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Applied and Environmental Microbiology, October 2005, p. 5951-5956, Vol. 71, No. 10
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.10.5951-5956.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
Metabolism of Carbaryl via 1,2-Dihydroxynaphthalene by Soil Isolates Pseudomonas sp. Strains C4, C5, and C6
Vandana P. Swetha and
Prashant S. Phale*
Biotechnology Group, School of Biosciences and Bioengineering, Indian Institute of Technology, Bombay, Powai, Mumbai 400 076, India
Received 9 March 2005/
Accepted 10 May 2005

ABSTRACT
Pseudomonas sp. strains C4, C5, and C6 utilize carbaryl as the
sole source of carbon and energy. Identification of 1-naphthol,
salicylate, and gentisate in the spent media; whole-cell O
2 uptake on 1-naphthol, 1,2-dihydroxynaphthalene, salicylaldehyde,
salicylate, and gentisate; and detection of key enzymes, viz,
carbaryl hydrolase, 1-naphthol hydroxylase, 1,2-dihydroxynaphthalene
dioxygenase, and gentisate dioxygenase, in the cell extract
suggest that carbaryl is metabolized via 1-naphthol, 1,2-dihydroxynaphthalene,
and gentisate. Here, we demonstrate 1-naphthol hydroxylase and
1,2-dihydroxynaphthalene dioxygenase activities in the cell
extracts of carbaryl-grown cells. 1-Naphthol hydroxylase is
present in the membrane-free cytosolic fraction, requires NAD(P)H
and flavin adenine dinucleotide, and has optimum activity in
the pH range 7.5 to 8.0. Carbaryl-degrading enzymes are inducible,
and maximum induction was observed with carbaryl. Based on these
results, the proposed metabolic pathway is carbaryl

1-naphthol

1,2-dihydroxynaphthalene

salicylaldehyde

salicylate

gentisate

maleylpyruvate.

INTRODUCTION
Carbamate insecticides, such as carbaryl (1-naphthyl-
N-methylcarbamate),
are highly toxic, have a wide range of activity, and comprise
a major portion of pesticides used in the agriculture industry.
Widespread and repeated use leads to pollution of soil and groundwater
(
5). The ester bond between
N-methylcarbamic acid and 1-naphthol
is responsible for carbaryl toxicity. Carbamates are competitive
inhibitors of neuronal nicotinic acetylcholine receptors and
acetylcholinesterase (
28).
N-Nitrosocarbamates and the 1-naphthol
that they generate are potent mutagens and are more toxic and
recalcitrant than carbaryl itself (
8,
22,
26,
27,
32). Carbamate
pesticides generally do not persist in the environment for a
long time. In aqueous solutions, carbaryl hydrolyzes to 1-naphthol,
methylamine, and CO
2 (
30). Bacteria capable of degrading carbamate
pesticides have been isolated from the soil (
3,
6,
7,
13,
16,
25). The first step in degradation is the hydrolysis of carbaryl
to 1-naphthol by carbaryl hydrolase, which has been purified
and characterized from various organisms (
3,
5,
10,
11,
20,
24). Depending on the strain, 1-naphthol is metabolized via
salicylate to either gentisate or catechol (
4,
7,
9,
16,
17).
It has been proposed that prior to ring cleavage, 1-naphthol
is hydroxylated either to 4-hydroxy-1-tetralone (
1), 3,4-dihydro-dihydroxy-1(2H)-naphthalenone
(
31), or 1,4-naphthoquinone (
25). Though 1-naphthol, salicylate,
and gentisate are well-established intermediates in carbaryl
degradation, the steps and enzymes responsible for the conversion
of 1-naphthol to salicylate have not been demonstrated so far.
In this study, we report isolation of three soil bacterium Pseudomonas sp. strains, C4, C5, and C6, utilizing carbaryl as the carbon source via 1-naphthol, salicylate, and gentisate. The aim of this study is to investigate the catabolic pathway and its regulation, with emphasis on the enzymes involved in the conversion of 1-naphthol to salicylate. Here, we report 1-naphthol hydroxylase and 1,2-dihydroxynaphthalene (1,2-DHN) dioxygenase activities in the cell extracts and induction patterns of key enzymes. Based on the results, we propose 1,2-dihydroxynaphthalene as a metabolic intermediate in carbaryl degradation.

MATERIALS AND METHODS
Chemicals.
Salicylate, gentisate, catechol, 1,2-dihydroxynaphthalene, flavin
adenine dinucleotide (FAD), NADH, NADPH, and NAD were purchased
from Sigma-Aldrich. 1- and 2-naphthol were purchased from Merck.
Carbaryl was a gift from Bayer Ltd. (India). Analysis of the
carbaryl gave a single spot by thin-layer chromatography (TLC)
and a single peak by gas chromatography (GC). All other chemicals
were of analytical grade and purchased locally.
Bacterial strains and culture conditions.
Using enrichment culture techniques, the three bacterial strains C4, C5, and C6 were isolated from soil contaminated with carbaryl. The cultures were grown in 150 ml minimal salt medium (MSM) in 500-ml baffled Erlenmeyer flasks at 30°C on a rotary shaker (200 rpm). For strains C4 and C5, the components of MSM per liter of distilled water were as follows: K2HPO4, 6 g; KH2PO4, 4.1 g; NH4NO3, 1 g; MgSO4 · 7H2O, 100 mg; MnSO4, 1 mg; CuSO4 · 5H2O, 1 mg; FeSO4 · 7H2O, 5 mg; H3BO3, 1 mg; CaCl2 · 2H2O, 5 mg; ZnSO4, 1 mg; and NaMoO4, 1 mg (pH 6.8). For strain C6, MSM composition was the same except that 8 g of K2HPO4 and 1 g of KH2PO4 (pH 7.4) were used. The medium was supplemented aseptically with appropriate hydrocarbon (0.1%) or glucose (0.25%) as the carbon source. Growth was monitored spectrophotometrically at 540 nm.
Isolation and identification of metabolites.
To isolate and identify the metabolites, spent medium was acidified to pH 2 with 2 N HCl and extracted with an equal volume of ethyl acetate. The organic phase was dried over anhydrous sodium sulfate, concentrated, and analyzed by TLC using hexane:chloroform:acetic acid 8:2:1 (vol/vol/vol) as a solvent system. Metabolites were identified by comparing Rf and UV fluorescence properties with authentic compounds. Metabolites were purified using preparative TLC and subjected to UV-visible-light spectroscopy (Perkin-Elmer Lambda UV35). GC-mass spectrometry (MS) analysis was carried out on a Hewlett-Packard G1800A mass spectrometer attached to a gas chromatograph. GC analysis was carried out using an HP1 column (30-m length; inlet temperature, 100°C, increased to 280°C at the rate of 10°C/min) and using helium (20 ml/min) as a carrier gas. The conditions for mass analysis were ionization at 70 eV, a mass range of 10 to 425 m/z, and a chamber temperature of 280°C.
Biotransformation and oxygen uptake studies.
Late-log-phase cells grown on respective hydrocarbons were harvested by centrifugation (12,000 x g), washed twice, suspended in MSM plus hydrocarbon (0.1%), and incubated at 30°C on a shaker for 3 to 4 h. The products were extracted from spent media and analyzed by TLC as described above. For O2 uptake studies, washed cells were suspended at 100 mg (wet weight) per ml of phosphate buffer (50 mM, pH 7.5). The respiration rates were measured at 30°C using an oxygraph (Hansatech, United Kingdom) fitted with Clark's type O2 electrode. The reaction mixture (2 ml) contained cells (4 mg, wet weight), a substrate (50 µM), and phosphate buffer (50 mM, pH 7.5). The rates were corrected for endogenous cell respiration and expressed as nmol O2 consumed · min1 · mg1 of cells.
Preparation of cell extract.
Late-log-phase cells (1 g) were suspended in 4 ml ice-cold phosphate buffer (50 mM, pH 7.5, K-PO4 buffer) and disrupted by sonication (Ultrasonic processor, model GE130) at 4°C with four cycles of 15 pulses each and an output at 11 W with a 3- to 4-min interval. Cell homogenate was centrifuged at 40,000 x g for 30 min at 4°C. The clear membrane-free supernatant obtained was referred as cell extract and used as the enzyme source.
Enzyme assays and bulk enzyme reaction.
Carbaryl hydrolase (CH) was monitored spectrophotometrically (Perkin Elmer; model Lambda 35) by measuring the rate of increase in absorbance at 322 nm due to the formation of 1-naphthol. The reaction mixture (1 ml) contained the substrate (100 µM), an appropriate amount of enzyme, and K-PO4 (50 mM, pH 7.5) buffer. The activity was calculated by using the molar extinction coefficient at 322 nm (
322) of 1-naphthol of 2,200 (M1 cm1) in K-PO4 buffer. 1-Naphthol hydroxylase (1-NH) was monitored by two methods. In an oxygraph assay, the reaction mixture (2 ml) contained K-PO4 buffer (50 mM, pH 7.5), the substrate (100 µM), FAD (6.25 µM), and NADH (100 µM). The reaction was started by the addition of enzyme. In the spectrophotometric assay, the disappearance of NADH at 340 nm was monitored. The assay mixture (1 ml) contained K-PO4 buffer, the substrate (100 µM), FAD (6.25 µM), NADH (100 µM), and enzyme. The enzyme activity was calculated using the molar
340 of NADH of 6,220 (M1 cm1). 1,2-Dihydroxynaphthalene dioxygenase (1,2-DHNO) (19, 23) was monitored using an oxygraph. The reaction mixture (2 ml) contained K-PO4 buffer (50 mM, pH 7.5), the substrate (100 µM), and an appropriate amount of enzyme. Gentisate dioxygenase (GDO) (29) and catechol dioxygenase (14, 21) were monitored spectrophotometrically in K-PO4 buffer (50 mM, pH 7.5). The reaction mixture contained buffer, the substrate (100 µM), and enzyme. Catechol dioxygenase was also monitored by an oxygraph under similar conditions. A time-dependent increase in the product formation was monitored spectrophotometrically for CH and GDO at defined intervals from 200 to 400 nm. All enzyme activities are expressed either as nmol of the substrate that disappeared, the product that appeared, or oxygen consumed · min1. Specific activities are reported as nmol · min1 · mg1 of protein. Protein estimation was carried out as described by Lowry et al. (18) using bovine serum albumin as a standard.
Bulk enzyme reactions (10 ml) were performed for CH, 1-NH, 1,2-DHNO, and salicylaldehyde dehydrogenase. Depending on the enzyme, the substrate (25 µM) and cofactor(s), namely, FAD (3.75 µM), NADH (50 µM), or NAD (50 µM), were added intermittently at 15, 30, and 60 min. The salicylaldehyde dehydrogenase reaction was carried out in glycine-KOH buffer (50 mM, pH 9.6) and NAD. Reaction mixtures were incubated at 30°C for 90 min, and products were extracted and analyzed as described earlier. To confirm that 1-NH belongs to an oxygenase group, a reaction was performed in an O2-free environment for 1 h at 30°C in a Thunberg tube. All reaction components were degassed, and anaerobic conditions were maintained by applying vacuum. The reaction was started by tipping NADH solution from the side arm of the tube into the main reaction chamber. The products were identified as described above.

RESULTS
Isolation and characterization of bacterial strains.
Bacterial strains capable of utilizing carbaryl as the sole
source of carbon and energy were isolated by a culture enrichment
technique from three garden soil samples (top 1 to 2 cm of the
soil layer; nursery, IIT B Campus, Mumbai, India) contaminated
with carbaryl. Soils (2 g) were inoculated in MSM plus carbaryl
(0.1%). Cultures were allowed to develop for the first 4 days
and were then transferred subsequently every 48 h. Pure cultures
were raised by inoculating a single colony from the 2YT plate
onto MSM plus carbaryl (0.1%). The three pure bacterial cultures
obtained were designated strains C4, C5, and C6. All strains
were gram-negative, motile, aerobic rods and catalase, oxidase,
urease, and citrate positive. Based on biochemical properties,
isolates were tentatively identified as
Pseudomonas sp. (
12)
and referred to as strains C4, C5, and C6. Besides carbaryl,
all strains utilize 1-naphthol, salicylate, and 4-hydroxybenzoate;
however, they failed to grow on naphthalene and 3-hydroxybenzoate.
The growth pattern of the strains on 0.1% carbaryl is shown
in Fig.
1.
Metabolism of carbaryl by strains C4, C5, and C6.
TLC analysis of the metabolites of early- to mid-log-phase (6
to 12 h) cultures showed four major spots with
Rf and UV fluorescence
properties similar to those of authentic carbaryl, 1-naphthol,
salicylate, and gentisate (Table
1). Metabolites corresponding
to 1,4-naphthoquinone and catechol could not be detected. Purified
metabolites were subjected to UV-visible spectroscopy and mass
analysis. Spectral properties and fragmentation patterns of
the metabolites were identical to those of the authentic compounds
(Table
1), confirmi ng the metabolites as carbaryl, 1-naphthol,
salicylate, and gentisate. The stationary-phase (18- to 24-h)
spent media showed a metabolite (
Rf of 0.79, sky-blue fluorescence)
corresponding to salicylate. To elucidate the metabolic sequence,
biotransformation experiments were performed, and results are
summarized in Table
2. When supplemented with carbaryl, metabolites
with
Rf and fluorescence properties similar to those of authentic
carbaryl, 1-naphthol, salicylate, and gentisate were detected.
With salicylaldehyde, spots corresponding to salicylate and
gentisate were observed; however, the cells failed to transform
1,4-naphthoquinone (Table
2).
Various metabolic studies with strains C4, C5, and C6 showed
similar results; hence, data pertaining only to strain C4 are
presented. To elucidate the steps involved in the conversion
of 1-naphthol to salicylaldehyde, whole-cell O
2 uptake rates,
enzyme activities, and products of bulk enzyme reactions were
monitored. Carbaryl-grown C4 cells showed good O
2 uptake on
carbaryl, 1-naphthol, 1,2-DHN, salicylaldehyde, salicylate,
and gentisate; however, they failed to respire on 1,4-naphthoquinone
(Table
3). Salicylate-grown cells showed comparable levels of
O
2 uptake on salicylate and gentisate but significantly low
respiration on other probable intermediates. Glucose-grown cells
showed very low respiration (<0.1 nmol). Carbaryl-grown cells
showed CH, 1-NH, 1,2-DHNO, and GDO activities (Table
4). Salicylate-grown
cells showed comparable activities of GDO but significantly
low activities of CH and 1-NH. The activity of 1,2-DHNO was
two- to threefold lower than that of carbaryl-grown cells. We
failed to detect salicylate-5-hydroxyalse activity. Enzyme activities
from glucose-grown cells were significantly low (Table
4). Growth
versus specific activity showed the maximum activity of CH,
1-NH, and GDO during the late-log phase of growth (Fig.
2).
Conversion of the substrate to product was monitored by time-dependent
spectral changes during the enzyme reaction and identifying
the products of bulk enzyme reactions using carbaryl, 1-naphthol,
1,2-DHN, and salicylaldehyde as substrates. Time-dependent spectral
changes for CH showed a decrease in carbaryl at 280 nm, with
a concomitant appearance of 1-naphthol at 322 nm and an isobestic
point at 287 nm (Fig.
3). GDO showed an increase in absorbance
at 330 nm due to the conversion of gentisate (320 nm) to maleylpyruvate
(330 nm) (Fig.
3B). The bulk enzyme reaction with carbaryl gave
1-naphthol, salicylaldehyde, and salicylate (Table
2). With
either 1-naphthol, 1,2-DHN, or salicylaldehyde as the substrate,
salicylaldehyde and salicylate were detected as reaction products.
None of the bulk enzyme reactions showed spots corresponding
to gentisate or catechol formation (Table
2).
We demonstrated the presence of 1-NH and 1,2-DHNO activities
in the cell extracts of carbaryl-degrading strains. 1,2-DHNO
is purified and characterized from naphthalene-degrading organisms
(
15,
19,
23); however, 1-NH has not been characterized. We studied
1-NH for its cofactor and O
2 requirement. The enzyme showed
good activity with FAD and NADH. When NADPH and FAD were used
as cofactors, a 20 to 30% increase in activity was observed
(Table
5). 1-NH showed maximum activity in the pH range 7.5
to 8.0. Heat denaturation (enzyme in a boiling water bath for
10 min) or trichloroacetic acid precipitation failed to show
activity and product formation by TLC (Table
5). Under aerobic
conditions in the presence of NADH and FAD, 1-NH showed conversion
of 1-naphthol to salicylate (Table
2). However, under anaerobic
conditions, we failed to detect salicylate by TLC (Table
5),
suggesting that the enzyme requires O
2 as one of the substrates.
The enzyme was inducible and showed maximum activity from carbaryl
compared to its activity in salicylate- or glucose-grown cells
(Table
4).

DISCUSSION
Pseudomonas sp. strains C4, C5, and C6 utilize carbaryl. Compared
to reported organisms, isolated strains degrade carbaryl at
very high concentrations (1% so far tested). Based on various
metabolic studies (Tables
1 to
4), the proposed metabolic pathway
for carbaryl degradation is shown in Fig.
4. Degradation of
carbaryl via 1-naphthol, salicylate, and gentisate is well documented
(
4,
7,
9); however, the metabolic steps and enzymes involved
in the conversion of 1-naphthol to salicylate have not been
reported so far. A few 1-naphthol-degrading microorganisms have
been reported to hydroxylate 1-naphthol to 4-hydroxy-1-tetralone
(
1), 3,4-dihydro-dihydroxy-1(2H)-naphthalenone (
31), or 1,4-naphthoquinone
(
25). However, further metabolism of these hydroxylated intermediates
is not clearly understood. Conversion of carbaryl, 1-naphthol,
and 1,2-DHN to salicylaldehyde and salicylate (Table
2), O
2 uptake on 1,2-DHN (Table
3), detection of 1-NH and 1,2-DHNO
(Table
4), and the inability to transform 1,4-naphthoquinone
strongly support 1,2-DHN being an intermediate in the carbaryl
metabolic pathway. We could detect salicylate but failed to
observe 1,2-DHN as an intermediate in bulk enzyme reactions
with carbaryl and 1-naphthol (Table
2). This could be due to
the presence of enzymes, viz, 1,2-DHNO, 2-hydroxybenzalpyruvate
aldolase, and SalDH, responsible for the conversion of 1,2-DHN
to salicylate. Similar enzyme reactions are reported for naphthalene
degradation (
33). Interestingly, none of the three carbaryl-degrading
strains utilize naphthalene as the carbon source. This could
be due to the lack of a ring hydroxylting naphthalene dioxygenase,
the first enzyme of the pathway. 1,2-DHNO is an extradiol ring-cleaving
enzyme. Besides 1,2-DHN, it catalyzes a reaction with 4-methylcatechol,
yielding 2-hydroxy 5-methyl
cis,
cis-mucconic semialdehyde (382
nm) (
2,
19,
23). Cell extracts of the three isolates showed
increases in the absorption at 382 nm with 4-methylcatechol
as a substrate, suggesting the presence of an extradiol ring-cleaving
1,2-DHNO enzyme. The cells metabolize salicylate to gentisate,
as evident from biotransformation and whole-cell O
2 uptake studies
(Table
2 and
3); however, we failed to monitor salicylate-5-hydroxylase
activity in the cell extracts. This could be due to the complex
and unstable nature of the enzyme, as reported for several other
hydroxylases.
Involvement of CH and GDO in the carbaryl degradation is well
documented (
4,
7,
9). However, to the best of our knowledge,
the activity of 1-naphthol oxygenase has been demonstrated at
the whole-cell level by O
2 uptake studies with the carbaryl-degrading
organisms
Pseudomonas sp.,
Rhodococcus sp. (
16), and
Micrococcus sp. (
7). The cofactor requirement and oxygenase nature of the
enzyme have not been investigated so far. Here, we demonstrate
for the first time the activity of 1-NH in the cell extract
of carbaryl-degrading strains. Initial characterization indicates
that 1-NH is oxygenase and requires FAD and a reducing cofactor
(NADH or NADPH) (Table
5), suggesting that the enzyme belongs
to a flavin monooxygenase group of an oxidoreductase class of
enzymes. The enzymes of the carbaryl metabolic pathway are inducible,
as carbaryl-grown cells showed maximum activities compared to
those of glucose-grown cells. Carbon source-dependent O
2 uptake
and enzyme activity studies (Tables
3 and
4) suggest that the
carbaryl pathway is probably organized into upper and lower
pathways. The upper pathway metabolizes carbaryl to salicylate,
while the lower pathway converts salicylate to tricarboxylic
acid cycle intermediates through gentisate. We propose that
carbaryl induces both upper and lower pathway enzymes while
salicylate induces lower pathway enzymes only.
In conclusion, Pseudomonas sp. strains C4, C5, and C6 utilize carbaryl via 1-naphthol, 1,2-DHN, salicylate, and gentisate. The detection of 1-NH and 1,2-DHNO confirms the carbaryl metabolic pathway via 1,2-DHN. The ability to degrade high concentrations of carbaryl makes these strains ideal candidates for their application in pesticide degradation/remediation at the contaminated sites.

ACKNOWLEDGMENTS
We thank Vidhu Mathur for helping with a few supporting experiments
with strain C5 and Prabin Majhi and Aditya Basu for comments
and constructive discussion.
P.S.P. thanks the Department of Biotechnology, Government of India, for the research grant and RSIC, IIT-B, for the GC-MS facility.

FOOTNOTES
* Corresponding author. Mailing address: Biotechnology Group, School of Biosciences and Bioengineering, Indian Institute of Technology, Bombay, Powai, Mumbai 400 076, India. Phone: 91-22-2576 7836. Fax: 91-22-2572 3480. E-mail:
pphale{at}iitb.ac.in.


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Applied and Environmental Microbiology, October 2005, p. 5951-5956, Vol. 71, No. 10
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