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An evaluation of methods to study the gut bacterial community composition of freshwater zooplankton HANNES PETER AND RUBEN SOMMARUGA* LABORATORY OF AQUATIC PHOTOBIOLOGY AND PLANKTON ECOLOGY , INSTITUTE OF ECOLOGY , UNIVERSITY OF INNSBRUCK, TECHNIKERSTR. 25, 6020 INNSBRUCK, AUSTRIA PRESENT ADDRESS: EVOLUTIONARY BIOLOGY CENTRE, DEPARTMENT OF LIMNOLOGY , UNIVERSITY OF UPPSALA, BOX 573, SE-75123 UPPSALA, SWEDEN *CORRESPONDING AUTHOR: [email protected] Received April 8, 2008; accepted in principle May 21, 2008; accepted for publication May 26, 2008; published online May 27, 2008 Corresponding editor: John Dolan The occurrence of gut bacteria in freshwater and marine zooplankton has long been recognized, but knowledge about the composition of the gut “microflora” and its permanent presence in different zooplankters is still inadequate. In this study, we tested the suitability of fluorescence in situ hybridization (FISH), catalysed reporter deposition (CARD)-FISH, cultivation and transmission electron microscopy (TEM) on homogenates and whole-specimen sections to assess the presence and identity of gut bacteria in several freshwater copepod and cladoceran species. Unambiguous results about the presence of a permanent gut “microflora” were obtained for freshly caught Daphnia pulex by TEM. CARD-FISH on gut homogenates from Acanthodiaptomus denticornis and D. pulex revealed a very similar bacterial composition to that present in the water column. Major bacterial groups found in cladocerans and copepods were alpha-, beta-, gamma- Proteobacteria and Cytophaga –Flavobacteria. The high contribution of alpha-Proteobacteria in A. denticornis suggested a specific niche for this group, but probably in association with its cara- pace. FISH on paraffin semithin sections had the potential to provide quantitative and qualitative information about the composition of the gut “microflora”, but loss of bacteria and gut content was significant. INTRODUCTION The existence of gut bacteria in zooplankton has long been recognized as shown by numerous marine and freshwater studies (Sochard et al., 1979; Gowing and Silver, 1983; Musko ´, 1988; Nagasawa, 1988; Nagasawa and Nemoto, 1988; Plante et al., 1989; Gu ¨nzl, 1991; Gowing and Wishner, 1992). However, knowledge about the presence, composition and role of gut “micro- flora” in freshwater zooplankton is still inadequate, mainly because of methodological constrains. Interactions between microorganisms and zooplank- ton are manifold. For example, bacteria are known to be a food source for freshwater and marine zooplank- ters (Carman and Thistle, 1985; Gowing and Wishner, 1992; Vrede and Vrede, 2005), to provide nutrients like essential amino acids and vitamins (Fong and Mann, 1980) and to enhance the host digestive abilities by con- tributing enzymes (Sochard et al., 1979). Schoenberg et al. (Schoenberg et al., 1984), however, reported cellu- lose digestion in three cladoceran species in the absence of gut bacteria, but only a few cases where crustacean guts were devoid of bacteria are known (Boyle and Mitchell, 1978; Schoenberg et al., 1984). Commensal (Kaneko and Colwell, 1975; Huq et al., 1983; Tamplin et al., 1990; Heidelberg et al., 2002) and parasitic bacteria (Rodriguez et al., 2008), as well as symbiotic phototrophs (Chang and Jenkins, 2000), have been documented. doi:10.1093/plankt/fbn061, available online at www.plankt.oxfordjournals.org # The Author 2008. Published by Oxford University Press. All rights reserved. For permissions, please email: [email protected] JOURNAL OF PLANKTON RESEARCH j VOLUME 30 j NUMBER 9 j PAGES 997 1006 j 2008

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Page 1: An evaluation of methods to study the gut bacterial ... · An evaluation of methods to study the gut bacterial community composition of freshwater zooplankton HANNES PETER† AND

An evaluation of methods to study thegut bacterial community compositionof freshwater zooplankton

HANNES PETER† AND RUBEN SOMMARUGA*

LABORATORY OF AQUATIC PHOTOBIOLOGY AND PLANKTON ECOLOGY, INSTITUTE OF ECOLOGY, UNIVERSITY OF INNSBRUCK, TECHNIKERSTR. 25, 6020INNSBRUCK, AUSTRIA

†PRESENT ADDRESS: EVOLUTIONARY BIOLOGY CENTRE, DEPARTMENT OF LIMNOLOGY, UNIVERSITY OF UPPSALA, BOX 573, SE-75123 UPPSALA, SWEDEN

*CORRESPONDING AUTHOR: [email protected]

Received April 8, 2008; accepted in principle May 21, 2008; accepted for publication May 26, 2008; published online May 27, 2008

Corresponding editor: John Dolan

The occurrence of gut bacteria in freshwater and marine zooplankton has long been recognized, but

knowledge about the composition of the gut “microflora” and its permanent presence in different

zooplankters is still inadequate. In this study, we tested the suitability of fluorescence in situ

hybridization (FISH), catalysed reporter deposition (CARD)-FISH, cultivation and transmission

electron microscopy (TEM) on homogenates and whole-specimen sections to assess the presence

and identity of gut bacteria in several freshwater copepod and cladoceran species. Unambiguous

results about the presence of a permanent gut “microflora” were obtained for freshly caught

Daphnia pulex by TEM. CARD-FISH on gut homogenates from Acanthodiaptomus denticornis

and D. pulex revealed a very similar bacterial composition to that present in the water column.

Major bacterial groups found in cladocerans and copepods were alpha-, beta-, gamma-

Proteobacteria and Cytophaga–Flavobacteria. The high contribution of alpha-Proteobacteria in

A. denticornis suggested a specific niche for this group, but probably in association with its cara-

pace. FISH on paraffin semithin sections had the potential to provide quantitative and qualitative

information about the composition of the gut “microflora”, but loss of bacteria and gut content

was significant.

I N T RO D U C T I O N

The existence of gut bacteria in zooplankton has longbeen recognized as shown by numerous marine andfreshwater studies (Sochard et al., 1979; Gowing andSilver, 1983; Musko, 1988; Nagasawa, 1988; Nagasawaand Nemoto, 1988; Plante et al., 1989; Gunzl, 1991;Gowing and Wishner, 1992). However, knowledgeabout the presence, composition and role of gut “micro-flora” in freshwater zooplankton is still inadequate,mainly because of methodological constrains.Interactions between microorganisms and zooplank-

ton are manifold. For example, bacteria are known tobe a food source for freshwater and marine zooplank-ters (Carman and Thistle, 1985; Gowing and Wishner,

1992; Vrede and Vrede, 2005), to provide nutrients likeessential amino acids and vitamins (Fong and Mann,1980) and to enhance the host digestive abilities by con-tributing enzymes (Sochard et al., 1979). Schoenberget al. (Schoenberg et al., 1984), however, reported cellu-lose digestion in three cladoceran species in the absenceof gut bacteria, but only a few cases where crustaceanguts were devoid of bacteria are known (Boyle andMitchell, 1978; Schoenberg et al., 1984). Commensal(Kaneko and Colwell, 1975; Huq et al., 1983; Tamplinet al., 1990; Heidelberg et al., 2002) and parasiticbacteria (Rodriguez et al., 2008), as well as symbioticphototrophs (Chang and Jenkins, 2000), have beendocumented.

doi:10.1093/plankt/fbn061, available online at www.plankt.oxfordjournals.org

# The Author 2008. Published by Oxford University Press. All rights reserved. For permissions, please email: [email protected]

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Zooplankton are known to regulate bacterial abun-dance and productivity, either by direct feeding or viacascading effects of feeding on bacterial predators(Zollner et al., 2003; Grosshart et al., 2008). In the sea,copepods are regarded as hotspots for bacterial growth,as they concentrate organic matter in their guts andfaecal pellets (Tang, 2005) and provide attachment sitesfor bacterial colonization (Møller et al., 2007). Severalstudies report massive colonization of faecal pellets andof the body surface of crustacean zooplankton species,especially around the oral region (Huq et al., 1983;Nagasawa, 1988). There is also evidence that the gutbacterial composition is different from that of the exter-nal milieu suggesting either a stable gut “microflora” orselective ingestion/digestion by the host (Hansen andBech, 1996).Regarding the fate of bacteria inside the gut, it seems

that no general pattern is found. Thus, increase (Planteet al., 1989) and decrease (Hymel and Plante, 2000) inbacterial abundance during gut passage have beendocumented, as well as bacterial survival (Hansen andBech, 1996). Nevertheless, in many studies, it is unclearwhether the “microflora” was resident, i.e. permanentlyinhabits the gut or transient, i.e. bacteria were ingested,but defecated. Resident bacteria should possess capabili-ties to adhere to the gut wall to avoid expulsion fromthe gut (Harris, 1993).Most studies on gut “microflora” have been done

using culture-based techniques (Sochard et al., 1979;Delille and Razouls, 1994; Hansen and Bech, 1996).Yet, considering that culture media are generally veryselective and only a small percentage of bacteria can becultured, probably only a small number of gut bacterialtaxa have been recognized. For example, Hansen andBech (Hansen and Bech, 1996) calculated a ratio of0.05 comparing colony forming units with acridineorange direct counts for faecal pellet bacteria of amarine copepod.Although the gut “microflora” potentially plays a key

role in the ecological performance and the biogeochem-ical activity of their zooplankton hosts, little is knownabout the gut bacterial community composition. This isrelevant not only to the study of sources and distributionof bacteria in the aquatic environment, but also to otherresearch areas such as the transformation of organic com-pounds by gut bacteria. For example, mycosporine-likeamino acids, an important family of UV sunscreen com-pounds are thought to be transformed by gut bacteria insea urchins (Dunlap and Shick, 1998), but no informationis available for freshwater organisms. Furthermore, zoo-plankton are often found to be depleted in d13C com-pared with potential food sources such as phytoplankton orparticular organic matter (del Giorgio and France, 1996).

Bastviken et al. (Bastviken et al., 2003) hypothesized thatconsumption of methanotrophic bacteria, especially byzooplankton in profundal and metalimnic waters,accounts for the differences in the d13C signatures, butthe role of gut bacteria was not taken into account. Littleis also known about the chemical and physical conditionsinside the gut of different species. Potentially, gradients ofpH, nutrient concentration and oxygen could formniches for rare bacterial species with unknown functions.

Molecular approaches, such as fingerprinting methods(denaturating gradient gel electrophoresis, DGGE), term-inal restriction fragment length polymorphism (T-RFLP),cloning and sequencing of 16S rRNA, or more quantitat-ive ones such as fluorescence in situ hybridization (FISH),catalysed reporter deposition (CARD)-FISH and scan-ning electron microscopy-in situ Hybridization (SEM-ISH) (Kenzaka et al., 2005), may provide more detailedinformation about gut bacterial communities of zoo-plankton species. Metagenomic and proteomic analysis,as recently applied by Warnecke et al. (Warnecke et al.,2007) on hindgut microbial communities of termites,could reveal large sets of genes and functions. Whereassingle-cell identification techniques, such as FISH orSEM-ISH, allow for the detection of bacterial cells in situ,PCR-based techniques are more prone to confoundingthe intestinal bacterial composition with that of externallycolonizing bacteria.

In this study, we tested the suitability of differentmethods including FISH and CARD-FISH on gut homo-genates and semithin sections of paraffin-embedded speci-mens, cultivation and transmission electron microscopy(TEM) to establish the existence of a gut “microflora” inseveral freshwater copepod and cladoceran species. Ouraim was to assess the strengths and weaknesses of differenttechniques and to make a preliminary exploration of thegut bacterial composition of freshwater zooplankton.

M E T H O D S

Test organisms

The calanoid copepod Acanthodiaptomus denticornis andthe cladoceran Daphnia longispina were collected fromPiburger See (Austria, 4781100N, 1085300E, 913 m abovesea level) by vertical net tows above the deepest pointusing a 55 mm plankton net in autumn 2005 and 2006.In autumn 2006, D. longispina was not found in the lake.The cyclopoid copepod Cyclops abyssorum tatricus wascollected in a similar way from the alpine lakeGossenkollesee, located at 2417 m above sea level in theCentral Alps (478130N, 118000E). Daphnia pulex andD. rosea were sampled from an artificial, shallow pond

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located at the Innsbruck University campus (4781500N,1182000E) by horizontal net tows with a 55 mm planktonnet.

Fixation and dissection

All organisms were either immediately killed [1:199.9% ethanol or 1:3 4% paraformaldehyde (PFA) for3 h and than in 1:1 ethanol] and stored at 2208C ormaintained alive in 1 L bottles filled with unfiltered lakewater. PFA was prepared following the protocol ofAmann et al. (Amann et al., 1995). In the laboratory,CO2-narcotized specimens were identified under thestereomicroscope, washed three times in Milli-Q waterand the gut dissected for cultivation of bacteria.Dissection of the whole gut was not possible for thecopepods, because of the compact anatomy of theseanimals. Hence, the head, tail and legs were removed,and the thorax with the gut inside was used. The fixedspecimens were kept at 2208C until further processing.Acanthodiaptomus denticornis and D. pulex were alsoanalysed by TEM analysis in samples fixed with 2.5%glutaraldehyde (microscopy grade). See Table I for anoverview of which method was applied to each species.

Paraffin sections

All copepod and cladoceran species were embedded inparaffin and cut in semithin sections (5–10 mm) forfurther FISH analysis. The animals were concentratedimmediately after sampling using a 100 mm mesh netand fixed with 4% PFA (1:3) for 3 h and stored in99.9% ethanol (EtOH) at 2208C overnight. Thefollowing day �20 specimens of each species were

washed three times in PBS 1�, dehydrated in anincreasing series of EtOH concentrations. The wholespecimens were then transferred to methyl benzoateand left there overnight. Fresh methyl benzoate wasadded the following 2 days. Afterwards, methyl benzo-ate was removed and benzene (100%) was added twotimes for 30 min. The specimens were then incubatedin 1:1 benzene and paraffin for 3 h followed by a seriesof hot paraffin (3 � 6 h). Subsequently, they were placedin metal dishes and cooled quickly on a freezing plate.A microtome (2040, Reichert-Jung) with a 80 mm knife[Shandon MB 35 Premier (358, 80 mm)] was used toprepare sections of 5–10 mm thickness. Each of thesections was straightened using a drop of Ruyter-solution on an adhesive, electrostatically charged micro-scope slide (SuperFrost, Carl Roth). The sections wereannealed to the microscope slide at 708C for 2 h.Subsequently, the paraffin was removed in a series ofxylene and finally dehydrated in a series of ethanol.Haematoxylin–eosin stains were used to obtain a quickoverview and to control the quality of the preparations.

FISH on paraffin sections

FISH (Amann et al., 1995) was applied on the semithinsections. The hybridization buffer was pipetted onto thesections and 1 mL of Cy3-labelled eubacterial probeEUB338 was added.

To reduce the background autofluorescence, we usedEvans blue and methylene blue according to Mosimanet al. (Mosiman et al., 1997) with some modifications. Inour experiments, the sections were incubated for 5 minin the dyes and air-dried before mounting in aCitifluor–Vectashield mixture. Thimm and Tebbe

Table I: Summary of results obtained with the different methods for the five zooplankters studied

Study organism Method Presence of bacteria Bacterial community composition

Daphnia pulex CARD-FISH on gut homogenates þ Cytophaga–Flavobacteria, alpha-,beta-, gamma-Proteobacteria

FISH on paraffin sections Not detectable N/ATEM unstarved þ N/ATEM starved þ N/ACulture þ Cytophaga–Flavobacteria, beta-,

gamma-ProteobacteriaDaphnia longispina Culture þ Beta-ProteobacteriaDaphnia rosea culture þ Cytophaga–FlavobacteriaAcanthodiaptomus

denticornisCARD-FISH on gut homogenates þ Alpha-, beta-,

gamma-Proteobacteria,Cytophaga–Flavobacteria

FISH on paraffin sections Not detectable N/ATEM unstarved 2 N/ATEM starved 2 N/ACulture þ Alpha-Proteobacteria

Cyclops abyssorumtatricus

Culture þ Cytophaga–Flavobacteria, beta-,gamma-Proteobacteria

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(Thimm and Tebbe, 2003), working on cryosections ofmicroarthropods, overcame the problem of autofluores-cence with a triple-band-pass filter (Filter Set 25, Zeiss)with excitation wavelengths of 400, 495 and 570 nmand emission wavelengths of 460, 530 and 610 nm,respectively. We also tested this Filter Set with anAxioImager Z1 (Zeiss) epifluorescence microscope.

Transmission electron microscopy

Freshly caught and starved (3 days in 0.2 mm sterilefiltered lake water) specimens of D. pulex and A. denticor-nis were prepared for TEM. Organisms were fixed over-night in 2.5% glutaraldehyde in 0.1 M potassiumphosphate buffer, washed in PBS 1� to remove thefixative, and post-fixed in 1% OsO4 in cacodylate bufferfor 2 h. The samples were washed several times in PBS1� and dehydrated either in a series of EtOH oracetone. Subsequently, the specimens were placed inSpurr-resin (Spurr, 1969) and EtOH (1:1) overnight andthen in Spurr only at 608C for 4 days. Semithin(0.5 mm) and ultrathin sections (90 nm) were cut auto-matically with a microtome (Ultracut VCT, Leica).Shape of the organisms and cutting position were

controlled with methyl blue stain (5 min, on a heatingplate). Ultrathin sections were incubated with uranylacetate (8 min) and lead citrate (4 min), following theprotocol of Reynolds (Reynolds, 1963). The ultrathinsections were observed with a TEM (Libra 120, Zeiss)at 4000–20 000�. For length measurement and imageacquisition, the software iTEM (Olympus Soft ImagingSolutions) was used.

Bacterial cultivation

Bacteria were isolated from the gut of 10 freshly caughtand CO2-narcotized animals of each species. The indi-viduals were first washed three times in Milli-Q waterto reduce the abundance of adhering bacteria from thesurface (Huq et al., 1983) and subsequently, the gut wasdissected using a small scalpel (blade 4 mm length)and micromanipulation scissors (sterilized with 96%ethanol). As described above, the guts of copepods wereincluded with the thorax. The guts of 10 individualswere pooled in 1 mL of filtered (0.2 mm) Milli-Q waterand treated with a tip sonicator for 2 min at 30%power (Sonoplus UW 2070 Bandelin). Gut extractswere then plated onto an agar-rich nutrient medium(1 g L21 peptone, 0.5 g L21 yeast-extract and 15 g L21

agar) and onto modified WC agar-medium (Guillardand Lorenzen, 1972). The cultures were grown at 16+28C with a 16:8 h light:dark cycle in an environmentalgrowth chamber. After several cleaning cycles, pure

isolates were transferred into a liquid medium of thesame composition. To determine the bacterial groupaffiliation of the isolates, CARD-FISH was applied. Forthis purpose, the culture was fixed with PFA and filteredonto white polycarbonate filters (0.22 mm, Millipore)using a 0.45 mm support filter (Type HA, Millipore).Filters were air-dried and stored at 2208C until proces-sing within 1 month.

Comparison of D. pulex and A. denticornisgut homogenates

For this objective, animals were also fixed with both99.9% EtOH (1:1) and 4% PFA (1:3). Guts were dis-sected and 10 guts were pooled in 1.5 mL Milli-Q waterand sonicated. The gut homogenates were immediatelyfiltered onto white polycarbonate filters (0.2 mm,Millipore) and stored at 2208C for CARD-FISH (dis-cussed later). Additionally, water samples (pre-screened,100 mm and fixed with PFA) collected from PiburgerSee (0, 1, 2, 3 and 4 m depth) and the pond (0, 0.5, 1,1.5 and 2 m depth) were analysed to compare with thegut bacterial composition.

CARD-FISH of bacterial isolates and guthomogenates

To determine the gut bacterial community composition,we used the protocol of Pernthaler et al. (Pernthaler et al.,2002) for the detection of bacteria using FISH followed byCARD-FISH. The permeabilization step was modifiedafter Sekar et al. (Sekar et al., 2003) to be able to betterdetect Actinobacteria. CARD-FISH was applied tothe isolates and the gut homogenates of D. pulex andA. denticornis using horseradish peroxidase (HRP)-labelledprobes EUB I–III (Eubacteria), ALF968 (alpha-Proteobacteria), BET42a (beta-Proteobacteria, togetherwith an unlabelled competitor probe), GAM42a (gamma-Proteobacteria, together with an unlabelled competitorprobe), CF319a (Cytophaga–Flavobacteria), HGC69a(Actinobacteria) and LGC0355 (Firmicutes). Furtherdetails on oligonucleotide probes are available atprobeBase (Loy et al., 2003). Alexa-488 labelled tyramidewas used for signal amplification.

Hybridized bacteria were observed with anAxioImager Z1 (Zeiss) or Axiophot (Zeiss) epifluores-cence microscope. At least 400 bacterial cells per probeand filter section were counted for the dissected gutsand the water samples from the pond and Piburger See.To differentiate between the Alexa-488 signal and theautofluorescence background originating from chitinousparts of the animals, the excitation wavelength waschanged while counting. The CARD-FISH signal was

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detectable only under 450–490 nm excitation, but auto-fluorescence was also observed with other excitationwavelengths available (365 and 546 nm).

R E S U LT S

Paraffin sections and FISH

To obtain an overview of the sections, haematoxylin–eosin stains were observed using bright field microscopy.The gut could easily be identified in cross- and longi-tudinal sections. However, since embedding in paraffinresulted in a random position of the animals, the sectionsincluded different parts of the gut. Cladocerans, which arelaterally flattened, were often cut in a longitudinal way.Sections examined by epifluorescence microscopy

exhibited autofluorescence for all tested excitation wave-lengths. As the animals consist largely of fluorescentchitin, differences between the FISH signal, especially thatfrom the gut wall attached cells, and autofluorescencewere not obvious (Fig. 1). When Evans blue and methyl-ene blue were added to reduce autofluorescence, bindingof the dyes to the sections was observed using bright fieldmicroscopy. Despite reduced autofluorescence, the signal-background ratio still did not allow for an unambiguousidentification of hybridized bacterial cells.Using the filter set 25 (Zeiss), the tissue and hybridi-

zation signals appeared in different colours, but in fewcases, bacteria were distinguishable (Fig. 1C; for a colourfigure at high resolution see the online Supplementarydata). In most cases, however, the gut content was lostduring the last step of the protocol, when the paraffin wasremoved from the sections using a series of xylene concen-trations. Although electrostatically charged microscopicslides were used to improve adhesion of the sections to the

slides, major parts of the gut content and bacteria werelost. Only in rare cases (,10%), remaining gut contentand bacteria could be observed (Fig. 2).

Elimination of the xylene treatment revealed DAPIsignals in the gut of D. pulex, but optical resolution athigher magnification was too poor because of blurringby the remaining paraffin (data not shown). Single bac-terial cells could therefore not be identified and countedusing this approach (Table I).

Transmission electron microscopy

Cross-sections of the gut of D. pulex immediately fixedafter sampling showed that large proportions of the gutwere filled with bacteria (Table I, Fig. 3). In contrast,cross-sections of starved specimens of D. pulex showedfewer bacteria in the gut lumen, but still some wereobserved near the microvilli (Table I, Fig. 4). Althoughobservation at high magnification showed some appen-dages, it was unclear whether bacteria were attached tothe gut lining or not. At 20 000� magnification, differ-ent bacteria morphotypes were present with some kindof appendages (Fig. 5).

In freshly caught specimens of A. denticornis, no bac-teria were detected inside the gut lumen or attached tothe gut wall. The same was observed in the starvedanimal (Table I, Fig. 6).

CARD-FISH of isolates

A total of 28 isolates were obtained from all copepodsand cladocerans analysed. Two isolates obtained fromA. denticornis did not grow in the liquid medium. Thus,12 isolates from copepods (A. denticornis and C. abyssorumtatricus) and 14 from cladocerans (D. pulex, D. longispinaand D. rosea) were analysed by CARD-FISH.

Fig. 1. Semithin sections (5 mm) of D. pulex (A) and A. denticornis (B) showing autofluorescence of chitinous parts when observed with excitationwavelengths between 450 and 495 nm (Filter Set 38 HE). (C) A semithin section (5 mm) of D. pulex, hybridized with probe EUB I-III andobserved with Filter Set 25. Several single pictures were taken for one overview picture (MosaiX, Zeiss, Germany). See the onlinesupplementary material for a high resolution photograph showing the chitinous parts in blue, gut content in orange and the EUB I–IIIhybridized bacterial cells in bright-red.

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Bacterial isolates from copepods corresponded toalpha-, beta- and gamma-Proteobacteria and Cytophaga–Flavobacteria. Alpha-Proteobacteria were the mostcommon group (33%) among the isolates derived fromcopepods, whereas the most frequent bacterial groups iso-lated from cladocerans were beta-Proteobacteria andCytophaga–Flavobacteria (31%). Isolates belonging toalpha-Proteobacteria represented only 7.7% in cladocer-ans, whereas Firmicutes were exclusively found in culturesderived from cladocerans.

CARD-FISH of gut homogenates fromD. pulex and A. denticornis

The detection efficiency by CARD-FISH with group-specific probes (Table II) was relatively low (27.5–68.1%).

Nevertheless, the comparison of the bacterial compositionbetween the gut of these two zooplankters and the bacter-ioplankton of the respective habitats by CARD-FISHrevealed a very similar composition. The contribution ofalpha-Proteobacteria in the gut homogenate from A. denti-cornis was greater than that in the water column ofPiburger See (Table II).

All bacterial groups found in the guts of copepodsand cladocerans also occurred in the water columnexcept for Actinobacteria (HGC69a) that were detectedin Piburger See, but not in the gut homogenates fromA. denticornis (Table II). The most frequent bacterialgroups were regularly distributed in the water columnof both freshwater systems (data not shown).

Large differences were observed for some bacterialgroups in homogenates of D. pulex fixed with 99.9%EtOH and 4% PFA; however, they were not significant(t-test, P ¼ 0.90). The same was true for A. denticornis

(t-test, P ¼ 0.61). For example, in PFA-fixed specimens ofA. denticornis, there were in total more than twice as manybacteria detected with specific probes compared withEtOH-fixed specimens. In contrast, in D. pulex, the differ-ences in total hybridized cells with specific probes weresmaller; however, alpha-Proteobacteria (ALF968) weremainly detected in the EtOH-fixed samples (Table II).

D I S C U S S I O N

To distinguish between resident and transient bacteria inthe gut of freshwater zooplankton, a set of differentmethods was used in the present study. However, onlyTEM allowed for a clear detection of epimural bacteria.Comparison of gut bacteria and free-living bacteria usingCARD-FISH would allow separation between resident

Fig. 2. Hybridized bacteria with the probe EUB I–III (arrows)associated with the gut contents (C) of D. pulex. W, gut wall.

Fig. 3. TEM micrographs of a cross-section of the gut of a non-starved D. pulex observed at 4000� (A) and at 20 000� (B). A large proportionof the gut lumen is filled with bacteria. b, bacteria; W, gut wall; MV, microvilli. Different morphotypes of bacteria (arrows) could be observednear the microvilli and in the gap of the microvilli, where two neighbouring cells touch each other (frame). Amorphous material (a) also filledthe gut lumen.

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Fig. 6. TEM micrographs (4000� magnification) of a cross-section from the gut of a non-starved (A) and a starved (B) A. denticornis. In (A)bacteria are not visible in the gut lumen (GL) or near the microvilli (MV). Some remnants (arrows) of ingested food can be observed.

Fig. 5. TEM micrograph (20 000� magnification) showing severalbacteria (arrows) in a pouch of the gut of a starved specimen ofD. pulex, MV, microvilli; W, gut wall. Insets show different bacterialmorphotypes possibly adhered to the microvilli (MV).

Fig. 4. TEM micrograph (20 000� magnification) of the gut ofD. pulex after 3 days of starvation showing bacteria. MV, microvilli;W, gut wall.

Table II: CARD-FISH results for gut homogenates of A. denticornis and D. pulex fixed with PFA andethanol (EtOH) and for water collected from their respective habitats (i.e. Piburger See and pond) fixedwith PFA

ALF968 BET42a GAM42a HGC69a LGC0355 CF319a Unknown

A. denticornis, PFA 27.2 6.9 4.0 0.0 28.3 1.7 31.9A. denticornis, EtOH 20.8 1.2 0 0.0 10.4 1.2 66.4Piburger See, PFA 13.2 5.5 2.0 1.0 9.5 10.3 58.5D. pulex, PFA 0.2 12.3 0.5 0.0 N/A 15.1 71.9D. pulex, EtOH 10.3 3.0 0.2 0.1 N/A 13.9 72.5Pond, PFA 0.5 2.7 0.7 0.0 N/A 23.8 72.3

Values are given as the percentage of cells targeted with the different bacterial group-specific probes (see Methods for explanations) to EUB I–IIItargeted cells. Values for Piburger See and the pond are the average for the different depths. N/A, not analysed.

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bacteria and those ingested with the food, only if the bac-terial composition of these two habitats significantlydiffers. However, this was not the case in this study.The culturing techniques used in this study are prone

to contamination by bacteria associated with the cara-pace. For example, Boyle and Mitchell (Boyle andMitchell, 1978) showed that the exoskeleton of twomarine and one terrestrial isopod, and one amphipodare heavily colonized by bacteria, whereas their gut wasbacteria-free. Moreover, it is known that culture mediaare very selective. This selectivity could explain thedifferences observed between CARD-FISH donedirectly on gut homogenates and isolates (Table I).FISH on paraffin sections has the potential to provide

not only quantitative (like TEM) but also qualitative infor-mation about the composition of the gut “microflora”. Itshould also be possible to distinguish between bacteriaattached to the gut wall (i.e. resident) and those that arefree (i.e. transient) by assessing whole-specimen sections.Although this approach failed to work in our assessment,it is promising because it could provide information aboutthe distribution of gut bacterial groups along the digestivetract. In our case, bacteria could only be found in a fewparaffin sections (Fig. 2). In most cases, the guts appearedbacteria-free, although stereo-microscopical observationsof the specimens before the embedding and sectioningsteps confirmed that the gut was filled with food particles.However, observations of the slides after the different stepsshowed no gut content. Paraffin sections of D. pulex

without xylene treatment and stained with DAPI revealedthat the gut content and bacteria were indeed removedtogether with the paraffin probably because they were notstrongly attached to the electrostatically charged slides.Other techniques (Bancroft, 1990) such as cryosections(Thimm and Tebbe, 2003) or synthetic resin embeddingcould probably overcome this problem and remain worthtesting.Observations of gut bacteria in marine zooplankton

using TEM have often been made (Musko, 1988;Gunzl, 1991; Gowing and Wishner, 1992; Wishner et al.,2000). Cross-sections of the gut of D. pulex immediatelyfixed after sampling showed that the gut was denselyfilled with bacteria (Fig. 3). This result is in agreementwith the observation that D. pulex feeds on natural bac-terial assemblages (Peterson et al., 1978). Bacteria wereobserved in the gut lumen and near the microvilli of thegut wall (Fig. 3), but it was not possible to differentiatebetween epimural and bacteria ingested as food.Daphnia pulex starved for 3 days in sterile lake water didnot have free bacteria in the gut lumen, but someremained near the gut wall (Fig. 4). Detailed TEMobservations at 20 000� magnification showed differentbacterial morphotypes with some kind of appendages

(Fig. 5). These bacteria were probably epimural whichin contrast to the bacteria taken up as food are part of astable gut “microflora”.

Harris (Harris, 1993) suggested that food plays animportant role in the establishment of gut “microfloras”in invertebrates. For example, Sochard et al. (Sochardet al., 1979) reported the occurrence of a stable gut“microflora” in the marine copepod Acartia tonsa evenwhen copepods were reared in the laboratory withsterile water and sterile algal food. However,Schoenberg et al. (Schoenberg et al., 1984) did not find a“microflora” in the gut of the cladocerans D. magna andAcantholeberis curvirostris fed sterile food. Bacteria-free gutsare also known for marine arthropods (Boyle andMitchell, 1978). This seems to be also the case in thecopepod A. denticornis. One possible reason for theabsence of bacteria is the existence of a peritrophicmembrane, a semi-permeable membrane that separatesthe gut lining from the ingested food in some arthro-pods and that is known to act as a barrier for bacteriacolonizing the gut (Harris, 1993). For instance, a peri-trophic membrane is known to be present in some cala-noid copepods (Gauld, 1957), but D. pulex also has sucha membrane (Schlecht, 1979).

In general, all bacterial groups tested, except forActinobacteria, were found in the isolates derived fromboth copepods and cladocerans, though there weredifferences among zooplankton species (Table I). SomeActinobacteria are known to require special culture con-ditions (Hahn et al., 2003) and probably did not growon the media used in our study. The fact that only onebacterial isolate was obtained from the copepod A. denti-cornis supports the observation that the gut of thisspecies was bacteria-free (Fig. 6) and points to bacteriaassociated with the thorax. All other isolates from cope-pods originated from C. abyssorum tatricus. However,Nagasawa et al. (Nagasawa et al., 1985) showed that thesurface of C. abyssorum tatricus is densely colonized bybacteria. Though the efficient removal of attached bac-teria to the exoskeleton is possible by extensivelywashing the organisms with sterile water (Huq et al.,1983), we cannot rule out the possibility of contami-nation, particularly for copepods where the gut but alsothe thorax were used to isolate bacteria. In contrast, iso-lates obtained from the gut of cladocerans did probablyderive from the bacteria in the gut lumen, which wereobserved in the TEM micrographs (Fig. 3).

CARD-FISH of the gut homogenates from A. denticor-nis and D. pulex revealed that bacterial composition wassimilar to that found in the water column (Table II). Wecannot eliminate the possibility that differences couldhave been found when more specific bacterial probesare used, however. All bacterial groups (except for

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Actinobacteria) found in the surrounding water werealso detected in the gut homogenates. However, thehigh percentage of alpha-Proteobacteria found ingut homogenates (Table II) but also in the isolates ofA. denticornis suggests a specific niche for them in thiscopepod, since this group is not very common infreshwater bacterioplankton (Glockner et al., 1999). Asdiscussed above, bacteria from this group were probablyassociated with the thorax of this copepod because gutbacteria were not found by TEM.One reason why Actinobacteria were detected by

CARD-FISH in the water from Piburger See, but notin the gut homogenate, could be the difficulty in differ-entiating them from other numerous auto-fluorescentparticles during counting. Although CARD-FISH yieldssignificantly higher signal intensities than FISH(Pernthaler et al., 2002), many particles with autofluores-cence (e.g. ingested food, remnants of the gut wall orthe thorax in the case of copepods) were included in thehomogenized guts. Differentiation of the CARD-FISHsignal and autofluorescence could only be done byswitching between different filter sets. Thus, we thinksmall cells, such as those of Actinobacteria fromPiburger See, were not easily visible among other fluor-escent particles. Alternatively, this bacterial group maynot be typically associated with zooplankton.

Perspectives

We suggest that the best approach to study the gut“microflora” in zooplankton is to combine FISH orCARD-FISH with semithin sections. However, itshould be tested whether bacterial FISH probes can beapplied with other embedding media than paraffin.Cryosectioning is also a promising approach, but theloss of bacteria during melting and subsequent washingsteps in the FISH protocol should be ruled out. Gutbacterial isolates are difficult to obtain without contami-nation, especially for small organisms such as zooplank-ton. Therefore, cultures should rather be used to assessgut bacterial properties than bacterial composition.Other molecular approaches, based on PCR, are alsoprone to contamination and insights in bacterial distri-bution (transient/resident) in the gut cannot beobtained. Electron microscopy (SEM or TEM) provideshigh-resolution micrographs of bacteria inside guts andloss of bacteria certainly does not occur. Differentiationbetween resident and transient gut bacteria, by obser-vation of adhesion to the gut wall, could be assessedwith SEM. Finally, Kenzaka et al. (Kenzaka et al., 2005)introduced SEM-ISH, a combination of in situ hybridiz-ation (ISH) and SEM. They used Cy3 and biotin-labelled oligonucleotide probes, which subsequently

leads to the deposition of Nanogold particles that canbe observed using SEM. Although it is a laborious andcostly approach, it could overcome the major problemsthat arise in the observation of gut bacteria in zooplank-ton species.

S U P P L E M E N TA RY DATA

Supplementary data can be found online at http://plankt.oxfordjournals.org.

AC K N OW L E D G E M E N T S

We thank W. Salvenmoser for expert help in preparingthe thin and ultrathin sections and TEM and P. Hirschfor valuable comments on the manuscript.

F U N D I N G

This study was supported by a grant from the AustrianScience Fund (FWF, P19245-B03) to R.S.

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