisphenol A and their conjugated metabolites. Toxicological Sciences, 122(2): 372–382

[19]

Ronen Z, Abeliovich A (2000). Anaerobic-aerobic process for microbial degradation of tetrabromobisphenol A. Applied and Environmental Microbiology, 66(6): 2372–2377

[20]

Rosenkranz F, Cabrol L, Carballa M, Donoso-Bravo A, Cruz L, Ruiz-Filippi G, Chamy R, Lema J M (2013). Relationship between phenol degradation efficiency and microbial community structure in an anaerobic SBR. Water Research, 47(17): 6739–6749

[21]

Sellström U, Bo J (1995). Analysis of tetrabromobisphenol A in a product and environmental samples. Chemosphere, 31(4): 3085–3092

[22]

Simon M I, Seviour R J (2009). Elucidating further phylogenetic diversity among the Defluviicoccus-related glycogen-accumulating organisms in activated sludge. Environmental Microbiology Reports, 1(6): 563–568

[23]

Singh M, Srivastava R K (2011). Sequencing batch reactor technology for biological wastewater treatment: A review. Asia-Pacific Journal of Chemical Engineering, 6(1): 3–13

[24]

Song M, Liang D, Liang Y, Chen M, Wang F, Wang H, Jiang G (2014). Assessing developmental toxicity and estrogenic activity of halogenated bisphenol A on zebrafish (Danio rerio). Chemosphere, 112: 275–281

[25]

Spieck E, Hartwig C, McCormack I, Maixner F, Wagner M, Lipski A, Daims H (2006). Selective enrichment and molecular characterization of a previously uncultured Nitrospira-like bacterium from activated sludge. Environmental Microbiology, 8(3): 405–415

[26]

Sun H, Shen O X, Wang X R, Zhou L, Zhen S Q, Chen X D (2009). Anti-thyroid hormone activity of bisphenol A, tetrabromobisphenol A and tetrachlorobisphenol A in an improved reporter gene assay. Toxicology In Vitro, 23(5): 950–954

[27]

Tang C C, Tian Y, Liang H, Zuo W, Wang Z W, Zhang J, He Z W (2018). Enhanced nitrogen and phosphorus removal from domestic wastewater via algae-assisted sequencing batch biofilm reactor. Bioresource Technology, 250: 185–190

[28]

Terasaki M, Kosaka K, Kunikane S, Makino M, Shiraishi F (2011). Assessment of thyroid hormone activity of halogenated bisphenol A using a yeast two-hybrid assay. Chemosphere, 84(10): 1527–1530

[29]

Thomsen C, Lundanes E, Becher G (2015). A simplified method for determination of tetrabromobisphenol A and polybrominated diphenyl ethers in human plasma and serum. Journal of Separation Science, 24(4): 282–290

[30]

Yang Y, Lu L, Zhang J, Yang Y, Wu Y, Shao B (2014). Simultaneous determination of seven bisphenols in environmental water and solid samples by liquid chromatography-electrospray tandem mass spectrometry. Journal of Chromatography. A, 1328: 26–34

[31]

Yang Y, Zhang L, Cheng J, Zhang S, Li X, Peng Y (2018). Microbial community evolution in partial nitritation/anammox process: From sidestream to mainstream. Bioresource Technology, 251: 327–333

[32]

Ye G, Chen Y, Wang H O, Ye T, Lin Y, Huang Q, Chi Y, Dong S (2016). Metabolomics approach reveals metabolic disorders and potential biomarkers associated with the developmental toxicity of tetrabromobisphenol A and tetrachlorobisphenol A. Scientific Reports, 6(1): 35257

[33]

Yin N, Liang S, Liang S, Yang R, Hu B, Qin Z, Liu A, Faiola F (2018). TBBPA and its alternatives disturb the early stages of neural development by interfering with the NOTCH and WNT pathways. Environmental Science & Technology, 52(9): 5459–5468

[34]

Yuan S Y, Chen S J, Chang B V (2011). Anaerobic degradation of tetrachlorobisphenol-A in river sediment. International Biodeterioration & Biodegradation, 65(1): 185–190

[35]

Zeng R J, van Loosdrecht M C, Yuan Z, Keller J (2003). Metabolic model for glycogen-accumulating organisms in anaerobic/aerobic activated sludge systems. Biotechnology and Bioengineering, 81(1): 92–105

[36]

Zhang J, Liu S C, Li L L, Ren Y, Feng C H, Wei C H, Li Y P, Huang Z L (2017). Anaerobic dechlorination of tetrachlorobisphenol A in river sediment and associated changes in bacterial communities. Water, Air, and Soil Pollution, 228(2): 78

[37]

Zhang T, Liu Y, Fang H H P (2005). Effect of pH change on the performance and microbial community of enhanced biological phosphate removal process. Biotechnology and Bioengineering, 92(2): 173–182

[38]

Zhang Y, Cong J, Lu H, Li G, Qu Y, Su X, Zhou J, Li D (2014). Community structure and elevational diversity patterns of soil Acidobacteria. Journal of Environmental Sciences (China), 26(8): 1717–1724

[39]

Zheng D, Chang Q, Gao M, She Z, Jin C, Guo L, Zhao Y, Wang S, Wang X (2016). Performance evaluation and microbial community of a sequencing batch biofilm reactor (SBBR) treating mariculture wastewater at different chlortetracycline concentrations. Journal of Environmental Management, 182: 496–504

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