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Identification and abundance of Thiothrix in wastewater treatment plants
treating domestic wastewater using fluorescence in situ hybridization

ABSTRACT
CODE
821
W56

V. Romero, A. Zornoza, and J.L. Alonso
Instituto Universitario de Ingeniería del Agua y Medio Ambiente, (IIAMA). Universitát Politècnica de València, Spain (e-mail: jalonso@ihdr.upv.es).

INTRODUCTION
Bacteria that belong to the genus Thiothrix are characterized by distinctive morphological features, such as filamentous growth and accumulation of sulphur
granule when incubated in the presence of sulphide or thiosulphate. The Thiothrix morphotypes occur in municipal and industrial WWTPs with and without
nutrient removal [1]. Traditionally, the problems of biological bulking have been monitored by classical microscopy such as morphological observation and
polychromatic staining [2]. Few works have been carried out for the detection of Thiothrix in WWTP samples with molecular procedures such as the fluorescence
in situ hybridization (FISH) technique. In this study, we investigated several Spanish WWTPs with the FISH technique to analyze the composition of Thiothix
species and their relathionships with physico-chemical and operational parameters.

MATERIAL AND METHODS
The sampling period was conducted between February to November 2012 in 3
urban WWTPs with conventional activated sludge system (CAS) and 1 urban
WWTP with extended aeration system. Fortnightly samples of mixed liquor were
analyzed by light microscopy and quantitative FISH.
In the FISH analysis a set of 8 rRNA-targeted nucleic acid probes covering
Thiothrix genus and species were used (Table 1). The abundance of filamentous
bacteria in the 139 activated sludge samples was measured according to the
subjective scoring method of Eikelboom (2000) where observations are rated on
scale from 0 (none) to 5 (extensive growth). The hybridizations were performed at
46 º C for 2 hours. All the probes (Table 1), labelled at the 5’ end with Tamra, were
purchased from TibMobiol, Germany.
%FA: Formamide percentage; G123TC y Comp. TNI y TFR: Competitor probes

RESULTS
Thiothrix filaments were present in the four WWTP analyzed. In 92 (66,2 %) of the samples, Thiothrix filaments were observed with the probe G123T. It was
evident that mixed populations of Thiothrix (figure 1) were present in the activated sludge samples investigated, the observed differences were in the relative
abundance of the various groups. These findings were supported by the results obtained using conventional microscopy. T. eikelbomii (figure 2), T.
fructosivorans (figures 3) and T. nivea (figure 4) were common (FI>3) in two of the four WWTP analyzed. No fluorescence signal was detected with the probes G1B
(T. disciformis), G3M (T. flexilis) and Meg1028+Meg 983 (Meganema perideroedes). Redundancy analysis (RDA) ordination diagram (biplot) suggested different
behaviour among species within genus Thiothrix. T. eikelbomii showed a positive relationship with the reactor temperature (Tr) (figure 5). Conversely, T.
fructosivorans was negatively related with reactor temperature (Tr). T. nivea and T. fructosivorans were associated with high sludge retention time (SRT) values
and low values of organic loading rate (OLR). T. nivea showed a positive relationship with the hydraulic retention time (HRT) and negative with the influent
carbohydrates and proteins. T. eikelbomii and T. nivea were associated with nitrogen and phosphorus deficit (BOD5/TN/TP) (figure 6).

Figure 1: Thiothrix spp. (G123T probe), A:
phase contrast, B: epifluorescence 1000X
Figure 3: T. fructosivorans (TFR probe), A: phase contrast,
B: epifluorescence, 1000X

Figure 2: T. eikelbomii (G2M probe), A: phase
contrast, B: epifluorescence 1000X

A

B

Figure 5: RDA between Thiothrix species and
physico-chemical parameters

Figure 6: RDA between
operational parameters

Figure 4: T. nivea (TNI probe), A: phase contrast, B:
epifluorescence, 1000X

REFERENCES
[1] Eikelboom D (2000) Process control of activated sludge plants by microscopic investigation. IWA Publishing, London, England.
[2] Jenkins D., Richard M., Daigger G. (2004) Manual on cases and control of activated sludge bulking and foaming. Lewis Publishers, Chelsea, Michigan.

Thiothrix species and

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2013 - Estudio de las relaciones de las bacterias filamentosas no ramificadas...
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2016 - Estudio de la dinámica de protistas y metazoos en un reactor biológico...
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2014 - Estudio de las relaciones del morfotipo Nosotocoida limicola con los p...
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2014 - Identificación y cuantificación del morfotipo Haliscomenobacter hydros...
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2012 - Microscopía convencional versus FISH en la identificación, abundancia ...
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2017 - Plausible Bioindicators of Biological Nitrogen Removal Process in WWTPs
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Mais de WALEBUBLÉ (20)

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2015 - Archaeal populations in full-scale autotrophic nitrogen removal biorea...
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2007 - Modelizacion EDAR Guardamar
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2012 - Optimización de la explotación de un sistema MBR
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2016 - EXPERIENCIA PILOTO DE SIMULACIÓN PARA LA MEJORA DEL RENDIMIENTO DE ELI...
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2017 - Analysis of nitrifying microbial communities by FISH and 16S rRNA ampl...
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2013 - Estudio de las relaciones de las bacterias filamentosas no ramificadas...
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2012 - Microscopía convencional versus FISH en la identificación, abundancia ...
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2011 - Estudio de la población de bacterias nitrificantes y su relación con l...
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2013 - Identification and abundance of thiothrix in wwt ps treating domestic wastewater using fish

  • 1. Identification and abundance of Thiothrix in wastewater treatment plants treating domestic wastewater using fluorescence in situ hybridization ABSTRACT CODE 821 W56 V. Romero, A. Zornoza, and J.L. Alonso Instituto Universitario de Ingeniería del Agua y Medio Ambiente, (IIAMA). Universitát Politècnica de València, Spain (e-mail: jalonso@ihdr.upv.es). INTRODUCTION Bacteria that belong to the genus Thiothrix are characterized by distinctive morphological features, such as filamentous growth and accumulation of sulphur granule when incubated in the presence of sulphide or thiosulphate. The Thiothrix morphotypes occur in municipal and industrial WWTPs with and without nutrient removal [1]. Traditionally, the problems of biological bulking have been monitored by classical microscopy such as morphological observation and polychromatic staining [2]. Few works have been carried out for the detection of Thiothrix in WWTP samples with molecular procedures such as the fluorescence in situ hybridization (FISH) technique. In this study, we investigated several Spanish WWTPs with the FISH technique to analyze the composition of Thiothix species and their relathionships with physico-chemical and operational parameters. MATERIAL AND METHODS The sampling period was conducted between February to November 2012 in 3 urban WWTPs with conventional activated sludge system (CAS) and 1 urban WWTP with extended aeration system. Fortnightly samples of mixed liquor were analyzed by light microscopy and quantitative FISH. In the FISH analysis a set of 8 rRNA-targeted nucleic acid probes covering Thiothrix genus and species were used (Table 1). The abundance of filamentous bacteria in the 139 activated sludge samples was measured according to the subjective scoring method of Eikelboom (2000) where observations are rated on scale from 0 (none) to 5 (extensive growth). The hybridizations were performed at 46 º C for 2 hours. All the probes (Table 1), labelled at the 5’ end with Tamra, were purchased from TibMobiol, Germany. %FA: Formamide percentage; G123TC y Comp. TNI y TFR: Competitor probes RESULTS Thiothrix filaments were present in the four WWTP analyzed. In 92 (66,2 %) of the samples, Thiothrix filaments were observed with the probe G123T. It was evident that mixed populations of Thiothrix (figure 1) were present in the activated sludge samples investigated, the observed differences were in the relative abundance of the various groups. These findings were supported by the results obtained using conventional microscopy. T. eikelbomii (figure 2), T. fructosivorans (figures 3) and T. nivea (figure 4) were common (FI>3) in two of the four WWTP analyzed. No fluorescence signal was detected with the probes G1B (T. disciformis), G3M (T. flexilis) and Meg1028+Meg 983 (Meganema perideroedes). Redundancy analysis (RDA) ordination diagram (biplot) suggested different behaviour among species within genus Thiothrix. T. eikelbomii showed a positive relationship with the reactor temperature (Tr) (figure 5). Conversely, T. fructosivorans was negatively related with reactor temperature (Tr). T. nivea and T. fructosivorans were associated with high sludge retention time (SRT) values and low values of organic loading rate (OLR). T. nivea showed a positive relationship with the hydraulic retention time (HRT) and negative with the influent carbohydrates and proteins. T. eikelbomii and T. nivea were associated with nitrogen and phosphorus deficit (BOD5/TN/TP) (figure 6). Figure 1: Thiothrix spp. (G123T probe), A: phase contrast, B: epifluorescence 1000X Figure 3: T. fructosivorans (TFR probe), A: phase contrast, B: epifluorescence, 1000X Figure 2: T. eikelbomii (G2M probe), A: phase contrast, B: epifluorescence 1000X A B Figure 5: RDA between Thiothrix species and physico-chemical parameters Figure 6: RDA between operational parameters Figure 4: T. nivea (TNI probe), A: phase contrast, B: epifluorescence, 1000X REFERENCES [1] Eikelboom D (2000) Process control of activated sludge plants by microscopic investigation. IWA Publishing, London, England. [2] Jenkins D., Richard M., Daigger G. (2004) Manual on cases and control of activated sludge bulking and foaming. Lewis Publishers, Chelsea, Michigan. Thiothrix species and