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A New Species of the Genus Metacystis (Ciliophora, Prostomatida, Metacystidae)
from a Wastewater Treatment Plant
LUCI´A ARREGUI,a
BLANCA PE´ REZ-UZ,a
ANDRE´ S ZORNOZAb
and SUSANA SERRANOa
a
Departamento de Microbiologı´a III, Facultad de Biologı´a, Universidad Complutense, 28040 Madrid, Spain, and
b
Grupo Aguas de Valencia, EDAR Quart-Benager, EPSAR, Valencia, Spain
ABSTRACT. Unusual prostomatid specimens were found in the biological reactor of a wastewater treatment plant in a health resort in
Valencia, Spain. These ciliates were attached to flocs unlike other free-swimming prostomatid ciliates described to date in the mixed liquor
of activated sludge plants. The morphological study of this species led to a typically different combination of characteristics: elongated
cell shape, 20–30 somatic kineties, 2 perioral kineties, and 1 circumoral kinety, 1 large vacuole protruding at the terminal end, a lorica
tapered toward the aperture with a smooth neck, and 11–16 annular ridges. These characteristics place this representative as a new species
of the genus Metacystis—Metacystis galiani n. sp. This species became the dominant population within the biological reactor when high
values of conductivity (4,244 mS/cm) and temperature (26.8 1C) were recorded.
Key Words. Activated sludge, high conductivity habitat, protist.
BIOLOGICAL reactors of sewage treatment plants receive in-
puts with different physical–chemical characteristics that de-
termine variable biocenosis structures. The main components of
this ecosystem are bacteria that reach 90–95% of the biomass,
while protists and other microorganisms represent just 5–10% of
the total biomass (Bitton 2005). The established community is
organized as bioaggregates or flocs in which the biotic component
is embedded in a complex matrix composed of organic and inor-
ganic particles (contained in the sewage) and extracellular poly-
meric substances produced by the microbial activity (Barker and
Stuckey 1999; Laspidou and Rittmann 2002).
Ciliates, often one of the most significant groups of protists
within this ecosystem, have been divided into two categories de-
pending on their ecological niche inside the reactor (Madoni
1988; Martı´n-Cereceda, Serrano, and Guinea 1996, 2001; Poole
1984): (i) associated with flocs are two functional groups—crawl-
ing ciliates with flattened bodies and a specialized ventral ciliature
allowing the movement on the floc surface and sessile ciliates at-
tached to the floc through stalks or adhesive structures; and (ii)
free-swimming ciliates moving freely in the mixed liquor. The
first category of ciliates is generally more abundant (Curds and
Cockburn 1970; Madoni 1988; Martı´n-Cereceda, Serrano, and
Guinea 1996).
Species of prostomatid ciliates are scarce in conventional ac-
tivated sludge wastewater treatment plants (WWTP), never reach-
ing higher numbers or reported as the dominant population under
stable reactor conditions (Curds 1969; Esteban, Te´llez, and Ba-
utista 1991; Madoni 1988; Martı´n-Cereceda, Serrano, and Guinea
1996). Exceptionally the prostomatid swimming ciliate Coleps
hirtus has been described in biological reactors showing high effi-
ciency in nitrification processes (Bick 1972; Madoni, Davoli, and
Chierici 1993; Poole 1984). However, our group showed recently
that several prostomatid species could be stable components in the
biological communities of activated sludge plants with advanced
nitrogen removal systems (Pe´rez-Uz et al. 2009).
The aim of this work was to characterize a sessile prostomatid
ciliate found as a stable population associated with flocs in the
biological reactor of a WWTP from a health resort with a very
specific set of physical–chemical conditions. We conclude that
this is a new species Metacystis galiani n. sp.
MATERIALS AND METHODS
Sessile ciliates were sampled from the biological reactor of a
WWTP of a health resort located in Cofrentes, Valencia, Spain
(391130
N, 11040
W). Samples were collected in plastic bottles and
taken to the laboratory for analysis. Fifty-microliter aliquots con-
taining living cells were observed with a phase contrast micro-
scope using either an Olympus BH-5 (Olympus Optical Espan˜a
S. A., Madrid, Spain) or a Zeiss Axiostar microscope (VWR In-
ternational Eurolab S. L., Barcelona, Spain). Digital images were
taken with a digital camera (Olympus Camedia C-5050 or a Dig-
ital Still Camera Sony DKC-CM30) attached to the microscope.
Linear measurements were obtained from the digital images with
Adobe Photoshop 6.0 after calibration with a 1-mm Zeiss stage
micrometer.
Ciliates were stained using the pyridinated silver carbonate
method of Ferna´ndez-Galiano (1976, 1994) and the protargol im-
pregnation modification of Wilbert (1975). Permanent slides of
both staining techniques were deposited at the Museo Nacional de
Ciencias Naturales (Madrid, Spain) with accession number
MNCN 39.04/1.
The specimens were also stained with Flutax-2, a fluorescent
derivative of taxol that binds specifically to microtubules (pro-
vided by J.M. Andreu of the Centro de Investigaciones Biolo´gicas,
Consejo Superior de Investigaciones Cientı´ficas, Madrid) as de-
scribed in Arregui et al. (2003) in order to acquire complementary
data to those obtained with the silver impregnations since optimal
silver impregnation images were difficult to obtain due to the
presence of a lorica. Samples were observed under a Zeiss Axio-
plan 2 epifluorescence microscope using 40X and 63X objectives.
Images were recorded with a CCD Spot Camera and then ana-
lyzed using the MetaMorph Imaging System software (Universal
Imaging Corporation).
Physical–chemical parameters were measured according to
standard methods (APHA 1989).
Corresponding Author: L. Arregui, Departamento de Microbiologı´a
III, Facultad de Biologı´a, C/Jose Antonio Novais 2, 28040 Madrid,
Spain—Telephone number: Æ 34 913 944 966; FAX number: Æ 34
913 944 964; email: arregui@bio.ucm.es
362
J. Eukaryot. Microbiol., 57(4), 2010 pp. 362–368
r 2010 The Author(s)
Journal compilation r 2010 by the International Society of Protistologists
DOI: 10.1111/j.1550-7408.2010.00484.x
Published by
the International
Society of
ProtistologistsEukaryotic Microbiology
The Journal of

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2018 - APLICACIÓN DE HERRAMIENTAS DE SIMULACIÓN PARA CONTROL Y SUPERVISIÓN EN...
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2014 - Estudio de las relaciones del morfotipo Nosotocoida limicola con los p...
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2012 - Microscopía convencional versus FISH en la identificación, abundancia ...
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2013 - Estudio de las relaciones de Gordonia con parámetros operacionales y f...
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2011 - Estudio de la población de bacterias nitrificantes y su relación con l...
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2010 - A new species of genus Metacystis from a Wastewater Treatment Plant

  • 1. A New Species of the Genus Metacystis (Ciliophora, Prostomatida, Metacystidae) from a Wastewater Treatment Plant LUCI´A ARREGUI,a BLANCA PE´ REZ-UZ,a ANDRE´ S ZORNOZAb and SUSANA SERRANOa a Departamento de Microbiologı´a III, Facultad de Biologı´a, Universidad Complutense, 28040 Madrid, Spain, and b Grupo Aguas de Valencia, EDAR Quart-Benager, EPSAR, Valencia, Spain ABSTRACT. Unusual prostomatid specimens were found in the biological reactor of a wastewater treatment plant in a health resort in Valencia, Spain. These ciliates were attached to flocs unlike other free-swimming prostomatid ciliates described to date in the mixed liquor of activated sludge plants. The morphological study of this species led to a typically different combination of characteristics: elongated cell shape, 20–30 somatic kineties, 2 perioral kineties, and 1 circumoral kinety, 1 large vacuole protruding at the terminal end, a lorica tapered toward the aperture with a smooth neck, and 11–16 annular ridges. These characteristics place this representative as a new species of the genus Metacystis—Metacystis galiani n. sp. This species became the dominant population within the biological reactor when high values of conductivity (4,244 mS/cm) and temperature (26.8 1C) were recorded. Key Words. Activated sludge, high conductivity habitat, protist. BIOLOGICAL reactors of sewage treatment plants receive in- puts with different physical–chemical characteristics that de- termine variable biocenosis structures. The main components of this ecosystem are bacteria that reach 90–95% of the biomass, while protists and other microorganisms represent just 5–10% of the total biomass (Bitton 2005). The established community is organized as bioaggregates or flocs in which the biotic component is embedded in a complex matrix composed of organic and inor- ganic particles (contained in the sewage) and extracellular poly- meric substances produced by the microbial activity (Barker and Stuckey 1999; Laspidou and Rittmann 2002). Ciliates, often one of the most significant groups of protists within this ecosystem, have been divided into two categories de- pending on their ecological niche inside the reactor (Madoni 1988; Martı´n-Cereceda, Serrano, and Guinea 1996, 2001; Poole 1984): (i) associated with flocs are two functional groups—crawl- ing ciliates with flattened bodies and a specialized ventral ciliature allowing the movement on the floc surface and sessile ciliates at- tached to the floc through stalks or adhesive structures; and (ii) free-swimming ciliates moving freely in the mixed liquor. The first category of ciliates is generally more abundant (Curds and Cockburn 1970; Madoni 1988; Martı´n-Cereceda, Serrano, and Guinea 1996). Species of prostomatid ciliates are scarce in conventional ac- tivated sludge wastewater treatment plants (WWTP), never reach- ing higher numbers or reported as the dominant population under stable reactor conditions (Curds 1969; Esteban, Te´llez, and Ba- utista 1991; Madoni 1988; Martı´n-Cereceda, Serrano, and Guinea 1996). Exceptionally the prostomatid swimming ciliate Coleps hirtus has been described in biological reactors showing high effi- ciency in nitrification processes (Bick 1972; Madoni, Davoli, and Chierici 1993; Poole 1984). However, our group showed recently that several prostomatid species could be stable components in the biological communities of activated sludge plants with advanced nitrogen removal systems (Pe´rez-Uz et al. 2009). The aim of this work was to characterize a sessile prostomatid ciliate found as a stable population associated with flocs in the biological reactor of a WWTP from a health resort with a very specific set of physical–chemical conditions. We conclude that this is a new species Metacystis galiani n. sp. MATERIALS AND METHODS Sessile ciliates were sampled from the biological reactor of a WWTP of a health resort located in Cofrentes, Valencia, Spain (391130 N, 11040 W). Samples were collected in plastic bottles and taken to the laboratory for analysis. Fifty-microliter aliquots con- taining living cells were observed with a phase contrast micro- scope using either an Olympus BH-5 (Olympus Optical Espan˜a S. A., Madrid, Spain) or a Zeiss Axiostar microscope (VWR In- ternational Eurolab S. L., Barcelona, Spain). Digital images were taken with a digital camera (Olympus Camedia C-5050 or a Dig- ital Still Camera Sony DKC-CM30) attached to the microscope. Linear measurements were obtained from the digital images with Adobe Photoshop 6.0 after calibration with a 1-mm Zeiss stage micrometer. Ciliates were stained using the pyridinated silver carbonate method of Ferna´ndez-Galiano (1976, 1994) and the protargol im- pregnation modification of Wilbert (1975). Permanent slides of both staining techniques were deposited at the Museo Nacional de Ciencias Naturales (Madrid, Spain) with accession number MNCN 39.04/1. The specimens were also stained with Flutax-2, a fluorescent derivative of taxol that binds specifically to microtubules (pro- vided by J.M. Andreu of the Centro de Investigaciones Biolo´gicas, Consejo Superior de Investigaciones Cientı´ficas, Madrid) as de- scribed in Arregui et al. (2003) in order to acquire complementary data to those obtained with the silver impregnations since optimal silver impregnation images were difficult to obtain due to the presence of a lorica. Samples were observed under a Zeiss Axio- plan 2 epifluorescence microscope using 40X and 63X objectives. Images were recorded with a CCD Spot Camera and then ana- lyzed using the MetaMorph Imaging System software (Universal Imaging Corporation). Physical–chemical parameters were measured according to standard methods (APHA 1989). Corresponding Author: L. Arregui, Departamento de Microbiologı´a III, Facultad de Biologı´a, C/Jose Antonio Novais 2, 28040 Madrid, Spain—Telephone number: Æ 34 913 944 966; FAX number: Æ 34 913 944 964; email: arregui@bio.ucm.es 362 J. Eukaryot. Microbiol., 57(4), 2010 pp. 362–368 r 2010 The Author(s) Journal compilation r 2010 by the International Society of Protistologists DOI: 10.1111/j.1550-7408.2010.00484.x Published by the International Society of ProtistologistsEukaryotic Microbiology The Journal of