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PLOS ONE  2014 

Bacterial Community Dynamics and Taxa-Time Relationships within Two Activated Sludge Bioreactors

DOI: 10.1371/journal.pone.0090175

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Abstract:

Background Biological activated sludge process must be functionally stable to continuously remove contaminants while relying upon the activity of complex microbial communities. However the dynamics of these communities are as yet poorly understood. A macroecology metric used to quantify community dynamic is the taxa-time relationship (TTR). Although the TTR of animal and plant species has been well documented, knowledge is still lacking in regard to TTR of microbial communities in activated sludge bioreactors. Aims 1) To characterize the temporal dynamics of bacterial taxa in activated sludge from two bioreactors of different scale and investigate factors affecting such dynamics; 2) to evaluate the TTRs of activated sludge microbial communities in two bioreactors of different scale. Methods Temporal variation of bacterial taxa in activated sludge collected from a full- and lab-scale activated sludge bioreactor was monitored over a one-year period using pyrosequencing of 16S rRNA genes. TTR was employed to quantify the bacterial taxa shifts based on the power law equation S = cTw. Results The power law exponent w for the full-scale bioreactor was 0.43 (R2 = 0.970), which is lower than that of the lab-scale bioreactor (w = 0.55, R2 = 0.971). The exponents for the dominant phyla were generally higher than that of the rare phyla. Canonical correspondence analysis (CCA) result showed that the bacterial community variance was significantly associated with water temperature, influent (biochemical oxygen demand) BOD, bioreactor scale and dissolved oxygen (DO). Variance partitioning analyses suggested that wastewater characteristics had the greatest contribution to the bacterial community variance, explaining 20.3% of the variance of bacterial communities independently, followed by operational parameters (19.9%) and bioreactor scale (3.6%). Conclusions Results of this study suggest bacterial community dynamics were likely driven partly by wastewater and operational parameters and provide evidence that the TTR may be a fundamental ecological pattern in macro- and microbial systems.

References

[1]  Gentile ME, Jessup CM, Nyman JL, Criddle CS (2007) Correlation of functional instability and community dynamics in denitrifying dispersed-growth reactors. Appl Environ Microb 73: 680–690. doi: 10.1128/aem.01519-06
[2]  Rittmann BE, Hausner M, Loffler F, Love NG, Muyzer G, et al. (2006) A vista for microbial ecology and environmental biotechnology. Environ Sci Technol 40: 1096–1103. doi: 10.1021/es062631k
[3]  Briones A, Raskin L (2003) Diversity and dynamics of microbial communities in engineered environments and their implications for process stability. Curr Opin Biotech 14: 270–276. doi: 10.1016/s0958-1669(03)00065-x
[4]  Wang X, Wen X, Xia Y, Hu M, Zhao F, et al. (2012) Ammonia oxidizing bacteria community dynamics in a pilot-scale wastewater treatment plant. Plos One 7: e36272. doi: 10.1371/journal.pone.0036272
[5]  Wells GF, Park HD, Yeung CH, Eggleston B, Francis CA, et al. (2009) Ammonia-oxidizing communities in a highly aerated full-scale activated sludge bioreactor: betaproteobacterial dynamics and low relative abundance of Crenarchaea. Environ Microbiol 11: 2310–2328. doi: 10.1111/j.1462-2920.2009.01958.x
[6]  Gentile ME, Nyman JL, Criddle CS (2007) Correlation of patterns of denitrification instability in replicated bioreactor communities with shifts in the relative abundance and the denitrification patterns of specific populations. ISME J 1: 714–728. doi: 10.1038/ismej.2007.87
[7]  Slater FR, Johnson CR, Blackall LL, Beiko RG, Bond PL (2010) Monitoring associations between clade-level variation, overall community structure and ecosystem function in enhanced biological phosphorus removal (EBPR) systems using terminal-restriction fragment length polymorphism (T-RFLP). Water Res 44: 4908–4923. doi: 10.1016/j.watres.2010.07.028
[8]  Fernandez AS, Hashsham SA, Dollhopf SL, Raskin L, Glagoleva O, et al. (2000) Flexible community structure correlates with stable community function in methanogenic bioreactor communities perturbed by glucose. Appl Environ Microb 66: 4058–4067. doi: 10.1128/aem.66.9.4058-4067.2000
[9]  Ofiteru ID, Lunn M, Curtis TP, Wells GF, Criddle CS, et al. (2010) Combined niche and neutral effects in a microbial wastewater treatment community. Proc Natl Acad Sci USA 107: 15345–15350. doi: 10.1073/pnas.1000604107
[10]  Wells GF, Park HD, Eggleston B, Francis CA, Criddle CS (2011) Fine-scale bacterial community dynamics and the taxa-time relationship within a full-scale activated sludge bioreactor. Water Res 45: 5476–5488. doi: 10.1016/j.watres.2011.08.006
[11]  van der Gast CJ, Ager D, Lilley AK (2008) Temporal scaling of bacterial taxa is influenced by both stochastic and deterministic ecological factors. Environ Microbiol 10: 1411–1418. doi: 10.1111/j.1462-2920.2007.01550.x
[12]  Kim T-S, Jeong J-Y, Wells GF, Park H-D (2013) General and rare bacterial taxa demonstrating different temporal dynamic patterns in an activated sludge bioreactor. Appl Microbiol Biot 97: 1755–1765. doi: 10.1007/s00253-012-4002-7
[13]  Shade A, Peter H, Allison SD, Baho DL, Berga M, et al. (2012) Fundamentals of microbial community resistance and resilience. Front Microbiol 3: 417. doi: 10.3389/fmicb.2012.00417
[14]  Werner JJ, Knights D, Garcia ML, Scalfone NB, Smith S, et al. (2011) Bacterial community structures are unique and resilient in full-scale bioenergy systems. Proc Natl Acad Sci USA 108: 4158–4163. doi: 10.1073/pnas.1015676108
[15]  Cocolin L, Bisson LF, Mills DA (2000) Direct profiling of the yeast dynamics in wine fermentations. Fems Microbiol Lett 189: 81–87. doi: 10.1111/j.1574-6968.2000.tb09210.x
[16]  Shade A, Gregory Caporaso J, Handelsman J, Knight R, Fierer N (2013) A meta-analysis of changes in bacterial and archaeal communities with time. ISME J 7: 1493–1506. doi: 10.1038/ismej.2013.54
[17]  Adler PB, White EP, Lauenroth WK, Kaufman DM, Rassweiler A, et al. (2005) Evidence for a general species-time-area relationship. Ecology 86: 2032–2039. doi: 10.1890/05-0067
[18]  White EP, Adler PB, Lauenroth WK, Gill RA, Greenberg D, et al. (2006) A comparison of the species-time relationship across ecosystems and taxonomic groups. Oikos 112: 185–195. doi: 10.1111/j.0030-1299.2006.14223.x
[19]  Matthews B, Pomati F (2012) Reversal in the relationship between species richness and turnover in a phytoplankton community. Ecology 93: 2435–2447. doi: 10.1890/11-2289.1
[20]  Ye L, Shao MF, Zhang T, Tong AHY, Lok S (2011) Analysis of the bacterial community in a laboratory-scale nitrification reactor and a wastewater treatment plant by 454-pyrosequencing. Water Res 45: 4390–4398. doi: 10.1016/j.watres.2011.05.028
[21]  Wang X, Hu M, Xia Y, Wen X, Ding K (2012) Pyrosequencing analysis of bacterial diversity in 14 wastewater treatment systems in china. Appl Environ Microb 78: 7042–7047. doi: 10.1128/aem.01617-12
[22]  Marzorati M, Wittebolle L, Boon N, Daffonchio D, Verstraete W (2008) How to get more out of molecular fingerprints: practical tools for microbial ecology. Environ Microbiol 10: 1571–1581. doi: 10.1111/j.1462-2920.2008.01572.x
[23]  Wang XH, Wen XH, Yan HJ, Ding K, Zhao F, et al. (2011) Bacterial community dynamics in a functionally stable pilot-scale wastewater treatment plant. Bioresource Technol 102: 2352–2357. doi: 10.1016/j.biortech.2010.10.095
[24]  Zhang T, Shao MF, Ye L (2012) 454 Pyrosequencing reveals bacterial diversity of activated sludge from 14 sewage treatment plants. ISME J 6: 1137–1147. doi: 10.1038/ismej.2011.188
[25]  Hu M, Wang X, Wen X, Xia Y (2012) Microbial community structures in different wastewater treatment plants as revealed by 454-pyrosequencing analysis. Bioresource Technol 117: 72–79. doi: 10.1016/j.biortech.2012.04.061
[26]  Wittebolle L, Vervaeren H, Verstraete W, Boon N (2008) Quantifying community dynamics of nitrifiers in functionally stable reactors. Appl Environ Microb 74: 286–293. doi: 10.1128/aem.01006-07
[27]  Siggins A, Enright AM, O'Flaherty V (2011) Temperature dependent (37-15 degrees C) anaerobic digestion of a trichloroethylene-contaminated wastewater. Bioresource Technol 102: 7645–7656. doi: 10.1016/j.biortech.2011.05.055
[28]  Pholchan MK, Baptista JD, Davenport RJ, Curtis TP (2010) Systematic study of the effect of operating variables on reactor performance and microbial diversity in laboratory-scale activated sludge reactors. Water Res 44: 1341–1352. doi: 10.1016/j.watres.2009.11.005
[29]  Liu G, Wang J (2013) Long-Term Low DO Enriches and Shifts Nitrifier Community in Activated Sludge. Environ Sci Technol 47: 5109–5117. doi: 10.1021/es304647y
[30]  Park HD, Noguera DR (2004) Evaluating the effect of dissolved oxygen on ammonia-oxidizing bacterial communities in activated sludge. Water Res 38: 3275–3286. doi: 10.1016/j.watres.2004.04.047
[31]  van der Gast CJ, Jefferson B, Reid E, Robinson T, Bailey MJ, et al. (2006) Bacterial diversity is determined by volume in membrane bioreactors. Environ Microbiol 8: 1048–1055. doi: 10.1111/j.1462-2920.2006.00996.x
[32]  Ayarza JM, Erijman L (2011) Balance of Neutral and Deterministic Components in the Dynamics of Activated Sludge Floc Assembly. Microbial Ecol 61: 486–495. doi: 10.1007/s00248-010-9762-y
[33]  Curtis TP, Sloan WT (2006) Towards the design of diversity: stochastic models for community assembly in wastewater treatment plants. Water Sci Technol 54: 227–236. doi: 10.2166/wst.2006.391
[34]  Sloan WT, Lunn M, Woodcock S, Head IM, Nee S, et al. (2006) Quantifying the roles of immigration and chance in shaping prokaryote community structure. Environ Microbiol 8: 732–740. doi: 10.1111/j.1462-2920.2005.00956.x
[35]  Graham DW, Knapp CW, Van Vleck ES, Bloor K, Lane TB, et al. (2007) Experimental demonstration of chaotic instability in biological nitrification. ISME J 1: 385–393. doi: 10.1038/ismej.2007.45
[36]  McGlinn DJ, Palmer MW (2009) Modeling the sampling effect in the species-time-area relationship. Ecology 90: 836–846. doi: 10.1890/08-0377.1

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