Previous Article | Next Article 
Appl Environ Microbiol, July 1998, p. 2730-2735, Vol. 64, No. 7
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
A Chromosomally Based tod-luxCDABE
Whole-Cell Reporter for Benzene, Toluene, Ethybenzene, and
Xylene (BTEX) Sensing
B. M.
Applegate,
S.
R.
Kehrmeyer, and
G. S.
Sayler*
Department of Microbiology and the Center for
Environmental Biotechnology, University of Tennessee, Knoxville,
Tennessee 37996-1605
Received 30 September 1997/Accepted 28 April 1998
 |
ABSTRACT |
A tod-luxCDABE fusion was constructed and introduced
into the chromosome of Pseudomonas putida F1, yielding the
strain TVA8. This strain was used to examine the induction of the
tod operon when exposed to benzene, toluene, ethylbenzene,
and xylene (BTEX) compounds and aqueous solutions of JP-4 jet fuel
constituents. Since this system contained the complete lux
cassette (luxCDABE), bacterial bioluminescence in response
to putative chemical inducers of the tod operon was
measured on-line in whole cells without added aldehyde substrate. There
was an increasing response to toluene concentrations from 30 µg/liter
to 50 mg/liter, which began to saturate at higher concentrations. The
detection limit was 30 µg/liter. There was a significant light
response to benzene, m- and p-xylenes, phenol,
and water-soluble JP-4 jet fuel components, but there was no
bioluminescence response upon exposure to o-xylene. The
transposon insertion was stable and had no negative effect on cell
growth.
 |
TEXT |
Due to the widespread use of
petroleum products and the current regulations requiring underground
storage tanks to be upgraded, replaced, or closed by December 1998 (4), the number of petroleum-contaminated sites has
abounded. Of particular concern for drinking water quality are the more
water-soluble components, benzene, toluene, ethylbenzene, and xylenes
(BTEX). Natural attenuation, which relies on in situ biodegradation of
pollutants, has received a large amount of attention, especially for
petroleum contaminants (15). While microorganisms capable of
biodegradation of BTEX compounds are usually present at these sites,
there is a need to know whether or not conditions are favorable for
biodegradation to occur. A recent approach to determine whether
compounds are bioavailable and what conditions are favorable for
degradation is the use of whole-cell bioluminescent reporters
(9).
Bioluminescent reporters have been widely used for the real time
nondestructive monitoring of gene expression. Heitzer et al.
(8) developed a quantitative assay for naphthalene
bioavailability and biodegradation by using a nah-lux
reporter strain constructed by King et al. (13) and expanded
its use as an on-line optical biosensor for application in groundwater
monitoring (10). Other lux fusions have been
constructed for monitoring the expression of catabolic genes, including
those for degradation of isopropylbenzene (21) and toluene
(1, 5). lux fusions have also been constructed for monitoring heat shock gene expression (24, 25),
oxidative stress, (3), the presence of Hg(II)
(20), and alginate production (26). In all of
these cases, the lux fusions were plasmid based and were
constructed by placing the promoter of interest in front of the
promoterless lux genes from Vibrio fischeri
contained in pUCD615 (18).
In this study, a strategy was pursued to introduce a single copy of the
lux fusion into the bacterial chromosome via a transposon delivery system. A mini-Tn5 delivery vector constructed by
Herrero et al. (11) provided the basic model for this work.
By this approach, a tod-lux fusion was constructed and
introduced into Pseudomonas putida F1 to examine the
induction of the tod operon when exposed to BTEX compounds
and aqueous solutions of JP-4 jet fuel constituents. Since this system
contains the complete lux cassette
(luxCDABE), bacterial bioluminescence was measured
on-line in whole cells without addition of an aldehyde substrate. The resultant strain was also evaluated for its stability and fitness compared to those of the wild-type strain, F1.
Organisms and culture conditions.
The strains used in these
experiments are shown in Table 1. All
cultures were grown at 28°C with appropriate antibiotic selection, except for Escherichia coli strains, which were grown at
37°C.
DNA isolation and manipulation.
Large-scale plasmid DNA
isolation was done by a modified alkaline lysis protocol
(16). Chromosomal DNA was prepared by the protocol outlined
by Ausubel et al. (2). All DNA preparations were further
purified by CsCl-ethidium bromide ultracentrifugation (19).
DNA modifications and restriction endonuclease digestions were
performed as outlined by Sambrook et al. (19).
Transposon and plasmid construction.
The transposon
mini-Tn5KmNX was constructed with two 58-base
oligonucleotides 5' and 3' with respect to the kanamycin resistance gene (Kmr) in pCR II (Invitrogen, San Diego, Calif.) (I
end,
5'GGGCGCTAGCGAAATGTTGACTGTCTCTTGATCAGATC TTTCAATTCAGAAGAACTCG3';
O end,
5'CGAATTCTGACTCTTATACACAAGTTCTAGATTGCGGCCGCTTGG TTAAAAAATGAGC3').
Oligonucleotides were synthesized with a Beckman Oligo 1000 DNA
synthesizer (Palo Alto, Calif.). Base substitutions were made to
generate both I and O insertion sequences as well as unique
NotI and XbaI sites inside the transposon for
cloning. An extra adenine was mistakenly added between the
NotI and XbaI sites in the O primer, but it did
not affect the construction. Primers were used to amplify the kanamycin
resistance gene from pCR II by using touchdown PCR (7). The
manufacturer's protocol was used with the following thermocycler
conditions. Initial denaturation at 94°C for 5 min, followed by five
cycles of denaturation at 94°C for 1 min, 72°C annealing for 1 min,
and 72°C extension for 2 min. The annealing temperature was then
lowered 5°C every five cycles until 42°C, at which point, eight
cycles were run, followed by a final extension of 15 min at 72°C. The
resultant PCR fragment was cloned into the transposon delivery vector
pUT, generating pUTK210. The cloning vector pLJS was constructed from
pBluescript II (KS) (Stratagene, LaJolla, Calif.) by cleavage with
BssHII removing the multicloning site (MCS). The resultant
plasmid was named "pBSMCS(
)." Two oligonucleotides (a
47-mer and a 44-mer) (KpnI end,
5'CCAAGCGCGCAACTAGTCTAGACTAAAGCTAGCCTAGGCTGGGATCC3'; SacI end,
5'GTGAGCGCGCGTAATACGAGCTAGCCTAGGGCGAATTGGAGCA C3')
were synthesized to regenerate the MCS and add the restriction
sites XbaI, NheI, SpeI, and
AvrII. The orientation of the added sites can be seen in
Fig. 1. The new MCS was amplified from
pBluescript II (KS) by using the manufacturer's protocol with the
following thermocycler conditions. Initial denaturation was at 94°C
for 5 min, followed by 38 cycles of denaturation at 94°C for 30 s, annealing at 42°C for 1 min, extension at 72°C for 30 s,
and final extension at 72°C for 15 min. The amplified fragment was
cleaved with BssHII, ligated into pBSMCS(
), and
transformed into DH5
. A portion of pLJS was sequenced, confirming
the base substitutions and integrity of the MCS, with an Applied
Biosystems model 373A sequencer (Foster City, Calif.). Plasmid pLJST2
was generated by directional cloning of the 0.8-kb
HindIII-HincII fragment containing the 5S
ribosomal rrnB T1T2 transcription
terminator from pKK223-3 (Pharmacia, Piscataway, N.J.) into pLJS
cleaved with HindIII and SmaI. The
NotI-AvrII terminator fragment from pLJST2 was
subsequently cloned into the NotI-XbaI site of
pUTK210, yielding pUTK211 containing mini-Tn5KmT2. This
allowed for the subsequent destruction of the XbaI site by
heterologous ligation and the regeneration of the NotI and
XbaI unique sites downstream of the terminator.
Mini-Tn5Kmtod-lux (pUTK214) was generated by
directional cloning of the 10.2-kb NotI-XbaI
tod-lux fragment from pUC18Not-todlux (Table 1)
into the NotI-XbaI site of pUTK211. Both the
insert and vector DNA were purified by agarose gel electrophoresis and
electroeluted prior to cloning. Electrocompetent E. coli
S17-1(
pir) cells were prepared and ligations were
electroporated as outlined by the manufacturer (BTX, San Diego,
Calif.). All other plasmids and relevant constructs are described in
Table 1.

View larger version (20K):
[in this window]
[in a new window]
|
FIG. 1.
(A) Construction of
mini-Tn5Kmtod-lux. A/X and Nh/X represent the
AvrII-XbaI and NheI-XbaI
heterologous cloning sites, respectively. N, NotI; Sa,
SalI; X, XbaI. (B) Cloning plasmid pLJS with
unique restriction sites. A, AvrII; Ac, AccI; Ap,
ApaI; B, BamHI; Bs, BstXI; C,
ClaI; D, DraII; E, EcoRI; Ea,
EagI; EV, EcoRV; H, HindIII; Hc,
HincII; K, KpnI; Nh, NheI; P,
PstI; S, SpeI; Sc, SacI; ScII,
SacII; Sm, SmaI; Xh, XhoI.
|
|
Strain construction.
Plasmid pUTK214 was conjugated into
P. putida F1 from E. coli
S17-1(
pir) as previously described (6).
Strains carrying transposon insertions were selected on
Pseudomonas isolation agar (Difco, Detroit, Mich.)
supplemented with 50 µg of kanamycin/ml. Colonies which produced
light upon exposure to toluene were grown in mineral salts media (MSM)
(23) with toluene vapor to ascertain that the transposon had
not inserted into a gene required for cell growth and also to evaluate
their performance as bioreporters in liquid, growing-cell assays
(8). A strain designated TVA8 was selected for further study
and subjected to DNA-DNA hybridization to verify transposition, as
opposed to recombination, by using a 32P-labeled probe
specific for the Tn5 transposase (tnp) contained on pUT. Equal target amounts of luxA, todC, and
tnp DNA were loaded onto a Biotrans nylon membrane (ICN,
Irvine, Calif.) by using a Bioslot blot apparatus (Bio-Rad, Hercules,
Calif.) according to the manufacturer's protocol. The blot consisted
of chromosomal DNA from F1, TVA8, and the aforementioned controls. The
DNA was loaded in triplicate, the blot was subdivided, and each
separate blot was hybridized with either luxA,
todC, or tnp PCR-generated P-labeled DNA probes. Blots, hybridized and washed as
previously described (1), verified that TVA8 contained
luxA and todC but not tnp (data not
shown). The negative transposase result confirmed that transposition
had occurred.
Stability assays.
Batch stability assays were performed by
transfer of 1 ml of a 100-ml overnight culture grown in Luria-Bertani
(LB) broth with 50 µg of kanamycin/ml (LBKm50) to a
250-ml Erlenmeyer flask with toluene used as the sole carbon source
(supplied as vapor). One milliliter of culture was transferred every
day for 5 days to flasks containing 100 ml of MSM supplied with toluene
vapor (without Km50). Assays were performed in triplicate.
Before each transfer, cells were plated on selective
(LBKm50) and nonselective (LB) media to ascertain
loss of kanamycin resistance resulting from deletion or excision
of the transposon. Colonies were subjected to colony hybridization with
a 295-bp luxA DNA probe (12). Stability was also
assayed in continuous culture with a New Brunswick Bio Flow fermentor
(Edison, N.J.) with a 370-ml vessel operated at 28°C at 180 rpm. The
feed consisted of MSM supplemented with toluene at approximately 100 mg/liter at a flow rate of 1.0 ml/min. Toluene was fed by
simultaneously adding toluene-saturated MSM at a flow rate of 0.2 ml/min and MSM at a flow rate of 0.8 ml/min by using FMI metering pumps
(Oyster Bay, N.Y.). The fermentor was operated for 14 days (100 generations) with daily bioluminescence and optical density (OD)
measurements. Plate counts (at 7 and 14 days) from selective
(LBKm50) and nonselective (LB) media were compared to determine if the kanamycin marker was being lost, and luxA
colony blot hybridization was performed to confirm that all colonies contained the lux transposon insert. In batch and chemostat
stability studies, TVA8 did not demonstrate instability when subjected
to the same evaluation. From batch assays, the selective/nonselective plate count ratio was 1.12 ± 0.13 after five daily transfers, and
all colonies hybridized with the luxA probe. After a 14-day continuous cultivation, the selective/nonselective plate count ratio
was 1.05 ± 0.13, and all colonies from selective and nonselective plates were lux positive.
Comparison of growth of TVA8 and F1 on toluene.
To examine the
effect of bioluminescence on the fitness of TVA8, growth curves of TVA8
and F1 were obtained by growing cells in 100 ml of MSM in 250-ml
Erlenmeyer flasks with toluene vapor supplied as the sole carbon
source. Flasks were inoculated from a fresh overnight culture, grown to
an OD at 546 nm (OD546) of 1.0 in 100 ml of LB, washed
twice in 100 ml of MSM, and resuspended in 100 ml of MSM. A 1-ml
aliquot of this suspension was added to the toluene flasks. The
cultures were shaken at 200 rpm at 28°C and sampled approximately
every hour. The OD546 was measured for each culture, and
rates of increase in OD were determined from the linear portion of the
curves. Growth curves for TVA8 and the parent strain F1 on toluene
vapor are shown in Fig. 2. The curves
show similar shapes with different lag times for TVA8 and F1 that can
be attributed to slightly different inoculum concentrations. Rates were
computed from the slopes of the linear portion of the growth curve for
both strains. The average rates of increase in OD for F1 and TVA8 were
(2.1 ± 0.3) and (2.2 ± 0.3) min
1 × 10
3, respectively and were not statistically different
(
= 0.05). These results demonstrate that the bioluminescence
reactions do not appear to affect cell growth.

View larger version (16K):
[in this window]
[in a new window]
|
FIG. 2.
Bioluminescence and growth of TVA8 and growth of F1 on
toluene vapor under batch conditions. , , and represent
individual replicates of bioluminescence readings over time. The solid
squares (TVA8) and circles (F1) represent the average OD546
of three replicates.
|
|
Bioluminescence of TVA8 was measured during growth on toluene and is
shown along with the cell density data in Fig.
2. The
graph shows that
there is a relationship between an increase in
biomass and an increase
in light production. At higher cell densities,
cells likely became
limited for oxygen, resulting in decreased
bioluminescence. Specific
bioluminescence (nanoamperes/OD
546)
of TVA8 versus time
shows an increase in specific bioluminescence
(Fig.
3). This suggests that a steady state of
luciferase in the
cell is not obtained in this time frame and that
luciferase is
accumulating (Fig.
3).

View larger version (11K):
[in this window]
[in a new window]
|
FIG. 3.
Specific bioluminescence of TVA8 grown on toluene vapor.
The regression line equation is y = 116x 418 (r2 = 0.982). (The
first four time points were not included in the linear regression
because the organisms were in lag phase.)
|
|
Bioluminescence response of TVA8 to toluene, BTEX compounds, and
JP-4 jet fuel.
Bioluminescence assays were conducted as described
by Heitzer et al. (8). Aqueous solutions of toluene,
benzene, ethylbenzene, phenol, isomers of xylene, and JP-4 jet fuel
constituents were prepared by adding pure hydrocarbon or JP-4 to MSM in
a 1:10 (vol/vol) ratio. The solutions were placed on a rotary shaker
for 24 h. After phase separation, aqueous-phase aliquots were
added to test vials. Final concentrations of dissolved toluene in
growing-cell assays ranged from 0 to 50 mg/liter (based on water
solubility). The final concentration of the other hydrocarbons was 50 mg/liter (based on their water solubility), and the percentage of
JP-4-saturated MSM in the test samples was 2%. Vials containing test
solutions and cells were shaken at 150 rpm on a rotary shaker, and
bioluminescence was measured every 30 min. Sample vials were placed in
a light-tight box, and light output was measured with a liquid light
pipe and an Oriel photomultiplier and digital display (models 77340 and 7070; Stratford, Conn.) (8). The light detection methods for continuous culture and growth curves were similar, except that the
light-tight box was modified to hold a cuvette, allowing for light
measurements and OD readings to be taken consecutively.
In preliminary experiments, an incubation time of 2 h was shown to
provide a consistent light response and signal intensity.
After 2 h, the final OD
546 was measured, and values were expressed
as specific bioluminescence (nanoamperes/OD
546). An
increase in
bioluminescence was observed to correlate with increasing
toluene
concentrations (Fig.
4). The
bioluminescence response to toluene
concentrations over the range of 5 to 20 mg/liter was linear,
with specific bioluminescence values of 133 to 228 nA/OD
546. The
fold increase in light response for
concentrations above 20 mg/liter
was less, showing a specific
bioluminescence value of 290 nA/OD
546 at 50 mg of toluene
per liter. The overall bioluminescence response
curve exhibited
Michaelis-Menten kinetics, showing saturation
at higher toluene
concentrations. The toluene detection limit
was determined to be 30 µg/liter (threefold increase over background
bioluminescence). There
was a significant light response to benzene,
m- and
p-xylenes, phenol, and JP-4 (Table
2). The same concentrations
of toluene
and benzene (50 mg/liter) resulted in a similar light
response. There
was no increase in bioluminescence upon exposure
to
o-xylene. The light response due to JP-4 was significantly
greater than the additive responses for JP-4 components (i.e.,
BTEX
compounds) present at their estimated concentrations in water
saturated
with JP-4 (
22). The increased response may be the
result of
induction due to other components of JP-4 which were
not tested. A
significant light response was observed for ethylbenzene
after 4 h. After a 2-h incubation, the cell densities for the
ethylbenzene
treatments were significantly less than those for
the other samples,
indicating that there may have been a toxicity
effect. Further
experiments showed that 50 mg of ethylbenzene
per liter would induce
the bioluminescence response without a
lag period when cells were
previously grown on ethylbenzene and
then subjected to growing-cell
assays.

View larger version (13K):
[in this window]
[in a new window]
|
FIG. 4.
Bioluminescence response of TVA8 to increasing
concentrations of toluene after a 2-h exposure. Values are averages of
three replicates and have been normalized to the cell density
(OD546).
|
|
Conclusions.
The majority of bioluminescent reporter systems
currently being used are the result of cloning of a promoter in front
of either a promoterless luxAB or luxCDABE gene
cassette and transfer of the plasmid construct into the strain that
contained the particular promoter. Plasmid-based systems have obvious
drawbacks, such as the need for constant selective pressure to ensure
plasmid maintenance (17). Another important consideration is
plasmid copy number. In a positively regulated system, copy number can
negatively effect gene expression. Multiple copies of the promoter
binding region for the regulatory protein on the plasmid compete with
the binding site on the chromosome, causing less expression of the
operon being studied (27). This negative effect is important
when lux fusions are used for on-line monitoring of
bacterial processes.
TVA8 was capable of growth on MSM with toluene as a sole carbon source,
demonstrating that the transposon insertion did not
disrupt a gene
necessary for growth. Furthermore, TVA8 did not
show loss of the
transposon insertion or loss of bioluminescence
after 100 generations
in continuous culture or five successive
transfers in batch culture
without antibiotic selection. These
results indicate that selective
pressure is not necessary for
strain integrity. This stability is
important, since it eliminates
the need for antibiotic selection,
which, if required, would exclude
the use of this bioreporter in situ.
TVA8 was also compared to
the wild-type strain, F1, to ascertain
whether or not the bioluminescent
reporter incurred a significant
metabolic demand on the cell,
as well as whether the site of
transposition was a hindrance to
the cell. No difference in growth
between the two strains was
seen, suggesting that neither the insertion
site nor the
lux fusion
was a significant handicap to the
cell.
The
tod-lux reporter was highly sensitive, detecting 30 µg
of toluene/liter. This bioreporter also showed a very low background
level of bioluminescence (less than 1 nA/OD
546),
demonstrating
its usefulness for detecting toluene present at low
concentrations
in aqueous solutions. Significant light levels were
observed for
very low ODs (Fig.
2).
TVA8 can be described as a generalized BTEX bioreporter rather than
simply a toluene bioreporter, since it was responsive
to benzene,
ethylbenzene, and
m- and
p-xylene and can
therefore
be used as a bioreporter for hydrocarbon contamination for
fuels
containing BTEX compounds. TVA8 can also be used for on-line
monitoring
of trichloroethylene cometabolism, since the
lux
and
tod operons
are under the same regulation (toluene
dioxygenase catabolizes
trichloroethylene).
Bioluminescent reporters may have great potential for field use
applications, since they can provide on-line and nondestructive
analyses of gene expression as well as detection of chemical
contaminants.
The development of stable transposon insertions of
lux reporter
gene fusions into environmental isolates
expands the utility of
bioreporter strains for in situ sensing of gene
expression.
 |
ACKNOWLEDGMENTS |
We thank V. de Lorenzo for providing strain
SV17-1(
pir) and plasmid pUT and for helpful comments. We
are also grateful to D. T. Gibson, M. Rawlings, and C. Kado for
providing strains and plasmids and S. Ripp for editing the manuscript.
This research was supported by TVA grant TV-94002V and U.S. DOE grant
DE-FG05-94ER61870; Office of Health and Environmental Research and
graduate fellowship support was provided by the University of
Tennessee's Waste Management Research and Education Institute (B.A.).
Support was also received through Air Force grant F49620-89-C-0023 (S.K.).
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Center for
Environmental Biotechnology, 676 Dabney Hall, University of
Tennessee
Knoxville, Knoxville, TN 37996-1605. Phone: (423) 974-8080. Fax: (423) 974-8086. E-mail: sayler{at}utk.edu.
 |
REFERENCES |
| 1.
|
Applegate, B.,
C. Kelly,
L. Lackey,
J. McPherson,
S. Kehrmeyer,
F.-M. Menn,
P. Bienkowski, and G. S. Sayler.
1997.
Pseudomonas putida B2: a tod-lux bioluminescent reporter for toluene and trichloroethylene co-metabolism.
J. Ind. Microbiol.
18:4-9.
|
| 2.
|
Ausubel, F. M.,
R. Brent,
R. E. Kingston,
D. D. Moore,
J. G. Seidman,
J. A. Smith, and K. Struhl.
1989.
Current protocols in molecular biology.
John Wiley and Sons, New York, N.Y.
|
| 3.
|
Belkin, S.,
D. R. Smulski,
A. C. Vollmer,
T. K. Van Dyk, and R. A. LaRossa.
1996.
Oxidative stress detection with Escherichia coli harboring a katG'::lux fusion.
Appl. Environ. Microbiol.
62:2252-2256[Abstract].
|
| 4.
|
Brinkley, D.
1997.
Selecting a storage tank system.
Pollut. Eng.
29:76-79.
|
| 5.
|
Burlage, R. S.,
A. V. Palumbo,
A. Heitzer, and G. S. Sayler.
1994.
Bioluminescent reporter bacteria detect contaminants in soil samples.
Appl. Biochem. Biotechnol.
45/46:731-740.
|
| 6.
|
de Lorenzo, V.,
S. Fernandez,
M. Herrero,
U. Jakubik, and K. Timmis.
1993.
Engineering of alkyl- and haloaromatic-responsive gene expression with mini-transposons containing regulated promoters of biodegradative pathways of Pseudomonas.
Gene
130:41-46[Medline].
|
| 7.
|
Don, R. H.,
P. T. Cox,
B. J. Wainwright,
K. Baker, and J. S. Mattick.
1991.
`Touchdown' PCR to circumvent spurious priming during gene amplification.
Nucleic Acids Res.
19:4008[Free Full Text].
|
| 8.
|
Heitzer, A.,
O. F. Webb,
J. E. Thonnard, and G. S. Sayler.
1992.
Specific and quantitative assessment of naphthalene and salicylate bioavailability by using a bioluminescent catabolic reporter bacterium.
Appl. Environ. Microbiol.
58:1839-1846[Abstract/Free Full Text].
|
| 9.
|
Heitzer, A., and G. S. Sayler.
1993.
Monitoring the efficacy of bioremediation.
Trends Biotechnol.
11:334-343[Medline].
|
| 10.
|
Heitzer, A.,
K. Malachowsky,
J. Thonnard,
P. R. Bienkowski,
D. C. White, and G. S. Sayler.
1994.
Optical biosensor for environmental on-line monitoring of naphthalene and salicylate bioavailability with an immobilized bioluminescent catabolic reporter bacterium.
Appl. Environ. Microbiol.
60:1487-1494[Abstract/Free Full Text].
|
| 11.
|
Herrero, M.,
V. de Lorenzo, and K. N. Timmis.
1990.
Transposon vectors containing non-antibiotic resistance selection markers for cloning and stable chromosomal insertion of foreign genes in gram-negative bacteria.
J. Bacteriol.
172:6557-6567[Abstract/Free Full Text].
|
| 12.
|
Johnston, W.
1996.
Fate of Pseudomonas fluorescens 5RL and its reporter plasmid for naphthalene biodegradation in soil environments. Ph.D. dissertation
University of Tennessee, Knoxville.
|
| 13.
|
King, J. M. H.,
P. M. DiGrazia,
B. Applegate,
R. Burlage,
J. Sanseverino,
P. Dunbar,
F. Larimer, and G. S. Sayler.
1990.
Rapid, sensitive bioluminescence reporter technology for naphthalene exposure and biodegradation.
Science
249:778-781[Abstract/Free Full Text].
|
| 14.
|
Menn, F.-M.,
G. J. Zylstra, and D. T. Gibson.
1991.
Location and sequence of the todF gene encoding 2-hydroxy-6-oxohepta-2,4-dienote hydrolase in Pseudomonas putida F1.
Gene
104:91-94[Medline].
|
| 15.
|
National Research Council.
1993.
In-situ bioremediation when does it work?
National Academy Press, Washington, D.C.
|
| 16.
|
Promega.
1992.
Promega technical bulletin 009.
Promega, Madison, Wis.
|
| 17.
|
Rice, J. F.,
R. F. Fowler,
A. A. Arrage,
D. C. White, and G. S. Sayler.
1995.
Effects of external stimuli on environmental bacterial strains harboring an algD-lux bioluminescent reporter plasmid for the study of corrosive biofilms.
J. Ind. Microbiol.
15:318-328.
|
| 18.
|
Rogowsky, P. M.,
T. J. Close,
J. A. Chimera,
J. J. Shaw, and C. I. Kado.
1987.
Regulation of the vir genes of Agrobacterium tumefaciens plasmid pTiC58.
J. Bacteriol.
169:5101-5112[Abstract/Free Full Text].
|
| 19.
|
Sambrook, J.,
E. F. Fritsch, and T. Maniatis.
1989.
Molecular cloning: a laboratory manual, 2nd ed.
Cold Spring Harbor Laboratory Press, Cold Spring Harbor, N.Y.
|
| 20.
|
Selifonova, O.,
R. Burlage, and T. Barkay.
1993.
Bioluminescence sensors for detection of bioavailable Hg(II) in the environment.
Appl. Environ. Microbiol.
59:3083-3090[Abstract/Free Full Text].
|
| 21.
|
Selifonova, O. V., and R. W. Eaton.
1996.
Use of an ipb-lux fusion to study regulation of the isopropylbenzene catabolism operon of Pseudomonas putida RE204 and to detect hydrophobic pollutants in the environment.
Appl. Environ. Microbiol.
62:778-783[Abstract].
|
| 22.
|
Smith, J. H.,
J. C. Harper, and H. Jaber.
1981.
Analysis and environmental fate of Air Force distillate and high density fuels.
Air Force Engineering and Services Center, Tyndall Air Force Base, Fla.
|
| 23.
|
Stanier, R. Y.,
N. J. Palleroni, and M. Doudoroff.
1966.
The aerobic pseudomonads: a taxonomic study.
J. Gen. Microbiol.
41:159-271.
|
| 24.
|
Van Dyk, T. K.,
W. R. Majarian,
K. B. Konstantinov,
R. M. Young,
P. S. Dhurjati, and R. A. LaRossa.
1994.
Rapid and sensitive pollutant detection by induction of heat shock gene-bioluminescence gene fusions.
Appl. Environ. Microbiol.
60:1414-1420[Abstract/Free Full Text].
|
| 25.
|
Van Dyk, T. K.,
T. R. Reed,
A. C. Vollmer, and R. A. LaRossa.
1995.
Synergistic induction of the heat shock response in Escherichia coli by simultaneous treatment with chemical inducers.
J. Bacteriol.
177:6001-6004[Abstract/Free Full Text].
|
| 26.
|
Wallace, W. H.,
J. T. Fleming,
D. C. White, and G. S. Sayler.
1994.
An algD-lux bioluminescent reporter plasmid to monitor alginate production in biofilms.
Microb. Ecol.
27:225-239.
|
| 27.
|
Wang, Y.,
M. Rawlings,
D. T. Gibson,
D. Labbe,
H. Bergeron,
R. Brousseau, and P. C. K. Lau.
1995.
Identification of a membrane protein and a truncated LysR-type regulator associated with the toluene degradation pathway in Pseudomonas putida F1.
Mol. Gen. Genet.
246:570-579[Medline].
|
| 28.
|
Zylstra, G. J., and D. T. Gibson.
1989.
Toluene degradation by Pseudomonas putida F1. Nucleotide sequence of the todC1C2BADE genes and their expression in Escherichia coli.
J. Biol. Chem.
264:14940-14946[Abstract/Free Full Text].
|
Appl Environ Microbiol, July 1998, p. 2730-2735, Vol. 64, No. 7
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
du Plessis, E., Theron, J., Berger, E., Louw, M.
(2007). Evaluation of the Staphylococcus aureus Class C Nonspecific Acid Phosphatase (SapS) as a Reporter for Gene Expression and Protein Secretion in Gram-Negative and Gram-Positive Bacteria. Appl. Environ. Microbiol.
73: 7232-7239
[Abstract]
[Full Text]
-
Shinoda, Y., Sakai, Y., Uenishi, H., Uchihashi, Y., Hiraishi, A., Yukawa, H., Yurimoto, H., Kato, N.
(2004). Aerobic and Anaerobic Toluene Degradation by a Newly Isolated Denitrifying Bacterium, Thauera sp. Strain DNT-1. Appl. Environ. Microbiol.
70: 1385-1392
[Abstract]
[Full Text]
-
Haddix, P. L., Shaw, N. J., LeChevallier, M. W.
(2004). Characterization of Bioluminescent Derivatives of Assimilable Organic Carbon Test Bacteria. Appl. Environ. Microbiol.
70: 850-854
[Abstract]
[Full Text]
-
Werlen, C., Jaspers, M. C. M., van der Meer, J. R.
(2004). Measurement of Biologically Available Naphthalene in Gas and Aqueous Phases by Use of a Pseudomonas putida Biosensor. Appl. Environ. Microbiol.
70: 43-51
[Abstract]
[Full Text]
-
Yarwood, R. R., Rockhold, M. L., Niemet, M. R., Selker, J. S., Bottomley, P. J.
(2002). Noninvasive Quantitative Measurement of Bacterial Growth in Porous Media under Unsaturated-Flow Conditions. Appl. Environ. Microbiol.
68: 3597-3605
[Abstract]
[Full Text]
-
Stiner, L., Halverson, L. J.
(2002). Development and Characterization of a Green Fluorescent Protein-Based Bacterial Biosensor for Bioavailable Toluene and Related Compounds. Appl. Environ. Microbiol.
68: 1962-1971
[Abstract]
[Full Text]
-
Hay, A. G., Rice, J. F., Applegate, B. M., Bright, N. G., Sayler, G. S.
(2000). A Bioluminescent Whole-Cell Reporter for Detection of 2,4-Dichlorophenoxyacetic Acid and 2,4-Dichlorophenol in Soil. Appl. Environ. Microbiol.
66: 4589-4594
[Abstract]
[Full Text]
-
Skärfstad, E., O'Neill, E., Garmendia, J., Shingler, V.
(2000). Identification of an Effector Specificity Subregion within the Aromatic-Responsive Regulators DmpR and XylR by DNA Shuffling. J. Bacteriol.
182: 3008-3016
[Abstract]
[Full Text]
-
Neilson, J. W., Pierce, S. A., Maier, R. M.
(1999). Factors Influencing Expression of luxCDABE and nah Genes in Pseudomonas putida RB1353(NAH7, pUTK9) in Dynamic Systems. Appl. Environ. Microbiol.
65: 3473-3482
[Abstract]
[Full Text]
-
Shingleton, J. T., Applegate, B. M., Nagel, A. C., Bienkowski, P. R., Sayler, G. S.
(1998). Induction of the tod Operon by Trichloroethylene in Pseudomonas putida TVA8. Appl. Environ. Microbiol.
64: 5049-5052
[Abstract]
[Full Text]