Vol. 56, No. 3
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, Mar. 1990, p. 739-746
0099-2240/90/030739-08$02.00/0
Copyright © 1990, American Society for Microbiology
DNA Hybridization To Compare Species Compositions of Natural
Bacterioplankton Assemblagest
SANGHOON LEElt* AND JED A. FUHRMAN2
Marine Sciences Research Center, State University of New York, Stony Brook, New York 11794-5000,' and
Marine Biology Research Section, Department of Biological Sciences, University of
Southern California, Los Angeles, California 90089-03712
Received 13 July 1989/Accepted 12 December 1989
culturing. However, its application to natural bacterioplankton communities is still at the stage of testing. An extension
of this approach is single-cell identification with 16S rRNAbased probes (9). For this technique, one must devise and
produce unique probes to identify each type of cell. Both of
these techniques require extensive time and labor to analyze
a few samples for a comprehensive communitywide species
Much research has been performed to measure and combacterial activities in various marine environments,
with the goal of understanding the roles of marine microorganisms. However, bacterioplankton assemblages have usually been treated as a single group, and most of the studies
were done at the assemblage level. Although assemblagelevel measurements have their own virtue in the study and
comparison of bacterioplankton processes, bulk parameters
alone, without proper attention given to the identities of the
components, do not allow us to understand natural variabilpare
comparison.
Complete cataloging of indigenous bacterial species is an
ultimate answer to the question of "how much of what kind
of bacteria are in the water column?" However, there is a
need for a rapid and simple technique that does not necessarily identify individual species but that can differentiate
bacterial communities in terms of their constituents. This
technique is particularly suitable for answering basic questions about the variability of species composition. It is
unclear how much species compositions of bacterioplankton
assemblages vary over time and space. The measured bulk
parameters are of more use in understanding the various
aspects of marine microbial ecology if they are combined
with information regarding the variability of the species
composition. The technique also allows us to choose typical
samples for more detailed and time-consuming species composition analyses.
DNA hybridization has been used widely to investigate
the phylogenetic relatedness of bacterial strains (8, 22, 29,
30). Palleroni et al. (26) reported that DNA-DNA hybridization has a high resolution for closely related organisms
whose differences could not be distinguished by DNA-rRNA
hybridization. They often found 0% DNA-DNA homology
between Pseudomonas species, although DNA-rRNA homologies ranged from 80 to 95%. Because of the wellconserved rRNA genome (rDNA) compared with the con-
ity.
One of the major reasons that little is known about species
composition and its variation is the difficulty of conventional
identification. Conventional identification of bacteria needs
pure cultures. However, most marine planktonic bacteria
are noncultivable (CFU, <1% of total counts [11]), despite
the observation that many (40 to 90% of total counts) can be
shown to be metabolically active by microautoradiography
(13).
Comparison of the base sequences of rRNA has become a
powerful tool to infer the evolutionary pathways of procaryotes (reference 33 and references therein). Recently, a
procedure that uses rRNA sequence homology was proposed for defining and enumerating the components of a
mixed natural population of bacteria (25). It should allow the
definition of a population, both quantitatively (species diversity) and qualitatively (phylogenetic relatedness), without
*
Corresponding author.
t Contribution no. 709 from the Marine Sciences Research Center, State University of New York at Stony Brook.
t Present address: Department of Biological Sciences, University
of Southern California, Los Angeles, CA 90089-0371.
739
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Little is known about the species composition and variability of natural bacterial communities, mostly
because conventional identification requires pure cultures, but <1% of active natural bacteria are cultivable.
This problem was circumvented by comparing species compositions via hybridization of total DNA of natural
bacterioplankton communities for the estimation of the fraction of DNA in common between two samples
(similarity). DNA probes that were labeled with 35S by nick translation were hybridized to filter-bound DNA
in a reciprocal fashion; similarities (in percent) were calculated by normalizing the values to self-hybridizations. In tests with DNA mixtures of pure cultures, the experimentally observed similarities agreed with
expectations. However, reciprocal similarities (probe and target reversed) were often asymmetric, unlike those
of DNA from single strains. This was due to the relative complexity and G+C content of DNA, which provided
a means to interpret the asymmetry that was occasionally observed in natural samples. Natural bacteria were
collected by filtration from Long Island Sound (LIS), N.Y., the Caribbean and Sargasso seas, and a coral reef
lagoon near Bermuda. The samples showed similarities of <10 to 95%. The LIS and Sargasso and Caribbean
sea samples were 20 to 50% similar to each other. The coral reef sample was <10% similar to the others,
indicating its unique composition. Seasonality was also observed; an LIS sample obtained in the autumn was
40% similar to two LIS samples obtained in the summer; these latter two samples were 95% similar. We
concluded that total DNA hybridization is a rapid, simple, and unbiased method for investigating the variation
of bacterioplankton species composition over time and space, avoiding the need of culturing.
740
APPL. ENVIRON. MICROBIOL.
LEE AND FUHRMAN
0.1 point mutation per sequence position
Ref.
% G+C Ref.
[Pseudavoms testosteronA
34
NJ
"Crane Neck Isolate Ea
*
.ILN 150"
*
*
N
ProteLs wl/garis
7
40
19
Escherichia coli
6
50-51
24
[AgAobacteriwn &refacir,s
Caulobacter VOC1
Ceulobacter "VC5O
Caulobacter halobacteroides
[F/avobacteni.rn heparimru
34
NJ
*
64-67 28
*
64-67 28
*
64-67 28
32
NJ
*
*
46
"Crane Neck Isolate C"
FIG. 1. Phylogenetic tree based on 16S rRNA base sequence homology. The phylogenetic distance between two species is proportional
to the sum of the lengths of the horizontal lines linking the two. Strains within brackets were not used (NU) in this study. ND, Not determined.
This study is the source for the references with asterisks.
servation of the total genome (10), rRNA (or rDNA)
hybridization is generally used for distantly related organisms up to the kingdom level (17), whereas DNA hybridization is used for relatively closely related organisms, e.g., at
the species level (16).
We adapted the DNA hybridization technique for use with
mixed populations, exploiting this specificity of DNA hybridization. The degree of commonness of identical or very
closely related bacterial strains shared between natural
bacterioplankton assemblages was determined by community DNA hybridization. The natural samples showed a full
range (from <10% to almost 100%) of similarities, with the
results being related to sampling locations and seasons. In
tests of this method with pure cultures, we found that the
results reflect not only the amount of shared DNA but also
the relative complexity, the percent molar G+C content of
DNAs of two communities that were compared, or both.
This information was useful in interpreting the results from
natural samples.
MATERIALS AND METHODS
Bacterial strains and their phylogenetic relations. Bacterial
strains used in this study were Caulobacter sp. strains VC1
and VC5; Caulobacter halobacteroides ATCC 15269; Escherichia coli cell line K-12; and Proteus vulgaris ATCC 13315,
"LN150," "Crane Neck isolate C" ("CN-C"), and "Crane
Neck isolate E" ("CN-E"). The caulobacters were from
east Pacific deep hydrothermal vents (strains VC1 and VC5)
or filtered seawater (C. halobacteroides) and were provided
by J. Poindexter. Strain LN150 was isolated from the Pacific
Ocean near San Diego by A. Carlucci. Strains CN-C and
CN-E were isolated from Long Island Sound (LIS) by
members of our laboratory. Strains CN-C and CN-E are
oligotrophs that are capable of growth in unsupplemented
filtered seawater.
The strains used in this study are listed in Fig. 1, which is
a phylogenetic tree built with a computer program written by
G. Olsen based on 16S rRNA base sequence homology (23).
Strains were sequenced by members of our laboratory by the
reverse transcription method (18). The G+C contents reported in this study were determined by high-pressure liquid
chromatography (21). Other strains not used in this study are
included in the phylogenetic tree in Fig. 1 to help understand
the relative positions.
Preparation of DNA from cultured cells. Cells were grown
in CPM medium (seawater filtered through glass fiber filters;
diluted to 80% with deionized water, 0.05% Bacto-Peptone
[Difco Laboratories, Detroit, Mich.], and 0.05% Casamino
Acids [Difco]; and autoclaved) for the marine isolates or in
LB medium (20) for the other isolates. Cells were harvested
by centrifugation (15 min, 10,000 x g), and cell pellets
(volume, about 100 to 200 IL) were rinsed with 1 ml of
ice-cold 10% sucrose-50 mM Tris (pH 8.0) to remove the
salts and were then pelleted again. Cells were suspended in
1 ml of 10% sucrose-50 mM Tris (pH 8.0), 0.3 ml of 0.5 M
EDTA (pH 8.0) was added and mixed thoroughly, and 0.6 ml
of 10% sodium dodecyl sulfate (SDS) was added. The tube
was inverted actively until the liquid became clear. The
liquid was extracted once with phenol (pH 8.0), three times
with phenol-chloroform-isoamyl alcohol (24:6:1, by volume;
pH 8.0), and once with chloroform-isoamyl alcohol (24:1, by
volume). Ammonium acetate (final concentration, 2.5 M)
and ethanol (two times the volume of the total aqueous
phase) were added to the final aqueous phase and precipitated overnight at -20°C. The DNA was pelleted by centrifugation (10 min, 12,000 x g, 40C), rinsed with 70%
ethanol, briefly dried, and dissolved in TE (10 mM Tris, 1
mM EDTA [pH 8.0]). The DNA was quantified by bisbenzimide (Hoechst 33258 dye; Sigma Chemical Co., St. Louis,
Mo.) fluorometry (27).
Preparation of probe and target DNA. Probe DNA was
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I
64
VOL. 56, 1990
BACTERIAL COMMUNITY COMPARISON BY DNA HYBRIDIZATION
TABLE 1. Dates and locations of natural
bacterioplankton samples
Sample
(moldaylyr)
Location
Autumn LIS
11/18/87
Summer LIS-1
6/16/88
Summer LIS-2
6/23/88
Caribbean Sea
3/2/88
Sargasso Sea
Coral reef lagoon
8/27/87
8/26/87
40058' N, 73°09' W, Crane Neck,
Long Island, N.Y.
40058' N, 73009' W, Crane Neck,
Long Island, N.Y.
40058' N, 73009' W, Crane Neck,
Long Island, N.Y.
12039' N, 61047' W, 50 km
northwest of Grenada
10 km southeast of Bermuda
Coral reef, North Shore,
Bermuda
served similarities (SO) were compared with theoretical ones.
When two mixtures had a species in common, the species
contributed x (in percent) to one mixture and y (in percent) to
another, whereas x may not have been the same as y. The
smaller of the two, x and y, was used for the calculation of
the theoretical similarity (S,); i.e., S, is the least common
fraction between two mixtures. When two mixtures had n
species in common, the calculation of S, (in percent) was:
n
St =
pi,
where n is the number of common species, and pi (in
percent) is the percentage contribution of the ith common
species to either of the two mixtures, whichever one was
smaller.
Hybridization kinetics. The progress of hybridization with
incubation time was examined to understand the nature of
the hybridization under the conditions we set. Hybridization
kinetics of three different DNA types were examined: simple
DNA (single-strain DNA), complex DNA (mixture of equal
amounts of DNA from six different strains), and DNA of a
natural bacterioplankton community (from an oligotrophic
Pacific Ocean sample; 34049' N, 124008' W). Probes were
made of the three types of DNA and hybridized to the DNA
from which the probe was prepared (control) as well as to the
other DNA samples. Four replicate sets were incubated for
each DNA type; and one set was removed and processed
after 6, 12, 24, and 48 h of incubation. The similarities at
each time were calculated.
Experiments with natural bacterioplankton. Naturally occurring near-surface marine planktonic bacteria were collected with Niskin bottles (Caribbean and Sargasso sea
samples) or plastic buckets and carboys from various places
and times (Table 1). Filtration and DNA extraction followed
the protocol of Fuhrman et al. (14), with slight modifications.
Collected seawater was immediately pressure filtered from a
stainless steel pressure vessel (20 liters; Gelman Sciences,
Inc., Ann Arbor, Mich.) to which two stainless steel filter
holders (142-mm diameter; Fisher Scientific Co., Pittsburgh,
Pa.) were attached in-line in series. With gentle pressure (ca.
70 kPa), the water was first prefiltered through glass fiber
filters (type AE; Gelman) to remove larger particles, and
bacterial cells were collected on 0.22-,um-pore-size filters
(Durapore; Millipore Corp., Bedford, Mass.). The filtrations
were done in a relatively short period of time (a total of 1 to
4 h after sample collection, depending on the volume being
filtered), to prevent a possible change of the species compo-
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labeled with [a-35S]dATP or [a-35S]dCTP (Dupont, NEN
Research Products, Boston, Mass.) with a nick-translation
kit (Bethesda Research Laboratories, Inc., Gaithersburg,
Md.). The probes were purified with a nucleic acid cleaning
kit (NENSORB; Du Pont Co., Wilmington, Del.), to remove
unincorporated nucleotides and enzymes, and were dried
with a stream of N2. The dried probes were reconstituted in
50 ,l of deionized water and denatured for 10 min in a boiling
water bath before they were added to the hybridization
solution. Target DNA, which was unrestricted, unlabeled
total DNA, was loaded onto a nylon membrane (0.45-,um
pore size; Magnagraph; Micron Separations Inc., Westboro,
Mass.) in a series of dots (the amount ranged from 100 to 500
ng, each within a 5- by 5-mm square).
Hybridization. After target DNA loading, the membrane
was dried at room temperature, denatured (3 min in 1.5 M
NaCl-0.2 N NaOH; 2 min in 0.5 M Tris [pH 7.5]; 2 min in 5x
SSC [20x SSC is 3 M NaCl plus 0.3 M trisodium citrate; pH
7.0]), and baked at 80°C for 1.5 h. Filters were prehybridized
at 64 to 69°C (mostly at 68°C) for 6 to 8 h with denatured
salmon sperm DNA (1 mg/ml) in hybridization solution (6x
SSC, 1% SDS, Sx Denhardt solution [50x Denhardt solution is 1% Ficoll {Pharmacia Fine Chemicals, Piscataway,
N.J.}, 1% polyvinylpyrrolidone, and 1% bovine serum albumin]), and hybridized at the same temperature with probe
added (concentration, 0.5 to 2 ,ug/ml; 2 x 107 to 10 X 107
dpm/ml) for 24 to 28 h. The filters were washed twice in each
of 2x SSC (5 min at room temperature), 0.5% SDS in 2x
SSC (30 min at the hybridization temperature), and 0.1x
SSC (5 min at room temperature). The filters were dried at
room temperature, and the squares (5 by 5 mm) of the filter
containing each DNA dot were cut.
The radioactivities of the DNA dots were counted by
liquid scintillation with 2 ml of scintillation fluor (Ecoscint;
National Diagnostics, Manville, N.J.). The blank was a filter
square without DNA. Eucaryotic (calf thymus) DNA was
also tested as a blank. The target dots of DNA from which
the probe was prepared served as a control (control target);
i.e., the radioactivity on these dots was defined as 100%
similarity. For the calculation of observed similarity (SO),
hybridization signals (in disintegrations per minute) from
unidentical DNA dots (sample target) were normalized to the
control: S, (%) = 100 x [(R - Rb)l(RC - Rb)], where R is the
radioactivity (in disintegrations per minute) from the target
DNA dot and the subscripts s, b, and c denote, respectively,
sample DNA, blank (no DNA), and control DNA.
Degree of cross-hybridization among cultured strains. The
degree of cross-hybridization under the hybridization stringency condition we set was examined. DNAs of C. halobacteroides LN150, CN-C, and CN-E were used for the estimation of the cross-hybridization between distantly related
strains. The degree of cross-hybridization between closely
related strains was examined with DNA from the three
caulobacters, E. coli, and P. vulgaris. The degree of crosshybridization was calculated in the same way as the S,,
calculation described above.
Hybridization of mixed DNA of defined composition. The
DNAs from single strains were mixed in various manners to
make mixtures with diverse compositions and complexities.
Probes were made from the mixtures and hybridized to the
other mixtures by using the same methods and conditions
described above. Single-strain DNA was also hybridized to
mixture DNA. For tests of reciprocity (reciprocal hybridizations), the probe and target were switched (i.e., probe A to
target B and probe B to target A), and the reverse similarity
was compared with the forward one. Experimentally ob-
741
APPL. ENVIRON. MICROBIOL.
LEE AND FUHRMAN
742
4-
TABLE 3. Comparison of SO with S, from hybridizations of
single-strain DNA probe to mixture DNA targeta
(%/0)
0)
100
A
Mean ± SEM S0 (%) of the following probes:
S, (%)
o
4-' 04,
80
10
17
25
33
50
70
.0
a to
0o
-o- single-strain DNA
---e----. mixture DNA (6 sp)
//
iEN 40
O
°
4-
co
60
Co
v1)X 20
20
30
40
(15), to monitor the filtering efficiencies. The filters were
frozen immediately and kept frozen until DNA extraction.
DNA from the cells collected on the Durapore filters was
extracted in hot 1% SDS, concentrated by ethanol precipitation, and purified by phenol extraction (14). After a final
ethanol precipitation and redissolution in TE (pH 8.0), DNA
was quantified by Hoechst 33258 dye fluorometry (27) that
was modified to decrease the amount of the sample DNA
spent for the quantitation (flow-injection fluorometry; injection volume, 6 to 12 [LI of 1 to 10 ng of DNA per ,ul; final dye
concentration, 1.5 x 10-6 M).
Probe preparation and hybridization were the same as
described above. Hybridizations were carried out reciprocally except for the coral reef lagoon sample, due to a
shortage of the sample.
natural DNA
mixture DNA----
a)
.0
.60
0E
BB
100-
U)
ol
50-
_-
<
/
~~~--------.;-----
I-=L
10
0
30
20
40
12 1
20±1
21 4
37 2
64 3
69 5
5C
Incubation Time (h)
150
NDb
17±2
32 ± 2
26 ± 3
64 ± 4
ND
50
Incubation Time (h)
FIG. 2. (A) Effect of complexity on hybridization kinetics. Radioactivities of control dots were normalized to the radioactivity at
the end of the incubation (48 h). The curves, Y = k1 + k2 (natural
log of X), where k is constant, were fit by a least-squares method.
Error bars indicate 2 standard errors of the mean. (B) Similarities
determined from sample DNA dots after incubations of 6, 12, 24,
and 48 h. The six lines are from six different samples. Error bars
indicate 2 standard errors of the mean of each independent determination of the similarity.
sition under confinement (11). Subsamples were taken from
unfiltered seawater, the intermediate filtrate (between AE
filter and Durapore filter), and the final filtrate; and cells
were counted by the acridine orange direct counting method
RESULTS
Cross-hybridization among the pure strains. Cross-hybridizations of total DNA between distantly related strains were
<1% to 2%. Cross-hybridization of bacterial DNA to eucaryotic DNA (calf thymus) was <0.1%, and it was not
significantly different (paired comparison t test, 0.1 > P >
0.05) from the blank (no DNA) level, which was <7% (mode,
1%) of the control signal level during the experiments. The
range of 16S rRNA sequence homologies among the distantly related strains was 0.67 to 0.73 (given as fraction,
instead of as a percentage, to avoid confusion with total
DNA similarity). The DNA hybridization among the closely
related strains (16S rRNA homologies, 0.86 to 0.94) revealed
low similarities, from 3 to 11%, except for VC5 and C.
halobacteroides (16S rRNA homology, 0.90), which crosshybridized 30%. Cross-hybridization between E. coli and P.
TABLE 2. Comparison of S,, with S, from hybridizations of mixture DNA probe to single-strain DNA targeta
Probe
Target DNA strain
Mean ±SEM
SO (%(
CN-C
CN-E
LN150
Caulobacter strain VC5
C. halobacteroides
7 <1
144 ± 4
39 3
NP
175 ± 15
SI
%) (%)
10
30
30
30
Mean +SEM
Mea + SE
100 5
257 ± 30
53 4
NP
101 ± 12
Mixture D
Mixture C
Mixture B
Mixture A
Mean ± SEM
SIMean ±(%)SEM
Ma+SE,
(%)
S,
S,
50
17
17
17
1
33
51 7
261 ± 6
NP
33
33
19
+
Npb
S
St (%)
<1
NDc
35 ± 4
NP
NP
40
+
See text for definitions of parameters. Mixture compositions, as a percentage of the total, can be read down the S, columns. All data were from n
experiments, with two replicates for n = 1.
b
NP, Nonparticipating strain.
c ND, Not determined.
a
33
33
33
=
4
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10
D
P. vulgaris
" See text for definitions of parameters. All data were from n = 4
experiments with two replicates for n = 1.
b
ND, Not determined.
-o-- natural DNA
a:-
CN-E
VOL. 56, 1990
BACTERIAL COMMUNITY COMPARISON BY DNA HYBRIDIZATION
TABLE 4. Comparison of SO with S, from hybridizations of
mixture DNA probe to mixture DNA target'
TABLE 6. Species composition of mixture DNA
Mixture 1
Mixture 2
Mixture 3
Mixture 1
Mean ± SEM
S0 (%)
S,
Mixture 2
Mean ± SEM
SI (%)
S" (%)
b
108 ± 11
60 ± 7
94 16
% Constituent bacterial strainsa
Mixture
Probe
Target
60
75
83
+
60
17
743
75
a See text for definitions of parameters. See Table 6 for the species
compositions of the mixtures. All data were from n = 4 experiments, with two
replicates for n = 1.
b_, Self-hybridization, defined as 100% similarity.
C. halobacteroides
CN-E
CN-C
LN150
1
2
0
0
30
17
30
17
10
50
30
17
3
4
5
6
0
17
33
0
25
33
67
0
25
17
0
33
25
17
0
33
7
8
25
33
50
0
25
17
0
33
0
25
33
0
33
0
a See Fig. 1 for the G+C content of the bacterial strains.
However, hybridization done in one direction sometimes
yielded >100% S,, whereas the reverse hybridization gave a
number close to or lower than the S, (e.g., mixture 5 in Table
5). Table 5 presents extreme cases of asymmetric as well as
symmetric reciprocities from a set of experiments designed
to see this effect. S, was almost always between the two
reciprocal SO values (Table 5). Table 6 shows the compositions of the DNA mixtures.
Natural bacterioplankton. Loss of bacterial cells from the
prefiltration was 8 to 10% of the total cell count in unfiltered
seawater samples. About 1% or less passed through the
Durapore filters.
The species compositions of the natural bacterioplankton
assemblages from a variety of places and times showed a
wide range (from <10 to >90%) of similarity (Table 7). The
two LIS summer samples taken from the same site but 1
week apart were indistinguishable (>90% similarity). The
LIS autumn sample taken from the same site showed ca.
40% similarity to the two LIS summer samples, which was
higher than its similarity to samples from the open ocean
localities. The coral reef bacterioplankton assemblage was
consistently least similar (<10%) to the other assemblages,
even to nearby pelagic waters from the Sargasso Sea. The
Caribbean Sea sample was the most similar to the Sargasso
Sea sample. The reciprocal hybridizations were symmetric,
in general, except for the Sargasso and the Caribbean sea
samples and the Sargasso Sea and the LIS autumn samples
(Table 7).
DISCUSSION
General considerations. Community DNA of bacterioplankton from diverse environments is likely to have a
variety of complexities. The DNA reassociation rate is a
TABLE 5. Symmetric and asymmetric hybridization reciprocity and comparison of SO, with
SIa
Probe
Mixture 4
Target
Mean + SEM
Mixture 4
Mixture 5
Mixture 6
Mixture 7
Mixture 8
.b
201
18
110
41
S, (%)
40
14
1
4
4
Mixture 6
Mixture 5
Mean ± SEM
50
50
67
50
+
1
< 1+ <1
56 ± 3
20 ± 1
Mean ± SEM
S
50
0
75
33
60 4
6 ±2
12 <1
65 6
Mixture 7
Mean ± SEM
SI
50
0
25
67
NDc
325 45
7 1
41
2
Mixture 8
Mean ± SEM
S,
67
75
25
ND
125 ± 19
66 ± 5
70 ± 5
S
50
33
67
50
50
a Reciprocal hybridizations (probe and target exchanged) can be seen as mirror images across the diagonal. See text for definitions of parameters. See Table
6 for the species compositions of the mixtures. All data were from n = 4 experiments, with two replicates for n = 1.
b -, Self-hybridization, defined as 100% similarity.
c ND, Not determined.
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vulgaris (16S rRNA sequence homology, 0.94) was 4%. The
higher degree of cross-hybridization between VC5 and C.
halobacteroides, despite the lower 16S rRNA sequence
homology, as compared with those between E. coli and P.
vulgaris, was probably due to the high G+C content of
caulobacters (Fig. 1; discussed below).
Hybridization kinetics. Figure 2A shows the kinetics of the
three DNA types with different complexities. Regression
curves of Y = k, + k2. (natural log of X), where k is
constant, were fit by a least-squares method. The regression
curves of the three DNA types showed little difference
overall, except that the curve of the simple DNA was slightly
steeper than those of the other two DNA types. The curves
of the complex (mixture of six species) DNA and the natural
DNA were similar to each other. The similarities estimated
at each incubation time (i.e., SO) remained relatively constant at all apparent similarities over the whole incubation
period (Fig. 2B), despite the change of the absolute signal
and the different kinetics, if any, of the different types of
DNA (Fig. 2A).
Hybridization between single-strain DNA and mixture DNA
from cultures. Hybridization of a mixture DNA probe to
single-strain DNA targets usually gave high measurements
of SO, often >100% (Table 2). Hybridization of a singlestrain DNA probe to mixture DNA targets yielded a better
estimation, with S0 being close to theoretical similarity, S,
(Table 3).
Hybridization of mixture DNA. Observed and theoretical
similarities (SO and S,) were usually close within ca. 15%, or
±+1 standard error of mean (Table 4 and mixtures 6 through
8 in Table 5). Reciprocal similarities were usually symmetric; i.e., the forward and the reverse similarities agreed well
with each other (e.g., mixtures 6 through 8 in Table 5).
VC5
744
LEE AND FUHRMAN
APPL. ENVIRON. MICROBIOL.
TABLE 7. Species composition similarities of natural
bacterioplankton assemblages
10
4 SO>St I
10
U)
% Similarity of the following probes:
Autumn
Tart
Target
LIS
LISan)'
(mean)a
Autumn LIS
Summer LIS-1
Summer LIS-2
Caribbean Sea
Sargasso Sea
Coral reef
Summer
LIS-1
(mean +
SEM)bc
34 ±2
57
43
<1
43
5
94 ± 8
12 ± 3
19 ± 2
4 1
Summer
LIS-2
(mean ±
SEM)b,d
33 1
92 ± 9
30 + 9
30 8
7 1
Caribbean
Sea
(mean +
SEM)e
8 3
25 ± 13
32 + 9
(ea
(mean)a
5
13
15
119
46± 5
4
1
'-- i
Sargasso
Sa
13
function of the complexity of the DNA, i.e., sequence
diversity and size (1, 4). Unlike eucaryotic genomes, bacterial genomes do not generally contain repetitive sequences
(4), and the genome size varies relatively less from species to
species (within an order of magnitude [5]). Therefore, the
complexity in this study means DNA sequence diversity or
species diversity. If the similarity estimation is affected by
DNA complexity or incubation time, it may not be appropriate for the samples of different complexities to be hybridized in one fixed incubation time. In our experiments, the
relative signals (i.e., SO) did not change over the entire
incubation period, regardless of probe complexity (Fig. 2A
and B). According to Beltz et al. (2), the ratio of crosshybridization to self-hybridization stays constant over the
extent of the reassociation reaction when the filter-bound
target is in excess. In our study, the total amount of probe
was about one-quarter of the total amount of the control
DNA loaded onto the filter membrane. When the target is in
excess, the hybridization rate is limited by the diffusion of
the probe rather than by the complexity (12). Since the
diffusion of the probe is nonselective for the kind of DNA,
the hybridization (and SO) simply reflect the relative area of
probe-binding sites in the targets.
Community DNA similarity is an estimate of the fraction
of identical DNA shared in common between two communities. For that purpose, it is ideal that different strains do
not cross-hybridize with each other. Our tests showed that
total DNA rarely cross-hybridized (from <1 to 11%) across
the tested species (rRNA homologies, 0.67 to 0.94), except
for one case (30%). This level of cross-hybridization would
probably not cause a serious problem for general application
of the method, unless the two communities being compared
contained very closely related bacterial strains and these
strains constituted major components. For the definition of
species in bacteriology, it has been suggested that DNADNA cross-hybridization of .70% constitutes a single species (31), because the DNA hybridization technique is very
discriminating even at the species level (16). With this
criterion, a community DNA similarity of 70% can be
interpreted as indicating that the two communities are the
same at the species level. At the other extreme, it is possible
that the communities are completely different at the strain or
subspecies level. The most probable and realistic interpretation is between the two extreme examples. Given the
observation that even congeners usually cross-hybridize less
0n
(I)a).(j) lL
1
0
00
9 2
08
4So<St
8
°
o
0.1
0.1
~~--8...0
0.o_s____o
0
o
<
complex probe
simple target
1
sim-le probe
complex target
10
Relative Complexity of Target to Probe
FIG. 3. Goodness of fit of observed similarity (So) to theoretical
similarity (S,) (S,, divided by 5,) as a function of the relative
complexity of target DNA to probe DNA. The relative complexity
was calculated by dividing the number of species constituting the
target DNA by the number of species constituting the probe DNA.
The dotted line indicates the 95% confidence limit of the regression
line (solid line).
than a few percent, it is likely that the major part of the
similarity is from the presence of identical strains.
Calibration with cultures. Hybridization of a single-strain
DNA probe to a mixture DNA target gave a good estimate of
S, (Table 3), whereas hybridization of a mixture DNA probe
to a single-strain DNA target often resulted in an overestimation, sometimes >100% (Table 2). This is due to the
complexity of DNA; for example, if a mixture probe contains 20% of strain A, a sample target of 100% of strain A
would have five times the binding sites for the strain A DNA
compared with that of the control (the mixture) target, which
would contain strain A at only 20%. A reverse hybridization
of the example, a probe of 100% of strain A to a mixture
target containing 20% of strain A, would estimate So at close
to 20%, because the sample (the mixture) target would
contain 20% of strain A, whereas the control target would be
100% of strain A. When one is a subset (inclusion) or a
partial subset (partial inclusion) of the other, reciprocal
hybridization would easily be asymmetric. This is a limitation of an attempt to describe the relationship of species
composition with a single number representing the similarity. However, reciprocal hybridizations help to infer the
relative complexity of species compositions (as shown in
Tables 2 and 3).
A high percent molar G+C content (mol% G+C) also
affected the reciprocity by increasing the melting temperature of the DNA-DNA hybrid (reference 1 and references
therein). Since SO is the relative signal of a sample to a
control, a probe that has a high-G+-C-content DNA would
decrease SO by enhancing the control signal, whereas a
target with a high G+C content DNA would result in an
overestimation (mixture 5 in Table 5). The effect of high
G+C content was reflected in the asymmetry of reciprocal
hybridizations (Table 5).
A significant observation was that hybridization of a
simple probe to a complex target yielded an So value that
was closer to the 5, value than did the reverse (complex
probe to simple target) hybridization (Fig. 3; see Tables 2
and 3). The reciprocal similarities almost always bracketed
the 5,, and the S, was always much closer to the underestimated similarity (Table 5). We suspect that most variations
Downloaded from http://aem.asm.org/ on July 23, 2020 by guest
a One determination (two replicates for n = 1).
b
Samples LIS-1 and LIS-2 were collected 7 days apart.
c n = 4 (two replicates for n = 1).
d n = 6 (two replicates for n =
1).
e n = 3 (two replicates for n = 1).
f-, Self-hybridization, defined as 100% similarity.
4-
°
VOL. 56, 1990
BACTERIAL COMMUNITY COMPARISON BY DNA HYBRIDIZATION
filters) was observed. However, prefiltration selectively removed larger cells (typically, ca. >0.8 ,um in diameter; 10%
or less of the total count) and, probably, cells that were
attached to larger particles, so such bacteria are excluded
from these reported results. Cells that passed through the
Durapore filters (0.22-p.m pore size) made up a very small
fraction (<1% of the total cell count).
Possible improvements. Tetraethylammonium chloride was
introduced by Britten et al. (3) to suppress the G+C content
effect. Although not yet used for procaryotic DNA hybridization, tetraethylammonium chloride may help to separate
the complexity effect from the G+C content effect. We are
investigating this possibility. Also, preliminary experiments
indicated that closer examination of hybridization kinetics,
measurement of the melting curves of hybrid DNA, or use of
culturable strains isolated from the communities provides
more unambiguous results.
Conclusions. The differentiation of bacterioplankton assemblages has long been an unresolved problem. We chose
total community DNA extracted from mixed populations of
natural bacterioplankton to measure how close the species
compositions are between pairs of samples, circumventing
biases associated with culturing. We found that largely
noncultivable natural bacterioplankton communities have
species compositions with widely different patterns that vary
over time and space. Our methodology for community DNA
hybridization should be generally applicable for investigating
the distribution patterns of bacterial communities.
ACKNOWLEDGMENTS
We thank G. Olsen for kindly providing a computer program
written by him for sequence analysis and phylogenetic tree structure, J. Poindexter for helpful discussions and providing the Caulobacter strains, D. Dykhuizen for helpful advice, and R. Goodman
for offering the E. coli and P. vulgaris strains. We also thank E.
Carpenter and D. Capone for providing an opportunity for a
Caribbean cruise on RV Columbus Iselin.
This work was supported by grants OCE-8716988 and OCE8996117 from the National Science Foundation.
LITERATURE CITED
1. Anderson, M. L. M., and B. D. Young. 1985. Quantitative filter
hybridisation, p. 73-112. In B. D. Hames and S. J. Higgins (ed.),
Nucleic acid hybridisation: a practical approach. IRL Press,
Oxford.
2. Beltz, G. A., K. A. Jacobs, T. H. Eickbush, P. T. Cherbas, and
F. C. Kafatos. 1983. Isolation of multigene families and determination of homologies by filter hybridization methods. Methods Enzymol. 100:266-285.
3. Britten, R. J., A. Cetta, and E. H. Davidson. 1978. The singlecopy DNA sequence polymorphism of the sea urchin Strongylocentrotus purpuratus. Cell 15:1175-1186.
4. Britten, R. J., and D. E. Kohne. 1968. Repeated sequences in
DNA. Science 161:529-540.
5. Brock, T. D., and M. T. Madigan. 1988. Biology of microorganisms, 5th ed. Prentice-Hall, Inc., Englewood Cliffs, N.J.
6. Brosius, J., M. L. Palmer, P. J. Kennedy, and H. F. Noller. 1978.
Complete nucleotide sequence of a 16S ribosomal RNA gene
from Escherichia coli. Proc. Natl. Acad. Sci. USA 75:48014805.
7. Carbon, P., J. P. Ebel, and C. Ehresmann. 1981. The sequence
of the ribosomal 16S RNA from Proteus vulgaris. Sequence
comparison with E. coli 16S RNA and its use in secondary
structure model building. Nucleic Acids Res. 9:2325-2333.
8. Cox, R. L., C.-C. Kuo, J. T. Grayston, and L. A. Campbell.
1988. Deoxyribonucleic acid relatedness of Chlamydia sp. strain
TWAR to Chlamydia trachomatis and Chlamydia psittaci. Int.
J. Syst. Bacteriol. 38:265-268.
9. DeLong, E. F., G. S. Wickham, and N. R. Pace. 1989. Phyloge-
Downloaded from http://aem.asm.org/ on July 23, 2020 by guest
from a good fit when the probe had equal or less complexity
than the target were due to the percent G+C effect.
Calibration summary. From the pure culture experiments,
we can conclude the following. When reciprocal similarities
are symmetric, (i) a high similarity (>90%) indicates a nearly
identical species composition; (ii) a low similarity (<10%)
indicates that few or no identical species are present; and (iii)
an intermediate similarity indicates that a part of each
assemblage is in common or that a large fraction is phylogenetically close species, but it is most likely that the major
part of the similarity is from the identical strains that are
present. When reciprocal hybridizations are asymmetric,
(iv) the true similarity is closer to the lower of the two
measured values, and (v) the higher similarity indicates that
(a) the probe is more complex (more species each contributing a small percent) than the target (subset or partial subset
of the probe, with fewer species each contributing a high
percent), (b) DNA that is in common between the samples
has a high percent G+C content and makes up a larger
fraction of the target than of the probe, or (c) both. With the
current protocol at a fixed hybridization temperature, situations i, ii, and iv give unambiguous answers, but situations iii
and v have more than one possible interpretation. However,
a higher similarity means that there is a greater chance that
identical species are present than a lower similarity does.
Ways to potentially resolve the ambiguities are discussed
below.
Natural assemblages. The two LIS summer communities
taken 1 week apart were indistinguishable (>90%), while the
LIS autumn community taken from the same site was about
40% similar to the two LIS summer samples. Thus, the
species composition of the LIS samples changed significantly over time, yet the patterns in comparison with those
of samples from other locations suggest that certain species
were present in LIS throughout the studied period. Not
surprisingly, species composition also showed geographical
variations. The coral reef bacterioplankton assemblage was
found to be unique (<10% similarity to all others), even
when it was compared with assemblages from the nearby
Sargasso Sea, with which it must periodically mix during
rough weather. The Caribbean Sea sample was found to be
the most similar to the Sargasso Sea sample among the
samples that were compared, again, as might be expected.
A few natural communities showed a significant asymmetric reciprocity. This suggests that the natural communities
may be composed of heterogeneous groups and, thus, may
have a comparable complexity and a balanced distribution of
G+C content. Our measurements of the G+C content of
natural bacterial community DNA from LIS (summer and
autumn) and Sargasso Sea (summer) by high-pressure liquid
chromatography (21) ranged from 40 to 50%, despite the
potentially wide range of G+C content of procaryotic organisms (20 to 78% [5]). Asymmetric reciprocity between the
Sargasso and the Caribbean sea samples may indicate,
according to the results from pure cultures, that (i) the
Caribbean Sea sample has a major component of high G+C
content of DNA in common with the Sargasso Sea sample,
(ii) the Caribbean Sea community is a subset or a partial
subset (less complex) of the Sargasso Sea sample (more
complex), or (iii) both. The same reasoning may be proposed
for the asymmetric reciprocity between the Sargasso Sea
and the autumn LIS samples.
Since for our method we used extracted DNA to infer
species variations, it is important that the sample DNA
properly represents the community. No significant variation
in filtration efficiencies (88 to 91% collected on Durapore
745
746
10.
11.
12.
13.
15.
16.
17.
18.
19.
20.
21.
netic stains: ribosomal RNA-based probes for the identification
of single cells. Science 243:1360-1363.
Dubnau, D., I. Smith, P. Morell, and J. Marmur. 1965. Gene
conservation in Bacillus species. I. Conserved genetic and
nucleic acid base sequence homologies. Proc. Natl. Acad. Sci.
USA 54:491-498.
Ferguson, R. L., E. N. Buckley, and A. V. Palumbo. 1984.
Response of marine bacterioplankton to differential filtration
and confinement. Appl. Environ. Microbiol. 47:49-55.
Flavell, R. A., E. J. Birfelder, J. P. M. Sanders, and P. Borst.
1974. DNA-DNA hybridization on nitrocellulose filters. 1. General considerations and non-ideal kinetics. Eur. J. Biochem.
47:535-543.
Fuhrman, J. A., and F. Azam 1982. Thymidine incorporation as
a measure of heterotrophic bacterioplankton production in
marine surface waters: evaluation and field results. Mar. Biol.
66:109-120.
Fuhrman, J. A., D. E. Comeau, i. Hagstrom, and A. M. Chan.
1988. Extraction from natural planktonic microorganisms of
DNA suitable for molecular biological studies. Appl. Environ.
Microbiol. 54:1426-1429.
Hobbie, J. E., R. J. Daley, and S. Jasper. 1977. Use of
Nuclepore filters for counting bacteria by fluorescence microscopy. Appl. Environ. Microbiol. 33:1225-1228.
Kaneuchi, C., M. Seki, and K. Komagata. 1988. Taxonomic
study of Lactobacillus mali Carr and Davis 1970 and related
strains: validation of Lactobacillus mali Carr and Davis 1970
over Lactobacillus yamanashiensis Nonomura 1983. Int. J.
Syst. Bacteriol. 38:269-272.
Kwok, S., T. J. White, and J. W. Taylor. 1986. Evolutionary
relationships between fungi, red algae, and other simple eucaryotes inferred from total DNA hybridizations to a cloned basidiomycete ribosomal DNA. Exp. Mycol. 10:196-204.
Lane, D. J., K. G. Field, G. J. Olsen, and N. R. Pace. 1988.
Reverse transcriptase sequencing of ribosomal RNA for phylogenetic analysis. Methods Enzymol. 167:138-144.
Lautrop, H. 1974. Genus X. Proteus, p. 327. In R. E. Buchanan
and N. E. Gibbons (ed.), Bergey's manual of determinative
bacteriology, 8th ed. The Williams & Wilkins Co., Baltimore.
Maniatis, T., E. F. Fritsch, and J. Sambrook. 1982. Molecular
cloning: a laboratory manual. Cold Spring Harbor Laboratory,
Cold Spring Harbor, N.Y.
Mischke, C. F., and E. Wickstrom. 1980. Deoxynucleoside
composition of DNAs and modified nucleoside composition of
tRNAs determined at nanomole sensitivity by reversed-phase
liquid chromatography. Anal. Biochem. 105:181-187.
22. Moore, R. L., J. Schmidt, J. Poindexter, and J. T. Staley. 1978.
Deoxyribonucleic acid homology among the caulobacters. Int.
J. Syst. Bacteriol. 28:349-353.
23. Olsen, G. J. 1988. Phylogenetic analysis using ribosomal RNA.
Methods Enzymol. 164:793-812.
24. 0rskov, F. 1974. Genus I. Escherichia, p. 293. In R. E.
Buchanan and N. E. Gibbons (ed.) Bergey's manual of determinative bacteriology, 8th ed. The Williams & Wilkins Co.,
Baltimore.
25. Pace, N. R., D. A. Stahl, D. J. Lane, and G. J. Olsen. 1986. The
analysis of natural microbial populations by ribosomal RNA
sequences. Adv. Microb. Ecol. 9:1-55.
26. Palleroni, N. J., R. Kunisawa, R. Contopoulou, and M. Doudoroff. 1973. Nucleic acid homologies in the genus Pseudomonas.
Int. J. Syst. Bacteriol. 23:333-339.
27. Paul, J. H., and B. Myers. 1982. Fluorometric determination of
DNA in aquatic microorganisms by use of Hoechst 33258. Appl.
Environ. Microbiol. 43:1393-1399.
28. Poindexter, J. S. 1974. Genus Caulobacter, p. 153. In R. E.
Buchanan and N. E. Gibbons (ed.), Bergey's manual of determinative bacteriology, 8th ed. The Williams & Wilkins Co.,
Baltimore.
29. Salyers, A. A., S. P. Lynn, and J. F. Gardner. 1983. Use of
randomly cloned DNA fragments for identification of Bacteroides thetaiotaomicron. J. Bacteriol. 154:287-293.
30. Stackebrandt, E., B. Wunner-Fussel, V. J. Fowler, and K.-H.
Schleifer. 1981. Deoxyribonucleic acid homologies and ribosomal ribonucleic acid similarities among sporeforming members of the order Actinomycetales. Int. J. Syst. Bacteriol.
31:420-431.
31. Wayne, L. G., D. J. Brenner, R. R. Colwell, P. A. D. Grimont,
0. Kandler, M. I. Krichevsky, L. H. Moore, W. E. C. Moore,
R. G. E. Murray, E. Stackebrandt, M. P. Starr, and H. G.
Truper. 1987. Report of the ad hoc committee on reconciliation
of approaches to bacterial systematics. Int. J. Syst. Bacteriol.
37:463-464.
32. Weisberg, W. G., Y. Oyaizu, H. Oyaizu, and C. R. Woese. 1985.
Natural relationship between bacteroides and flavobacteria. J.
Bacteriol. 164:230-236.
33. Woese, C. R. 1987. Bacterial evolution. Microbiol. Rev. 51:
221-271.
34. Yang, D., Y. Oyaizu, H. Oyaizu, G. J. Olsen, and C. R. Woese.
1985. Mitochondrial origins. Proc. Natl. Acad. Sci. USA 82:
4443-4447.
Downloaded from http://aem.asm.org/ on July 23, 2020 by guest
14.
APPL. ENVIRON. MICROBIOL.
LEE AND FUHRMAN