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Ciliate and bacterial communities associated with White Syndrome and Brown Band Disease in reef-building coralsMichael Sweet* and John Bythell School of Biology, Ridley Building, Newcastle University, Newcastle upon Tyne, NE1 7RU, UK. Summary White Syndrome (WS) and Brown Band Disease (BrB) are important causes of reef coral mortality for which causal agents have not been definitively identified. Here we use culture-independent molecular tech- niques (DGGE and clone libraries) to characterize ciliate and bacterial communities in these diseases. Bacterial (16S rRNA gene) and ciliate (18S rRNA gene) communities were highly similar between the two dis- eases. Four bacterial and nine ciliate ribotypes were observed in both diseases, but absent in non- diseased specimens. Only one of the bacteria, Arco- bacter sp. (JF831360) increased substantially in relative 16S rRNA gene abundance and was consis- tently represented in all diseased samples. Four of the eleven ciliate morphotypes detected contained coral algal symbionts, indicative of the ingestion of coral tissues. In both WS and BrB, there were two ciliate morphotypes consistently represented in all disease lesion samples. Morph1 (JN626268) was observed to burrow into and underneath the coral tissues at the lesion boundary. Morph2 (JN626269), previously identified in BrB, appears to play a sec- ondary, less invasive role in pathogenesis, but has a higher population density in BrB, giving rise to the visible brown band. The strong similarity in bacterial and ciliate community composition of these diseases suggests that they are actually the same syndrome. Introduction The emerging ‘damage-response’ framework of microbial pathogenesis (Casadevall and Pirofski, 2003) suggests that diseases in general arise from complex host– pathogen interactions. Lesser and colleagues (2007) argued that coral diseases in particular may result more commonly from environmentally induced changes in these host–pathogen interactions than the novel expo- sure of a host to a specific, virulent pathogen. Indeed, several proposed causal agents of coral disease, such as Vibrio coralliilyticus (Ben-Haim et al., 2003; Sussman et al., 2008), V. shiloi (Kushmaro et al., 2001) and V. har- veyi (Luna et al., 2010), have commonly been detected in apparently healthy corals (Bourne, 2005; Bourne and Munn, 2005; Ritchie, 2006; Cervino et al., 2008; Kvenne- fors et al., 2010; Mouchka et al., 2010), increasing in abundance during disease and/or stress. In fact, it has been argued that all infectious agents could be consid- ered ‘opportunistic’ and immunocompetent organisms may normally host many pathogens (defined as microor- ganisms capable of causing damage to the host; Casa- devall and Pirofski, 2003). It is therefore vital that, in addition to the identification of pathogens via tests of Koch’s postulates: (i) an analysis of the microbial commu- nity of healthy and diseased hosts is undertaken to com- prehensively identify potential pathogens involved in disease, and (ii) increases in activity of these suspected pathogens are linked to sites of active pathogenesis. These need to be studied in combination to fully under- stand disease causation. Specifically we must be able to distinguish between pathogens that are capable of causing damage, those that are directly involved in a specific pathogenesis and heterotrophs that colonize dead and decaying tissues following disease. Historically, most studies of coral diseases have been focused on pathogenic bacteria (Richardson et al., 1998; Kushmaro et al., 2001; Ben-Haim and Rosenberg, 2002; Patterson et al., 2002; Frias-Lopez et al., 2003; Cervino et al., 2008; Sussman et al., 2008; Luna et al., 2010). Only relatively recently have ciliates and other protozoans been shown to be associated with diseases of corals such as skeletal eroding band (SEB) (Antonius and Lipscomb, 2001) and Brown Band Disease (BrB) (Willis et al., 2004). BrB is widespread in parts of the GBR and known to affect at least three major coral families, including members of the Acroporidae, Pocilloporidae and Faviidae (Willis et al., 2004). A ciliate, identified as a member of the subclass Scuticociliatia (Bourne et al., 2008), has been shown to ingest intact symbiotic algae of the coral and is Received 12 September, 2011; revised 9 March, 2012; accepted 16 March, 2012. *For correspondence. E-mail michael.sweet@ ncl.ac.uk; Tel. (+44) 191 246 4824; Fax (+44) 191 222 5229. Environmental Microbiology (2012) doi:10.1111/j.1462-2920.2012.02746.x © 2012 Society for Applied Microbiology and Blackwell Publishing Ltd
Transcript

Ciliate and bacterial communities associated withWhite Syndrome and Brown Band Disease inreef-building coralsemi_2746 1..16

Michael Sweet* and John BythellSchool of Biology, Ridley Building, Newcastle University,Newcastle upon Tyne, NE1 7RU, UK.

Summary

White Syndrome (WS) and Brown Band Disease (BrB)are important causes of reef coral mortality for whichcausal agents have not been definitively identified.Here we use culture-independent molecular tech-niques (DGGE and clone libraries) to characterizeciliate and bacterial communities in these diseases.Bacterial (16S rRNA gene) and ciliate (18S rRNA gene)communities were highly similar between the two dis-eases. Four bacterial and nine ciliate ribotypes wereobserved in both diseases, but absent in non-diseased specimens. Only one of the bacteria, Arco-bacter sp. (JF831360) increased substantially inrelative 16S rRNA gene abundance and was consis-tently represented in all diseased samples. Four ofthe eleven ciliate morphotypes detected containedcoral algal symbionts, indicative of the ingestion ofcoral tissues. In both WS and BrB, there were twociliate morphotypes consistently represented in alldisease lesion samples. Morph1 (JN626268) wasobserved to burrow into and underneath the coraltissues at the lesion boundary. Morph2 (JN626269),previously identified in BrB, appears to play a sec-ondary, less invasive role in pathogenesis, but has ahigher population density in BrB, giving rise to thevisible brown band. The strong similarity in bacterialand ciliate community composition of these diseasessuggests that they are actually the same syndrome.

Introduction

The emerging ‘damage-response’ framework of microbialpathogenesis (Casadevall and Pirofski, 2003) suggeststhat diseases in general arise from complex host–pathogen interactions. Lesser and colleagues (2007)

argued that coral diseases in particular may result morecommonly from environmentally induced changes inthese host–pathogen interactions than the novel expo-sure of a host to a specific, virulent pathogen. Indeed,several proposed causal agents of coral disease, such asVibrio coralliilyticus (Ben-Haim et al., 2003; Sussmanet al., 2008), V. shiloi (Kushmaro et al., 2001) and V. har-veyi (Luna et al., 2010), have commonly been detected inapparently healthy corals (Bourne, 2005; Bourne andMunn, 2005; Ritchie, 2006; Cervino et al., 2008; Kvenne-fors et al., 2010; Mouchka et al., 2010), increasing inabundance during disease and/or stress. In fact, it hasbeen argued that all infectious agents could be consid-ered ‘opportunistic’ and immunocompetent organismsmay normally host many pathogens (defined as microor-ganisms capable of causing damage to the host; Casa-devall and Pirofski, 2003). It is therefore vital that, inaddition to the identification of pathogens via tests ofKoch’s postulates: (i) an analysis of the microbial commu-nity of healthy and diseased hosts is undertaken to com-prehensively identify potential pathogens involved indisease, and (ii) increases in activity of these suspectedpathogens are linked to sites of active pathogenesis.These need to be studied in combination to fully under-stand disease causation. Specifically we must be able todistinguish between pathogens that are capable ofcausing damage, those that are directly involved in aspecific pathogenesis and heterotrophs that colonizedead and decaying tissues following disease.

Historically, most studies of coral diseases have beenfocused on pathogenic bacteria (Richardson et al., 1998;Kushmaro et al., 2001; Ben-Haim and Rosenberg, 2002;Patterson et al., 2002; Frias-Lopez et al., 2003; Cervinoet al., 2008; Sussman et al., 2008; Luna et al., 2010).Only relatively recently have ciliates and other protozoansbeen shown to be associated with diseases of corals suchas skeletal eroding band (SEB) (Antonius and Lipscomb,2001) and Brown Band Disease (BrB) (Willis et al., 2004).BrB is widespread in parts of the GBR and known to affectat least three major coral families, including members ofthe Acroporidae, Pocilloporidae and Faviidae (Willis et al.,2004). A ciliate, identified as a member of the subclassScuticociliatia (Bourne et al., 2008), has been shownto ingest intact symbiotic algae of the coral and is

Received 12 September, 2011; revised 9 March, 2012; accepted16 March, 2012. *For correspondence. E-mail [email protected]; Tel. (+44) 191 246 4824; Fax (+44) 191 222 5229.

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Environmental Microbiology (2012) doi:10.1111/j.1462-2920.2012.02746.x

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd

responsible for the visible signs of this disease (a variablebrown band). In 2006, ciliates (Halofolliculina sp.) werealso reported affecting over 26 Caribbean reef-buildingcoral species (Croquer et al., 2006a). Although it is still tobe determined whether this Caribbean Ciliate Infection(CCI) is the same as SEB in the Indo-Pacific, their mor-phology, life cycle and patterns of infection are similar.Therefore, increasing evidence indicates that ciliatesact as pathogens in some coral diseases. Despite this,Koch’s postulates have not been fulfilled for any of theciliates associated with coral diseases. However, severalstudies have shown ciliates to be pathogenic in a widerange of other organisms (Song and Wang, 1993; Brad-bury, 1996), including members of the Scuticociliatiaaffecting marine mammals such as dolphins and whales(Sniezek et al., 1995; Poynton et al., 2001; Song et al.,2009) and members of the Peritrichida affecting bivalvessuch as the clam Mesodesma mactroides (Cremonte andFigueras, 2004).

Some of the most ecologically important coral diseasesworldwide are the poorly defined ‘white diseases/syndromes’, few of which have been satisfactorily char-acterized (Bythell et al., 2004). These diseases arecollectively termed White Syndrome (WS) in the Indo-Pacific and include White Plague (WP) and White BandDisease (WBD) in the Caribbean. Many studies haveidentified bacterial pathogens involved in these white dis-eases (Peters et al., 1983; Barash et al., 2005; Thompsonet al., 2006; Sussman et al., 2008; Efrony et al., 2009).For example, Aurantimonas coralicida has been reportedto cause WP type II disease (Denner et al., 2003) andanother a-proteobacterium, thought to be the causativeagent of juvenile oyster disease (JOD), has been associ-ated with a WP-like disease (Pantos et al., 2003). Severalvibrio species have been proposed as causal agents ofWS (Sussman et al., 2008), with V. harveyi being the mostrecently identified (Luna et al., 2010). However, recently,Work and Aeby (2011) have reported that ciliates arealso associated with the WS pathology. Together withAinsworth and colleagues (2007) they also show no bac-terial populations associated with the pathogenesis andno signs of bacterial-induced necrosis. These recentstudies therefore question the primary role of bacteriain WS.

As a first step towards understanding disease causa-tion in WS (Fig. 1A) this study provides a comprehensive,culture-independent molecular analysis of both ciliate andbacterial communities associated with the disease. As acomparison with a known ciliate-associated syndrome,we also sampled corals displaying characteristic signs ofBrB (Fig. 1B). Since WS is a collective term that mayencompass both active and recovering lesions (Work andAeby, 2011), and is easily confused with non-infectiouscauses such as predation, we monitored disease lesion

progression in the field and selected only cases thatshowed actively progressing disease lesions, referred tohere as ‘Progressive White Syndrome (PWS)’ to distin-guish it from these other WS states.

Results

Bacterial 16S rRNA gene diversity

Significant differences in denaturing gradient gel electro-phoresis (DGGE) banding patterns of bacterial 16S rRNAgene diversity were shown between non-diseased colo-nies (ND; n = 10), the apparently healthy tissues adjacentto the disease lesion (AH; n = 10) and the disease lesion(DL; n = 10) in Acropora muricata from Heron Island, GBR[one-way analysis of similarity (ANOSIM), R = 0.937,P < 0.001]. There was no significant difference in bacterial16S rRNA DGGE profiles between corals with PWS andthose with BrB (ANOSIM, pairwise comparison, P = 0.64)of the same species from the same location; n = 10and 12 respectively. Only four bacterial ribotypes weredetected in diseased or apparently healthy tissue (tissuenear the disease lesion) yet absent in non-diseasedsamples, including ribotypes related to Clostridium sp.(GenBank Accession No. JN406280), Aeromonas sp.(JN406279), Cyanobacterium sp. (JN406285) and Arco-bacter sp. (JF831360). All four of these sequences weredominant representatives of both DGGE profiles (Fig. 2A)and clone libraries (Table 1), which were based onindependent primer sets targeting different subregionsof the 16S rRNA gene. One of these, Arcobacter sp.(JF831360), was absent in non-diseased tissues,appeared in apparently healthy tissues and increasedsubstantially in relative 16S rRNA gene abundance in thedisease lesion (Table 1). This species was also consis-tently represented in all replicate samples of the disease(Fig. 2A). The other three ribotypes did not increase asmarkedly in relative abundance (Table 1) and were notconsistently the dominant ribotypes across replicatesamples (Fig. 2A). Ribotypes related to Glycomycessp. (JN406287), V. harveyi (JN406288), Microbacteriumsp. (JN406289), Ferrimonas sp. (JN406292), Cyano-bacterium sp. (JN406296), Pseudoalteromonas sp.(JN406297), Shewanella sp. (JN406298) and a Marino-bacter sp. (JN406299) were all present in clone librariesof non-diseased corals in low relative abundance(Table 1), but increased both in apparently healthy tissueand at the disease lesion itself. Interestingly, one ribotyperelated to Aeromonas sp. (JN406293) increased in domi-nance in AH but decreased again in all disease lesionsamples (Fig. 2A; Table 1). Four out of these nineribotypes (Glycomyces sp., V. harveyi, Cyanobacteriumsp. and the Aeromonas sp.) were also detected as domi-nant DGGE bands in the apparently healthy or diseasedsamples.

2 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

Microscopic and molecular identification of ciliates

Live microscopic examination of all PWS and BrB lesionsover time (Fig. 3), showed diverse communities of ciliates,in large, mobile population masses at the edge of thedisease lesions, adjacent to apparently healthy tissuesand recently exposed coral skeleton (Table 2; Figs 2B and3). Pathogenesis was observed via time-lapse videogra-phy (Videos S1 and S2) and a number of ciliate morpho-types were observed to actively engulf coral tissues at thesite of lesion progression. Ciliate communities associatedwith progressive disease lesions encompassed at least 11different ciliate morphotypes (Table 2), four of whichcontained coral endosymbiotic algae, indicative of coral

tissue ingestion. There were no ciliates observed ordetected by molecular screening in samples of non-diseased and apparently healthy coral samples (Fig. 2B).There was no significant difference (ANOSIM, R = 1,P = 0.12) between DGGE profiles of ciliate 18S rRNAgene diversity between coral species (A. muricata, n = 10;and A. aspera, n = 4) for PWS. However there wasa significant difference (ANOSIM, R = 0.56, P = 0.04)between A. muricata with PWS collected from the GBR(n = 10) and those from the Solomon Islands (n = 5)(Fig. 2B). This difference was due to the lack of somespecies, such as Euplotes sp. (JN406271), Glauconemasp. (JN406267), Holosticha sp. (HQ013356), Varistrom-bidium sp. (HQ204551) and Diophrys sp. (JN406270)

Fig. 1. Photographs of Acropora muricata atHeron island on the Great Barrier Reefexhibiting disease signs of White Syndrome(A) and Brown Band Disease (B). Scalebar = 2 mm.

Fig. 2. Representative denaturing gradient gelelectrophoresis (DGGE) profiles of: ND:non-diseased coral; AH: apparently healthy tissue– the tissue above the advancing lesion on adisease coral; PWS: Progressive White Syndrome[note: from two different species, Acroporamuricata and A. aspera, and from two differentlocations, Heron Island (GBR) and the SolomonIslands]; and BrB: Brown Band Disease; (A)bacterial 16S rRNA gene fingerprints (DGGE).Closest matches (GenBank accession numbers)from BLAST analysis: 1. Symbiotic algal DNA, 2.Endozoicomonas sp. (DQ200474), 3. Firmicutessp. (HQ444233), 4. Aeromonas sp. (HQ180147),5. Arcobacter sp. (HQ317346), 6. Vibrio harveyi(GQ203118), 7. Glycomyces sp. (JF729475), 8.Clostridium sp. (GU227558), 9. Cyanobacteriumsp. (FJ844162), and (B) ciliate 18S rRNA genefingerprint; 10. Diophrys sp. (DQ35385), 11.Pseudocarnopsis sp. (HQ228545), 12. Aspidiscasp. (AF305625), 13. Morph1 (FJ648350), 14.Morph2 (AY876050), 15. Euplotes sp.(GU953668), 16. Glauconema sp. (GQ214552),17. Varistrombidium sp. (DQ811090), 18. Euplotessp. (AY361908), 19. Hartmanula sp. (AY378113),20. Holosticha sp. (DQ059583). Composite DGGEimage standardized for gel-to-gel comparisonusing BioNumerics.

Ciliate and bacterial pathogens in coral disease 3

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

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5)1

00

00

0H

Q18

0163

Unk

now

ng-

Pro

teob

acte

riaD

Q20

4262

(99)

21

11.

50

1.4

JN40

6300

Clo

strid

ium

sp.

Clo

strid

iaC

P00

0568

(100

)1.

71

22.

32.

52.

2JN

4062

99M

arin

obac

ter

sp.

g-P

rote

obac

teria

JF97

9330

(96)

1.3

0.6

55.

96.

25.

2JN

4062

98S

hew

anel

lasp

.g-

Pro

teob

acte

riaE

U29

0154

(98)

1.5

0.9

4.8

4.9

54.

7JN

4062

97P

seud

oalte

rom

onas

spg-

Pro

teob

acte

riaG

U06

2514

(95)

24.

55.

65.

24.

75

JN40

6294

Unc

ultu

red

bact

eriu

mU

nkno

wn

GU

1855

41(9

8)0.

66.

81

00

0JN

4062

93A

erom

onas

sp.

g -P

rote

obac

teria

EU

2499

60(1

00)

27.

51

0.4

0.9

0

JF83

1360

Arc

obac

ter

sp.

e -P

rote

obac

teria

HQ

3173

46(9

9)0

2.8

5.9

76.

56

0si

gnifi

esth

atcl

ones

rela

ted

toth

atse

quen

cew

ere

not

dete

cted

inth

esa

mpl

es.A

tota

lof

392

clon

esco

ntai

ning

the

16S

rRN

Age

nein

sert

sw

ere

rand

omly

sele

cted

from

each

sam

ple

(non

-dis

ease

d(N

D)

A.m

uric

ata,

appa

rent

lyhe

alth

y(A

H)

A.m

uric

ata,

PW

SA

.mur

icat

a[G

BR

],P

WS

A.a

sper

a[G

BR

],P

WS

A.m

uric

ata

[Sol

omon

s]an

dB

rBA

.mur

icat

a[G

BR

]).

4 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

Tab

le2.

Mor

phol

ogic

alde

scrip

tions

ofth

eci

liate

svi

sual

lyob

serv

edto

beas

soci

ated

with

PW

San

dB

rBdi

seas

edco

rals

,sh

owin

gth

esp

ecie

sID

from

sing

lece

llis

olat

es,

clos

est

mat

chan

dG

enB

ank

acce

ssio

nnu

mbe

r,a

uniq

ueG

enB

ank

acce

ssio

nnu

mbe

rfo

rea

chci

liate

sequ

ence

from

this

stud

yan

da

phot

ogra

phof

each

cilia

tede

scrib

ed.

Spe

cies

IDba

sed

onm

orph

olog

yA

cces

sion

No.

Clo

sest

mat

ch(%

)D

escr

iptio

nP

hoto

IDP

WS

BrB

Mor

ph1;

HQ

2045

45/

JN62

6268

FJ6

4835

0(9

9)B

ody

slen

der,

60–2

00¥

20–6

0mm

invi

vo,

varia

ble

inou

tline

from

cylin

dric

alto

fusi

form

;an

terio

rlyna

rrow

edan

dco

nspi

cuou

sly

poin

ted.

Leng

thof

bucc

alfie

ld~

40–5

0%of

body

,cy

tost

ome

cons

picu

ous

and

deep

lysu

nk.

Pel

licle

rigid

,pa

cked

with

clos

e-se

tex

trus

omes

(c.

2–3

mmlo

ng).

Mac

ronu

cleu

sba

nd-li

ke,

twis

ted

and

posi

tione

dce

ntra

llyal

ong

cell

med

ian

with

seve

ralm

icro

nucl

eiat

tach

edto

it.O

nesm

all,

term

inal

lylo

cate

dco

ntra

ctile

vacu

ole.

App

roxi

mat

ely

50so

mat

icki

netie

sco

mpo

sed

ofm

onok

inet

ids,

with

cilia

c.7–

10mm

long

;or

alci

lia~

10–1

5mm

long

;ca

udal

ciliu

m12

–15

mmin

leng

th.

Par

oral

mem

bran

eL-

shap

ed,

onrig

htof

oral

cavi

ty,

slig

htly

obliq

ueto

mai

nbo

dyax

is.

Scu

tica

with

c.15

basa

lbod

ies.

Ext

ruso

mes

dens

ely

pack

edbe

neat

hpe

llicl

e.Lo

com

otio

nby

fast

,sp

irals

wim

min

gw

hile

rota

ting

irreg

ular

lyab

out

itsm

ain

body

axis

,m

otio

nles

sfo

rsh

ort

perio

dsw

hen

feed

ing.

Slig

ht(u

pto

0.5%

)ge

netic

varia

tion

inD

NA

sequ

ence

betw

een

indi

vidu

als

sam

pled

.

✓✓

Phi

last

ersp

.

Mor

ph2;

HQ

2045

46/

JN62

6269

AY

8760

50(1

00)

Bod

yla

rger

,20

0–50

20–7

5mm

,va

riabl

ein

outli

ne,

cylin

dric

alto

fusi

form

;an

terio

rlyro

unde

dor

slig

htly

tape

red.

Ora

ldep

ress

ion

was

cons

picu

ous

and

deep

lyin

vagi

nate

d,w

ithrig

ht-p

oste

rior

in-p

ocke

ting

supp

orte

dby

fibre

s;th

ebu

ccal

field

was

~30

–40%

ofce

llle

ngth

.T

hecy

tost

ome

was

clea

rlyde

linea

ted

byfib

res,

lead

ing

toa

cyto

phar

ynx

exte

ndin

g~

30%

ofth

ece

llle

ngth

.T

hem

acro

nucl

eus

was

saus

age-

like,

elon

gate

but

ofte

nbe

nt,

posi

tione

dce

ntra

llyal

ong

the

mai

nce

llax

is.

Mic

ronu

clei

wer

eno

tob

serv

ed,

aspr

ey(c

oral

zoox

anth

ella

ean

dne

mat

ocys

ts)

nucl

eiob

fusc

ated

iden

tifica

tion.

Som

atic

cilia

wer

e~

5mm

long

;or

alci

lia~

5–10

mmlo

ng,

form

ing

cons

picu

ous

poly

kine

tids.

Cel

lsw

ere

colo

urle

ssto

brow

nish

yello

w,

ofte

nw

ithnu

mer

ous

food

vacu

oles

orzo

oxan

thel

lae.

Div

isio

nw

asra

rely

note

din

pres

erve

dsp

ecim

ens

but

com

mon

lyse

en.

Slig

ht(u

pto

0.5%

)ge

netic

varia

tion

inD

NA

sequ

ence

betw

een

indi

vidu

als

sam

pled

.

✓✓

Por

post

oma

guam

ense

Asp

idis

casp

.JN

4062

68A

F30

5625

(100

)E

uplo

tine

hypo

tric

hci

liate

s,le

ft-se

rialo

ralp

olyk

inet

ids

sepa

rate

ddu

ring

stom

atog

enes

is;

colla

ror

alpo

lyki

netid

sin

ante

rior

vent

rald

epre

ssio

nse

para

ted

from

lape

lora

lpol

ykin

etid

sin

oral

cavi

ty;

free

-livi

ng,

ofte

nsa

prop

elic

.N

oge

netic

varia

bilit

ybe

twee

nin

divi

dual

ssa

mpl

ed.

Ciliate and bacterial pathogens in coral disease 5

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

Tab

le2.

cont

.

Spe

cies

IDba

sed

onm

orph

olog

yA

cces

sion

No.

Clo

sest

mat

ch(%

)D

escr

iptio

nP

hoto

IDP

WS

BrB

Eup

lote

ssp

.JN

4062

71G

U95

3668

(99)

Bod

ysl

ight

lyre

ctan

gula

rin

outli

ne,

90–1

40mm

long

invi

vo,

with

noco

nspi

cuou

sdo

rsal

ridge

s.Le

ngth

ofbu

ccal

field

abou

t65

%of

body

.C

ytop

lasm

hyal

ine,

cent

rala

rea

ofte

nda

rkdu

eto

food

vacu

oles

and

gran

ules

.M

acro

nucl

eus

C-s

hape

d;m

icro

nucl

eus

sphe

rical

.A

ZM

with

abou

t60

mem

bran

elle

s,pr

oxim

alpo

rtio

ncu

rved

~90

°to

right

.Te

nfr

onto

vent

ral

cirr

iin

age

nus-

typi

calp

atte

rn;

two

left

mar

gina

lcirr

isep

arat

edan

dal

igne

dev

enly

with

3or

4ca

udal

cirr

i.N

ine

or10

dors

alki

netie

sex

tend

ing

entir

ele

ngth

ofce

ll.S

ilver

line

syst

emon

dors

alsi

dere

gula

ror

irreg

ular

vann

us-t

ype.

Loco

mot

ion

bym

ediu

m-f

ast

craw

ling

onco

ral,

som

etim

esst

atio

nary

for

long

perio

ds.

No

gene

ticva

riabi

lity

betw

een

indi

vidu

als

sam

pled

.

✓✓

Dio

phry

ssp

.JN

4062

70D

Q35

3850

(99)

Bod

y~

70¥

25mm

invi

vo,

oval

tosl

ende

rov

alw

ithbo

than

terio

ran

dpo

ster

ior

ends

ofbo

dym

ore

orle

sspo

inte

d,gr

eyto

slig

htly

yello

wis

h.C

iliar

yor

gane

lles

som

etim

esco

nspi

cuou

sly

long

,es

peci

ally

the

caud

alci

rria

ndth

ean

terio

rad

oral

mem

bran

elle

s.Le

ngth

ofbu

ccal

field

40–5

0%of

body

.C

iliat

ure

typi

calo

fth

esc

utum

-mod

e:5

fron

tal,

2pr

etra

nsve

rse

vent

ral,

5tr

ansv

erse

and

3ca

udal

cirr

i.Tw

om

argi

nalc

irric

onsp

icuo

usly

sepa

rate

dfr

omea

chot

her,

post

erio

ron

eal

way

sbe

ing

belo

wtr

ansv

erse

cirr

i.P

aror

alm

embr

ane

dist

inct

lysh

orte

rth

anth

een

dora

lmem

bran

e.T

hree

larg

ege

nus-

typi

calc

auda

lcirr

i~4

dors

alki

netie

s,th

edi

kine

tids

ofw

hich

are

arra

nged

inco

ntin

uous

row

s.N

oge

netic

varia

bilit

ybe

twee

nin

divi

dual

ssa

mpl

ed.

✓✓

Var

istr

ombi

dium

sp.

HQ

2045

51D

Q81

1090

(99)

Bod

y55

–75

¥40

–50

mmin

vivo

,sl

ight

lyas

ymm

etric

and

elon

gate

dba

rrel

-sha

ped

post

erio

ren

dus

ually

blun

tlypo

inte

d;co

llar

regi

ondo

med

tofo

rma

cons

picu

ous

apic

alpr

otru

sion

;bu

ccal

cavi

tysh

allo

wan

din

cons

picu

ous,

exte

ndin

gob

lique

lyto

right

and

term

inat

ing

~15

–20%

dow

nce

ll;no

hem

ithec

ade

tect

ed.

Ext

ruso

mes

prom

inen

t,ac

icul

ar,

c.10

mmlo

ng,

even

lyar

rang

edal

ong

dors

alsi

deof

cell

and

onna

rrow

edup

per

equa

toria

land

caud

alar

eas,

not

inbu

ndle

s.M

acro

nucl

eus

ovoi

dto

ellip

soid

al;

mic

ronu

cleu

sno

tfo

und.

AZ

Mw

ithdi

stin

ctve

ntra

lope

ning

and

clea

rlydi

vide

din

toan

terio

ran

dve

ntra

lpar

tsco

mpr

isin

g15

–17

and

7or

8m

embr

anel

les

resp

ectiv

ely.

Fiv

eso

mat

icki

netie

s(S

K)

com

pose

dof

diki

netid

s.S

light

(up

to1%

)ge

netic

varia

tion

inD

NA

sequ

ence

betw

een

indi

vidu

als

sam

pled

.

✓✓

Pse

udok

eron

opsi

ssp

.H

Q01

3358

AY

8816

33(9

6)B

ody

240–

350

¥50

–90

mmin

vivo

,da

rkre

ddis

h-co

lour

,lo

ngel

liptic

alw

ithan

terio

ren

dbr

oadl

yro

unde

d,po

ster

ior

end

narr

owed

,le

ftm

argi

nco

nspi

cuou

sly

conv

ex,

right

mar

gin

dist

inct

lysi

gmoi

dal,

wid

est

inm

id-r

egio

n,do

rsov

entr

ally

flatte

ned;

.Tw

oty

pes

ofco

rtic

algr

anul

e:ty

pe1,

pigm

ente

dor

ange

,m

ainl

ygr

oupe

dar

ound

cirr

iand

dors

albr

istle

s;ty

pe2,

colo

urle

ssan

dbl

ood-

cell-

shap

ed,

lyin

gju

stbe

neat

hty

pe1

gran

ules

and

dens

ely

dist

ribut

ed.A

ppro

xim

atel

y9–

13pa

irsof

fron

talc

irrii

ntw

oro

ws

form

ing

abi

coro

na.

Pos

terio

ren

dof

bico

rona

cont

inuo

usw

ithlo

ngm

idve

ntra

lrow

of65

–93

cirr

itha

tex

tend

spo

ster

iorly

totr

ansv

erse

cirr

i.Tw

ofr

onto

-ter

min

al,

one

bucc

alan

d7–

11tr

ansv

erse

cirr

i,th

ela

tter

form

ing

aro

wth

atex

tend

sto

ante

rior

ofce

ll;48

–79

left

and

right

mar

gina

lcirr

i;5–

7do

rsal

kine

ties.

AZ

Mw

ith68

–92

mem

bran

elle

san

dex

tend

sfa

ron

torig

htsi

deof

cell.

One

cont

ract

ileva

cuol

epo

sitio

ned

inpo

ster

ior

end

ofbo

dy.

Num

erou

sm

acro

nucl

ear

nodu

les.

Loco

mot

ion

bysl

owcr

awlin

g.F

eeds

ona

varie

tyof

prot

ists

.S

light

(up

to0.

5%)

gene

ticva

riatio

nin

DN

Ase

quen

cebe

twee

nin

divi

dual

ssa

mpl

ed.

✓✓

6 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

Tab

le2.

cont

.

Spe

cies

IDba

sed

onm

orph

olog

yA

cces

sion

No.

Clo

sest

mat

ch(%

)D

escr

iptio

nP

hoto

IDP

WS

BrB

Hol

ostic

hasp

.H

Q01

3356

DQ

0595

83(9

8)B

ody

80–9

25–5

0mm

invi

vo,

gene

rally

fusi

form

with

both

ends

slig

htly

narr

owed

and

dors

oven

tral

lyfla

ttene

d.C

ortic

algr

anul

espr

omin

ent,

bloo

d-ce

ll-sh

aped

and

spar

sely

dist

ribut

ed.

Thr

eefr

onta

l,on

ebu

ccal

,tw

ofr

onto

term

inal

and

6–10

tran

sver

seci

rri.

Mid

vent

ralr

owof

13–1

7ci

rrie

xten

dsto

tran

sver

seci

rri.

One

right

and

one

left

mar

gina

lci

rral

row

s,th

ela

tter

bein

gob

lique

lybe

ntat

ante

rior

end.

Fou

rdo

rsal

kine

ties.

Ado

ralz

one

with

24–3

0m

embr

anel

les

incl

udin

g8–

13di

stal

mem

bran

elle

sth

atar

ese

para

tefr

omth

eot

hers

.Tw

oel

lipso

idm

acro

nucl

ear

nodu

les.

One

cont

ract

ileva

cuol

epo

st-e

quat

oria

llylo

cate

dan

dno

tea

sily

obse

rved

.Lo

com

otio

nm

ainl

yby

craw

ling

slow

lyon

cora

l.S

light

(up

to1%

)ge

netic

varia

tion

inD

NA

sequ

ence

betw

een

indi

vidu

als

sam

pled

.

✓✓

Eup

lote

ssp

.H

Q01

3357

AY

3619

08(9

5)B

ody

oval

inou

tline

,~60

–70

¥50

–60

mmin

vivo

,do

rsov

entr

ally

flatte

ned,

with

noco

nspi

cuou

sdo

rsal

ridge

s.Le

ngth

ofbu

ccal

field

~75

%of

body

.M

acro

nucl

eus

C-s

hape

d;m

icro

nucl

eus

sphe

rical

.P

roxi

mal

port

ion

ofA

ZM

curv

edat

~90

°to

right

.Te

nfr

onto

vent

ral,

5tr

ansv

erse

and

2ca

udal

cirr

iin

genu

s-ty

pica

lpat

tern

;tw

ole

ftm

argi

nalc

irris

epar

ated

and

alig

ned

even

lyw

ithsm

allc

auda

lcirr

i.E

ight

toni

neki

netie

sex

tend

entir

ele

ngth

ofce

ll,le

ftmos

tki

nety

cont

aini

ngon

ly~

5di

kine

tids.

Silv

erlin

esy

stem

ondo

rsal

side

irreg

ular

vann

us-t

ype.

Loco

mot

ion

bysl

ow,

slig

htly

jerk

y,cr

awlin

gon

cora

l,re

mai

ning

stat

iona

ryfo

rlo

ngpe

riods

.N

oge

netic

varia

bilit

ybe

twee

nin

divi

dual

ssa

mpl

ed.

✓✓

Gla

ucon

ema

trih

ymen

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Ciliate and bacterial pathogens in coral disease 7

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

in the Solomon Islands samples compared with thosefrom the GBR (Fig. 2B). Significant differences (ANOSIM,R = 1, P = 0.04) also occurred between PWS and BrBsamples from the same reef site and same coral species,A. muricata. However, the two dominant ciliates, Morph1(JN626268) and Morph2 (JN626269), were present inboth BrB and PWS disease lesions and at both locations(GBR and Solomon Islands), but at different populationdensities.

The most aetiologically important agent in the mixedciliate community in PWS samples appeared to be aciliate closely related to a recently described member of anew genus, Philaster sp. (FJ648350) (Zhang et al., 2011).This ciliate (Morph1 JN626268) was approximately60–80 mm long and 25–30 mm wide (Table 2). Movementin this morphotype was rapid and they were observed toactively burrow into and beneath the live coral tissues,which showed no signs of necrosis under the binocularmicroscope (Fig. 3A). This ciliate was seen in abundanceat the lesion interface and was one of the four typescontaining coral algal symbionts (Table 2). In most cases,populations of this ciliate were mixed with populationsof a larger (250–300 mm in length and 50 mm in width)ciliate Morph2 (JN626269), morphologically resemblinga recently described ciliate, Porpostoma guamensis(Lobban et al., 2011), and identical in 18S rRNA genesequence to the BrB ciliate (AY876050) identified byBourne and colleagues (2008). This ciliate was also seenin abundance at the lesion interface and also containedalgal endosymbionts from the coral (Table 2); however, itappeared to take a secondary role to Morph1 (JN626268).The movement of Morph2 (JN626269) was generally

slower and less erratic than Morph1 (JN626268), withslow turning/spinning movements. A further two ciliatespecies, Varistrombidium sp. (HQ204551) and Euplotessp. (HQ013357), dominated PWS samples (Table 2) andwas seen to a lesser extent in BrB samples. These arerelatively small species (55–70 mm in length), differingfrom the other morphotypes with prominent (~ 10–12 mm)frontal cirri. The presence of symbiotic algae in theseciliate species again indicates ingestion of coral tissue.Other members of the mixed ciliate community presentwithin PWS and BrB (Table 2) included a smaller ovoidciliate, Diophrys sp. (JN406270), and the worm-likePseudokeronopsis sp. (HQ013358); however, these weremore commonly observed in the denuded coral skeletonrather than at the advancing tissue edge and none ofthese other ciliates contained coral symbionts or wereobserved ingesting coral tissues.

18S rRNA gene sequences retrieved for Morph1(JN626268) and Morph2 (JN626269) showed the twotypes to be closely related to each other and more closelyrelated to Philaster digitiformis (FJ648350) than Porpos-toma notate (HM236335) (Figs 4 and 5). Morph1(JN626268) showed 99.3 � 0.2% similarity to P. digitifor-mis (FJ648350) while Morph2 (JN626269) showed98.7 � 0.5% similarity (Fig. 5). Morph1 (JN626268) andMorph2 (JN626269) showed slight (up to 0.5%) variationin DNA sequence within each morph (Fig. 5). The twomorphotypes shared 98.5 � 0.1% similarity in a variablesequence region, with only 7–10 mismatches over 549base pairs (Figs 5 and S1). However, there was strongbootstrap support (99.5%) in the neighbour-joining con-sensus tree for a phylogenetic separation between these

Fig. 3. Time-lapse images of PWS (A) and BrB (B) lesion progression. The lesion progresses from left to right of the images. At this scale,individual ciliates are difficult to distinguish. (A) The ciliate mass appears to be a diffuse yellow-brown mass comprised predominantly of therapidly moving Morph1 (JN626268) ciliates embedded with variable densities of Morph2 (JN626269) ciliate, while the BrB lesion (B) isdominated by the ciliate Morph2 (JN626269). These are slower moving and large enough to be seen as individual cells, typically orientatedperpendicularly to the coral skeleton surface (white) exposed by the advancing lesion. Coral tissues (yellow-brown) immediately adjacent tothe advancing lesion are intact and appear normally pigmented. Scale bar = 1 mm.

8 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

morphotypes (Fig. 5). Nine out of sixteen sequences fromMorph2 (JN626269) showed 100% sequence similarityto the ciliate identified by Bourne and colleagues (2008)from BrB disease, with the remaining seven differing byapproximately 0.2%.

Discussion

This article is the first to comprehensively describe thediverse ciliate communities associated with both WS andBrB and supports recent observations linking ciliates withPWS (Work and Aeby, 2011). Ciliates are important com-ponents of many microhabitats and are known to regulatemicrobial biomass (Vargas and Hattori, 1990) and bacte-rial community composition (Geltser, 1992), resulting instrong controls on both benthic and pelagic food webs(Fenchel, 1968; 1980; Porter et al., 1979; Wieltschniget al., 2003; Vargas et al., 2007). This primary role of

ciliates as bacterial feeders may have in the past led totheir presence on corals being dismissed as secondaryinvaders (Ainsworth and Hoegh-Guldberg, 2009). Micro-scopic examination supports the conclusion that theciliates associated with these diseases are largelyresponsible for the macroscopic signs of both PWS andBrB, namely an advancing lesion, with a sharp demarca-tion between visibly healthy tissues and the denuded skel-eton (Bythell et al., 2004). The wide diversity of ciliatetypes in all the disease lesions sampled, including at leastfour that were observed to consume coral tissues, leadsto effective clearance of tissues from the skeleton.However, we also observed at least one type (Morph1JN626268) which appears to be involved in pathogenesis.This morphotype was consistently observed at the lesioninterface and seen to burrow into and beneath apparentlyhealthy tissues, as shown histologically by Work and Aeby(2011).

Fig. 4. Neighbour-joining consensus tree of partial 18S rRNA gene sequences of 13 species of ciliates found within Brown Band Disease andProgressive White Syndrome. Number in brackets relates to number of sequences retrieved from single cell isolates. Sequences were alignedin CLUSTAL W2 (Larkin et al., 2007), using an IUB cost matrix with a gap open cost of 15 and a gap extend cost of 7. A neighbour-joiningconsensus tree (1000¥ re-sampling) was constructed in Geneious Pro 5.0 using the Tamura genetic distance model (Tamura, 1994) with anopalinid protist, Opalina ranarium (AF141970), as the outgroup.

Ciliate and bacterial pathogens in coral disease 9

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

Surprisingly, the ciliate community associated withPWS was highly similar to that associated with BrB,except that the agent previously attributed to the visiblesigns of BrB by Bourne and colleagues (2008) (ourMorph2 JN626269 = AY876050 of Bourne et al., 2008),was present in greater population densities within thebrown band, a region that is often 1–2 mm away from thedisease lesion boundary (Fig. 1B, Willis et al., 2004) andless dominant, but still consistently present in PWSsamples. The characteristic brown band of BrB has beendescribed as highly variable in ciliate population densityand may not always be visible, leading to confusion withWS in field studies (Willis et al., 2004). In both PWS andBrB, the smaller, rapidly moving ciliate (Morph1) wasmore active at the disease lesion interface. Two otherciliates Varistrombidium kielum (HQ204551) and aEuplotes sp. (HQ013357) were also shown to containcoral endosymbionts, indicative of the ingestion of coraltissues, but these were not consistently observed in allcases of the diseases.

Morph1 (JN626268) was identified both morpholo-gically and genetically as a member of the classScuticociliata, closely related to Philaster digitiformis(FJ648350). Morph2 (JN626269) was morphologicallysimilar to the ciliate associated with BrB described byLobban and colleagues (2011) as Porpostoma guamen-sis. However, the 18S rRNA phylogeny shows this ciliateto be distinct from the only Porpostoma sp. sequencedto date, Porpostoma notate (HM236335), and moresimilar to Morph1 (JN626268) and Philaster digitiformis

(FJ648350), and genetically identical to the BrB ciliate(AY876050) described by Bourne and colleagues (2008).It is therefore proposed that the proper epithet for thisciliate should be Philaster guamensis not Porpos-toma guamensis. Morph2 (JN626269) also exhibitedsimilar morphology and behaviour (orientation perpen-dicular to the coral skeleton surface), to that of the BrBciliate described by Bourne and colleagues (2008).

Contrary to our expectations, given that WS is a broaddescriptive term that has generally been assumed toencompass several distinct but visually similar diseases(Bythell et al., 2004; Sussman et al., 2008; Luna et al.,2010; Work and Aeby, 2011), the bacterial (16S rRNAgene) community structure associated with PWSwas remarkably similar between independent replicatesamples and also highly similar to the BrB bacterial (16SrRNA gene) community. In part, this was because we onlysampled actively progressing lesions and so avoidedincluding samples with arrested and recovering diseaselesions (Work and Aeby, 2011) and/or possible non-pathogenic causes of mortality such as predation, whichtogether comprised approximately 17% of apparentWS lesions observed in this study. This consistencybetween bacterial 16S rRNA gene diversity indicates thatthe progressive form of WS does not include a widevariety of disease types, at least at the locations and timesstudied.

One bacterial ribotype (Arcobacter sp. JF831360)increased consistently in all diseased samples but wasabsent in healthy coral. Similar Arcobacter sp. have pre-

Fig. 5. Neighbour-joining consensus tree ofpartial 18S rRNA gene sequences of 12samples of Morph1 (JN626268) and Morph2(JN626269) found within Brown Band Diseaseand White Syndrome, illustrating slight (up to0.5%) variation within each morphotype, but1.3–1.8% variation between morphotypesover 549 bp. Number in brackets relates tonumber of identical sequences obtained forthe given GenBank accession number fromsingle cell isolates of each morph. Sequencealignment and tree construction were asdescribed in Fig. 4. Insert histogram showssequence mismatch frequencies within andbetween sequences of Morph1 and 2.

10 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

viously been identified in Black Band Disease (Frias-Lopez et al., 2002; Sato et al., 2010) and WP (Sunagawaet al., 2009). Interestingly, this Arcobacter sp. (JF831360)appeared in apparently healthy tissues in advance of thedisease lesion and so may be a candidate pathogeninvolved in active pathogenesis. Several other bacteria –V. harveyi (JN406288), Glycomyces sp. (JN406287),Pseudoalteromonas sp. (JN406297), Shewanella sp.(JN406298) and a Marinobacter sp. (JN406299) – werealso identified in both PWS and BrB. These latter speciesincreased in relative 16S rRNA gene abundance only atthe disease lesion and not in advance of it, so althoughthey are potential pathogens, they could equally be actingas heterotrophs colonizing dead and decaying tissues.Previously, several Vibrio species have been identified aspotential WS pathogens (Sussman et al., 2008; Lunaet al., 2010). However although the techniques employedhere (both DGGE and clone libraries) do not bias againstvibrios, which we routinely detect in other coral diseases(for example in YBD, A. Croquer, A. Elliot, C. Bastidas andM.J. Sweet, unpublished), here only one strain of vibrioclosely related to V. harveyi (JN406288) was identified.This ribotype increased in relative 16S rRNA gene abun-dance in diseased samples but was also present in non-diseased, apparently healthy coral. None of the strains ofvibrio related to V. coralliilyticus implicated in WS bySussman and colleagues (2008) was detected, althoughseveral other g-proteobacteria were common in both theclone libraries and the DGGEs in this study. At present, wecannot rule out either ciliates and/or bacteria as causalagents, but the strong similarities in both bacterial andciliate communities associated with PWS and BrB andobservations of similar pathogenesis by the Morph1 ciliate(JN626268) in both diseases, strongly suggests that theyare the same disease and we recommend that they besynonymized in future.

In this study we have applied a culture-independentapproach to establish the microbial diversity (bacteria andciliates) associated with two common coral diseases. Inorder to allow sufficient sample replication for statisticalanalysis, within reasonable costs, we used a DGGEscreening approach which highlighted a number of domi-nant bacterial and ciliate ribotypes consistently associ-ated with disease lesions from different host species andenvironments. The ciliate-specific DGGE screening suc-cessfully identified ribotypes matching all of the morpho-types microscopically observed and categorized usingmorphological characters (Lee et al., 2000), suggestingthat at least in this relatively low-diversity community, theDGGE approach is accurate. For the higher diversity ofbacterial communities, greater coverage was achievedthrough generation of six clone libraries from a variety ofsamples. More complete coverage could have beenachieved via high-throughput sequencing (Mouchka

et al., 2010). However, for potential pathogen identifica-tion, the focus was on the dominant ribotypes consistentlypresent across many diverse samples rather than rareramplicons and at present clone libraries can providelonger sequence reads providing greater phylogeneticresolution. In addition, all dominant ribotypes identified inthe DGGE screening were also detected consistently inclone libraries, with the two techniques using independentprimer sets targeting different 16S rRNA gene subregions,which suggest that the effects of potential primer biaswere minimized.

Although this study was aimed at identifying the diver-sity of bacteria and ciliates associated with these coraldiseases, and disease causation cannot be tested using apurely culture-independent approach, the observationslead us to propose two alternative hypotheses for causa-tion of BrB/PWS. (i) Bacteria are the primary causalagents, invading healthy tissue and leading to an impairedphysiological condition that allows ciliate communities toinvade and proliferate at the lesion boundary, consuminghealth-compromised coral tissues. In this instance, twocandidate bacterial pathogens were seen to increasein the apparently healthy tissues in advance of thedisease lesion: Arcobacter sp. (JF831360) and Aeromo-nas sp. (JN406293). Due to the lack of consistencyamong samples and lower levels of upregulation of otherbacterial pathogens (e.g. V. harveyi, Glycomyces sp.,Pseudoalteromonas sp., Shewanella sp. and Marino-bacter sp.), we propose that these are more likely sec-ondary invaders of dead and decaying tissues followingpathogenesis. Alternatively, (ii) ciliates are the causalagents and the bacterial agents identified are eitherpathogens that infect the host after it becomes physiologi-cally stressed as a result of ciliate pathogenesis, or oppor-tunistic heterotrophs invading dead and decomposingtissues. This latter hypothesis is supported by the obser-vation that ciliates are completely absent from healthycoral and by previous studies (Ainsworth et al., 2007;Work and Aeby, 2011) which have not detected significantbacterial populations in the apparently healthy tissues atthe advancing lesion edge. Work and Aeby (2011) particu-larly point out a lack of evidence for ‘bacterial-inducednecrosis’ in the WS pathology. Under either of thesehypotheses, while bacteria may represent a systemicinfection, the ciliate communities reported in this studyappear to be responsible for the characteristic visiblesigns of PWS/BrB, namely a rapidly advancing white bandof denuded skeleton.

Experimental procedures

In order to ensure that only active diseases were sampled,apparently diseased corals were tagged and photo-monitored over 4 days and only those showing lesion pro-

Ciliate and bacterial pathogens in coral disease 11

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

gression were subsequently sampled and analysed. All BrBlesions were found to progress whereas 83% of WS caseswere progressive, which are referred to here as PWS.

To test for differences in bacterial and ciliate moleculardiversity between healthy and PWS samples, we analysedcoral fragments (~ 2 cm length) from n = 10 non-diseased(ND) samples, n = 10 PWS samples (Fig. 1A) at the diseaselesion interface and n = 10 apparently healthy (AH) tissuesadjacent to the disease lesion for a single species, A. muri-cata, at Heron Island, GBR. In addition to this, we sampledfrom different host coral species, disease signs and loca-tions in order to identify the bacterial and ciliate agents con-sistently and uniquely associated with disease lesions.Three specific contrasts were made, these were between: (i)PWS (n = 10, as above) and BrB lesions (n = 12) on A. mu-ricata from Heron Island, GBR (Fig. 1B), (ii) PWS (n = 10, asabove) on A. muricata and PWS on A. aspera (n = 4) fromHeron Island, GBR, and (iii) PWS (n = 10, as above) onA. muricata from Heron Island, GBR and PWS (n = 5) onA. muricata from Solomon Islands. Samples were placedimmediately into 50 ml falcon tubes and the water replacedwith 100% EtOH and stored at -20°C until extraction andanalysis.

Bacterial 16S rRNA gene diversity

PCR amplification and DGGE of whole coral samples. Allcoral fragments (as above) were crushed using sterile, auto-claved pestle and mortar and DNA extracted using theQiagen DNeasy Blood and Tissue Kit; spin column protocol(Sweet et al., 2010). For DGGE analysis a portion of thebacterial 16S rRNA gene was amplified using universaleubacterial primers: (357F) (5′-CCTACGGGAGGCAGCAG-3′) and (518R) (5′-ATTACCGCGGCTGCTGG-3′). TheGC-rich sequence 5′-CGC CCG CCG CGC GCG GCG GGCGGG GCG GGG GCA GCA CGG GGG G-3′ was incorpo-rated into the forward primer 357 at its 5′ end to preventcomplete disassociation of the DNA fragments during DGGE.All reactions were performed using a Hybaid PCR Expressthermal cycler. PCR reaction mixtures and programme wereas described by Sweet and colleagues (2010). PCR productswere verified by agarose gel electrophoresis [1.6% (w/v)agarose] with ethidium bromide staining and visualized usinga UV transilluminator. DGGE was performed using theD-code universal mutation detection system (Bio-Rad). PCRproducts were resolved on 10% (w/v) polyacrylamide gelsthat contained a 30–60% formamide (denaturant) gradient for13 h at 60°C and a constant voltage of 50 V. Gels werestained as described by Sweet and colleagues (2010). Toidentify the dominant DGGE bands across samples, repre-sentative bands (n = 21) were excised and sequenced toaccount for known DGGE artefacts such as heteroduplexes(Muyzer, 1999). Excised bands were left overnight in Sigmamolecular grade water, vacuum centrifuged, re-amplified withprimers 357F and 518R, labelled using Big Dye (AppliedBiosystems) transformation sequence kit and sent to Gene-vision (Newcastle University UK) for sequencing. Bacterialoperational taxonomic units (OTUs) were defined fromDGGE band-matching analysis using Bionumerics 3.5(Applied Maths BVBA) as described by Sweet and col-leagues (2010).

Clone libraries and ARDRA screening. Almost-complete 16SrRNA gene fragments were amplified from the DNA extractedusing the ‘universal’ eubacterial 16S rRNA gene primers 27F(5′-AGA GTT TGA TCG TGG CTC AG-3′) and 1542R (5′-AAG GAG GTG ATC CAG CCG CA-3′) (Cooney et al., 2002;Galkiewicz and Kellogg, 2008). Ten PCR cycles were per-formed at 94°C for 1 min, 55°C for 1 min and 72°C for 3 minthen a further 25 cycles at 94°C for 1 min, 53°C for 1 min and72°C for 3 min with a final extension at 72°C for 10 min. Theamplified products were purified using the Qiagen PCRpurification kit, inserted into the pGEM-T vector system(Promega) and transformed into Escherichia coli JM109cells. A total of 392 clones containing the 16S rRNA geneinserts were randomly selected from each sample (non-diseased A. muricata, apparently healthy A. muricata, PWSA. muricata [GBR], PWS A. aspera [GBR], PWS A. muricata[Solomons] and BrB A. muricata), and boiled lysates wereprepared from each by mixing a picked clone in 30 ml of TEand boiled for 3 min followed by freezing. Each lysate (1 ml)was amplified using the primers pUCF (5′-CTA AAA CGACGG CCA GT-3′) and pUCR (5′-CAG GAA ACA GCT ATGAC-3′). Twenty-five PCR cycles were performed at 94°Cfor 1 min, 55°C for 1 min and 72°C for 1 min with a finalextension at 72°C for 10 min. The products were thendigested with the restriction enzymes HaeIII and RsaI(Promega) [4 mg of PCR product, 2 ml of restriction buffer,0.2 ml of Bovine serum albumin (BSA), 0.07 ml of HaeIII,0.1 ml of RsaI and made up to 20 ml with sigma water for 2 hat 37°C then 10 min at 67°C]. Restriction fragments wereresolved by 3% agarose gel electrophoresis, visualized usinga UV transilluminator and grouped based on restriction pat-terns. Representatives from each group were sequenced.Closest match of retrieved sequences was determined byRDP II similarity matching (Cole et al., 2009) Out of 162clones sequenced, 52 unique sequences were retrieved fromthe six clone libraries, all sequences in this study have beendeposited in GenBank and their unique accession numbersreported in the text.

Ciliate 18S rRNA gene diversity

PCR amplification of single cell isolates. Ninety-three singlecell isolates of the 11 different ciliate morphs visually identi-fied on A. muricata exhibiting signs of both PWS and BrB atHeron Island were taken from mixed samples under binocularmicroscopy using a micropipette and preserved in 100%Analar ethanol. DNA was extracted from the ethanol-fixedsingle isolates using a modified Chelex extraction (Walshet al., 1991). All samples were vacuum-centrifuged for 10 minand washed twice in Sigma water with a 2 min centrifuge step(20 000 g) in between. Following the final wash, 50 ml of 5%Chelex 100 (sigma) solution and 15 ml of proteinase K(20 mg ml-1) were added to the cell isolate. The sampleswere subsequently left in a water bath overnight at 54°C.After incubation, they were vortexed for 20 s, boiled at 100°Cfor 10 min, vortexed for a further 20 s and centrifuged at16 000 g for 3 min. Thirty microlitres of supernatant wastaken off and put in a fresh microcentrifuge tube. This wasthen stored at -20°C until further use. Twenty microlitres ofPCR reactions were routinely used [final PCR buffer con-tained: 1 mM MgCl2, and 1 U Taq DNA polymerase (QBio-

12 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology

gene); 100 mM dNTPs; 0.2 mM of each of the forwardand reverse primers; and 0.4% BSA, with 20 ng of templateDNA extracted as above] in a Hybaid PCR-Express thermalcycler. The universal 18S rRNA gene eukaryotic primers4617f (5′-TCCTGCCAGTAGTCATATGC-3′) and 4618r (5′-GATCCTTCTGCAGGTTCACC TAC-3′) (T. Tengs, pers.comm.) were used following the PCR protocol of Oldach andcolleagues (2000). The nested PCR reaction was carried outusing 1 ml of a 1:100 dilution of the first round PCR productwith the ciliate-specific primers 384f-cil (5′-YTBGATGGTAGTGTATTGGA-3′) and 1147r-cil (5′-GACGGTATCTRATCGTC TTT-3′), amplification conditions followed that of Dop-heide and colleagues (2008). All sequences were ethanol-purified from PCR products and sequenced as above.

PCR amplification and DGGE of whole coral samples. Fromcrushed and extracted samples, ciliate 18S rRNA genes wereamplified with an un-nested PCR approach (Jousset et al.,2010). Three 10 ml replicates of each sample were run using8 ng of DNA product (PCR mixture as above) with the forwardprimer CilF (5′-TGGTAGTGTATTGGACWACCA-3′) with a36 bp GC clamp (Muyzer and Smalla, 1998) attached to the5′ end and CilDGGE-r (5′-TGAAAACATCCTTGGCAACTG-3′). Initial denaturation was at 94°C for 5 min, followed by 26cycles of 94°C for 1 min, 52°C for 1 min and 72°C for min anda final elongation step of 10 min at 72°C to reduce doublebands in the DGGE patterns (Janse et al., 2004). The threePCR products of each sample were combined and DGGEcarried out using a D-code system (Bio-Rad) with 0.75 mmthick 6% polyacrylamide gels in 1¥ TAE buffer. Electrophore-sis was carried out for 16 h at 60°C and 50 V in a linear32–42% denaturant (formamide) gradient. Gels were stainedwith SYBR Gold as above.

Microscopic observation and characterization of thedominant ciliates

Additional coral fragments showing signs of PWS (n = 5)and BrB (n = 5) on A. muricata and PWS on A. aspera(n = 5) were collected from Heron Island reef, GBR andtransferred without handling to an observation tank formicroscopic and behavioural observations of associatedciliate species using an Olympus SZX7 binocular micro-scope and Olympus LG-PS2 fibre-optic light source. Stillimages and time-lapse videos were captured using a QIm-aging Micropublisher 3.3 camera and Q-Capture v6 imagingsoftware. Higher-magnification images were obtained usingan Olympus BX51 compound microscope and images cap-tured as above. The images were compared with morpho-logical descriptions in previous studies (Carey, 1992; Leeet al., 2000; Song, 2000; Croquer et al., 2006b; Page andWillis, 2008; Shimano et al., 2008), alongside the use of adichotomous key in the ‘Illustrated Guide to the Protozoa’(Lee et al., 2000). Morphological characteristics, such ascortical and ultrastructural features, provided a means ofdistinguishing ciliate morphotypes. Features such as kine-tosomal make-up and oral infraciliary structures such as theAZM (Adoral Zone of Membranelles) are highly conservedfeatures and together with organelle distribution, size,shape and colour are routinely used for distinguishinggenera (Lee et al., 2000).

Statistical analysis

A one-way ANOSIM based on Bray-Curtis similarities of bandintensity patterns was performed to test for differencesbetween DGGE profiles of the bacterial 16S rRNA and ciliate18S rRNA gene assemblages associated with different coralspecies, locations and health states using PRIMER v6(Clarke and Warwick, 2001). Pairwise comparisons withinANOSIM were used to contrast between specific sampletypes (Anderson, 2001).

Acknowledgements

This work was supported by the Natural EnvironmentalResearch Council, UK (NE/E006949). We would also like tothank the staff at Heron Island Research Station, Australiaand Dr Olga Pantos from the University of Queensland fortheir support and cooperation in the field. We would also liketo thank Dr Zhenzhen Yi and Dr Weibo Song from the Labo-ratory of Protozoology, Institute of Evolution & Marine Biodi-versity, Ocean University of China, Qingdao, China andDr Dave Roberts and Mr Premroy Jadubansa from theMicrobiology Laboratory, Department of Zoology, NaturalHistory Museum, London, UK, for guidance in morphologicalidentification and isolation techniques of the ciliates in thismanuscript.

References

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Supporting information

Additional Supporting Information may be found in the onlineversion of this article:

Fig. S1. Regions of the alignment of partial subunit 18SrRNA gene sequences from the dominant ciliates [Morph1(JN626268) and Morph2 (JN626269)] seen in PWS and BrB,along with closest relatives available in GenBank. Referencesequence is given at the top and colour coded for individualbases. Insertions were compensated by introducing align-ment gaps (-). Matched sites are represented in dots (.).Distinct sequence signatures of each ciliate aligned areindicated in colour according to base: T = green; A = red;G = yellow; and C = blue.Video S1. Time-lapse microvideography of lesion progres-sion in White Syndrome. A diverse ciliate community canbeen seen massing at the edge and underneath the tissuesat the lesion edge. Polychaete worms can also be seenpredating on the ciliates. Individual ciliate cells of the smaller

morphotype, Morph1 (Table 2) cannot be seen at this mag-nification and appear as yellowish masses. Video sequenceis 300 frames at a sampling rate of 3 min per frame; refer toFig 3 for scale.Video S2. Time-lapse microvideography of lesion progres-sion in Brown Band Disease. A diverse ciliate community canbeen seen massing at the edge of the disease lesion. Indi-vidual ciliate cells of the smaller morphotype; Morph1(Table 2) cannot be seen at this magnification and appear asa yellowish diffuse mass. Individual cells of the larger mor-photype, Morph2 (Table 2), which gives rise to the character-istic brown band visible to the naked eye, can be seen inabundance. Video sequence is 300 frames at a sampling rateof 3 min per frame; refer to Fig 3 for scale.

Please note: Wiley-Blackwell are not responsible for thecontent or functionality of any supporting materials suppliedby the authors. Any queries (other than missing material)should be directed to the corresponding author for the article.

16 M. Sweet and J. Bythell

© 2012 Society for Applied Microbiology and Blackwell Publishing Ltd, Environmental Microbiology


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