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Genetic and Biochemical Characterization of Indole Biodegradation in 1
Acinetobacter sp. Strain O153 2
3
Mikas Sadauskas#, Justas Vaitekūnas, Renata Gasparavičiūtė, Rolandas Meškys 4
5
Department of Molecular Microbiology and Biotechnology, Institute of 6
Biochemistry, Life Sciences Center, Vilnius University, Sauletekio al. 7, Vilnius, LT-7
10257, Lithuania. 8
E-mail addresses: 9
Mikas Sadauskas – [email protected] 10
Justas Vaitekūnas – [email protected] 11
Renata Gasparavičiūtė – [email protected] 12
Rolandas Meškys – [email protected] 13
14
Running Head: Indole biodegradation in Acinetobacter sp. O153 15
Keywords: indole, biodegradation, bacterial metabolism, Acinetobacter, bacterial 16
signalling, cofactor-independent oxygenases 17
18
#Address correspondence to Mikas Sadauskas, Sauletekio al. 7, Vilnius, LT-19
10257, Lithuania, +37062230055, [email protected] 20
AEM Accepted Manuscript Posted Online 4 August 2017Appl. Environ. Microbiol. doi:10.1128/AEM.01453-17Copyright © 2017 American Society for Microbiology. All Rights Reserved.
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ABSTRACT 21
Indole is a molecule of considerable biochemical significance, acting as both an 22
interspecies signal molecule and a building block of biological elements. Bacterial indole 23
degradation has been demonstrated for a number of cases; however, very little is known 24
about genes and proteins involved in this process. This study reports the cloning and 25
initial functional characterization of genes (iif and ant cluster), responsible for indole 26
biodegradation in Acinetobacter sp. strain O153. Catabolic cascade was reconstituted in 27
vitro with recombinant proteins and each protein was assigned an enzymatic function. 28
Degradation starts with oxidation, mediated by IifC and IifD flavin-dependent two 29
component oxygenase system. Formation of indigo is prevented by IifB and the final 30
product – anthranilic acid – is formed by IifA, an enzyme which is both structurally and 31
functionally comparable to cofactor-independent oxygenases. Moreover, the iif cluster 32
was identified in the genomes of wide range of bacteria, suggesting the potential 33
widespread of Iif-mediated indole degradation. This work provides novel insights into 34
genetic background of microbial indole biodegradation. 35
36
IMPORTANCE 37
The key finding of this research is identification of genes, responsible for 38
microbial biodegradation of indole, a toxic N-heterocyclic compound. A large amount of 39
indole is present in urban waste water and sewage sludge raising a demand for efficient 40
and eco-friendly means to eliminate this pollutant. A common strategy of oxidizing 41
indole to indigo has a major drawback of producing insoluble material. Genes and 42
proteins of Acinetobacter sp. strain O153 (DSM 103907) reported here pave the way for 43
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effective and indigo-free indole removal. In addition, this work suggests possible novel 44
means of indole-mediated bacterial interactions and provides the basis for future research 45
on indole metabolism. 46
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INTRODUCTION 47
48
Indole is an N-heterocyclic aromatic compound derived mainly by TnaA 49
tryptophanase from L-tryptophan in Escherichia coli (1) and is widely found in natural 50
environments. Indole acts as cell-to-cell signalling molecule that regulates the expression 51
of several virulence genes (2-4), promotes biofilm formation (5-7) and mediates complex 52
predator-prey interactions (8, 9). At high concentrations indole and its derivatives exhibit 53
toxic activity to both prokaryotic cells and animals and are even considered mutagens 54
(10). Toxic indole concentration reportedly varies for different microorganisms in the 55
range of 0.5–5 mM (11). The main mechanisms of indole toxicity are reported to be an 56
alteration of membrane potential with subsequent inhibition of cell division (12), 57
depletion of ATP levels (13) and an inhibition of acyl-homoserine lactone (AHL)-based 58
quorum-sensing by regulator misfolding (14). 59
In order to utilize aromatic compounds as energy source, microorganisms have to 60
cope with the problem of high resonance energy that stabilizes the aromatic ring system 61
(15). A common strategy is the use of oxygenases and O2, which itself requires the 62
activation of dioxygen. In addition to being thermodynamically unfavourable, reactions 63
between dioxygen (triple state) and most of the organic compounds (singlet state) are not 64
possible due to a spin barrier (16). Diverse elements, including transition metals (iron, 65
manganese, copper) or organic cofactors (flavins, pterin) are used extensively by 66
oxygenases to form a superoxide, a reactive singlet state form of dioxygen (17). As 67
nature never ceases to amaze, a remarkable group of cofactor-independent oxygenases 68
have been described which require neither an organic cofactor nor a metal to catalyse the 69
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incorporation of (di)oxygen into a single molecule of organic substrate (18, 19). 70
Establishment of the catalytic mechanisms for this group of enzymes provides interesting 71
mechanistic insights into substrate-assisted oxygen activation (20, 21). 72
To defend against its toxicity, indole-encountering bacteria have established 73
enzymatic detoxification systems, notably the oxidation of indole to insoluble non-toxic 74
indigoid pigments (22, 23) and biodegradation mechanisms (24, 25). A number of indole 75
degrading bacterial microorganisms (26-28) as well as bacterial consortia (29) were 76
reported, but no genetic background in these reports have been specified. Several 77
possible intermediates in bacterial indole degradation are also known, but proteins with 78
specific enzyme activities that drive the degradation cascade have not been identified in 79
this context. In this paper, the identification of indole degradation gene cluster (iif) in 80
indole-degrading Acinetobacter sp. strain O153 is reported. Catabolic pathway was 81
reconstituted in vitro with the recombinant proteins encoded by the iif genes and the 82
function of each enzyme was identified by analysing the reaction products. 83
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MATERIALS AND METHODS 84
Bacterial strains, chemicals and standard techniques 85
Escherichia coli DH5α and BL21(DE3) strains were used as cloning and protein 86
expression hosts, respectively. Transformation of bacteria by electroporation was 87
performed as described previously (31). E. coli strains with plasmids were cultivated in 88
LB medium supplemented with corresponding antibiotic (ampicillin, 100 μg/ml or 89
kanamycin, 50 μg/ml). Plasmid DNA was isolated using ZR Plasmid Miniprep Classic 90
kit (ZYMO Research). Indole, isatin and anthranilic acid were purchased from Sigma-91
Aldrich, 5-bromoindoline was obtained from Combi-Blocks Inc. All other chemicals 92
used in this study were of analytical grade. All media and reagent solutions were 93
prepared with Milli-Q water (Merck Millipore). 94
Isolation and identification of indole-oxidizing bacterial strain 95
Indole-oxidizing microorganisms were isolated from the intestine of Orconectes 96
limosus. Crustacean samples were collected at Lake Ruzis, Alytus district, Lithuania. 97
Intestines were suspended in 0.9 % NaCl solution and plated on Luria-Bertani (LB) agar 98
plates supplemented with 1 mM 5-bromoindoline. Following an overnight incubation at 99
30 °C purple pigment-forming colonies were isolated and maintained as pure cultures. 100
16S rRNA gene of isolate strain was amplified with universal bacterial primers 27F and 101
1492R (Table 1) according to (30) and sequenced. Phylogenetic analysis was performed 102
with blastn algorithm (https://blast.ncbi.nlm.nih.gov, 31) against the database of 16S 103
ribosomal RNA sequences. 104
Table 1 105
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Genomic DNA of strain O153 was extracted as described (32), digested with 106
HindIII (ThermoFisher Scientific) to obtain 5–20 kb DNA fragments, which were cloned 107
into pUC19 (ThermoFisher Scientific). Resulting library was transformed into E. coli 108
DH5α, cells were plated on LB agar with 5-bromoindoline, incubated overnight at 37 °C 109
and screened for purple pigment-producing colonies. 110
Whole-cell bioconversion assays and growth conditions 111
For growth kinetics experiments, an overnight culture of strain O153 grown in 112
LB medium was centrifuged, washed with potassium phosphate buffer and re-suspended 113
in 0.9 % NaCl. Cells were diluted in fresh M9 media with different carbon (5 mM 114
succinate or 1 mM indole) and nitrogen (5 g/L NH4Cl or different concentrations of 115
indole) sources. Cell suspensions were incubated at 30 °C with shaking (180 RPM). 116
Growth was monitored by measuring the absorbance at 600 nm. At least three 117
independent experiments were performed. 118
For whole-cell experiments, an overnight culture of Acinetobacer sp. O153 was 119
grown in M9 medium (3.5 g/L Na2HPO4, 1.5 g/L KH2PO4, 2.5 g/L NaCl, 0.2 g/L 120
MgSO4, 0.01 g/L CaCl2) supplemented with 5 mM succinate and 1 mM indole (induced 121
cells) or succinate and 5 g/L NH4Cl (uninduced cells). Cells were pelleted by 122
centrifugation, washed with 20 mM potassium phosphate buffer, pH 7.8, and re-123
suspended in M9 minimal medium to a final concentration of OD600 = 0.8 in a volume of 124
1 ml containing 1mM of appropriate substrate. Cells were incubated at 30 °C with 125
shaking. The sample without cells was used as an evaporation (negative) control. 126
Absorbance spectra of the cell-free supernatants were recorded every hour to monitor 127
substrate consumption. 128
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Cloning, expression and purification of proteins involved in indole 129
degradation 130
All reagents used for the cloning experiments were purchased from ThermoFisher 131
Scientific (Lithuania). Target genes were amplified by PCR in Mastercycler ep Gradient 132
S (Eppendorf) using the primer pairs listed in Table 1, Maxima Hot Start Green PCR 133
Master Mix and a colony of Acinetobacter sp. O153 cells. PCR conditions were as 134
follows: initial denaturation at 98 °C for 4 min, followed by 30 cycles of denaturation at 135
98 °C for 30s, annealing at varying temperatures for 30s, elongation at 72 °C for 90s and 136
final elongation at 72 °C for 10 min. DNA fragments obtained were cloned into 137
pTZ57R/T vector according to manufacturer’s protocol and sequenced. Resulting 138
plasmids were digested with restriction endonucleases that recognize the primer-139
introduced sequences (Table 1) and fragments were ligated into pET28-c(+) (Novagen) 140
previously digested with the same restriction endonucleases. Expression plasmids with 141
N-terminally encoded 6xHis tag were transformed into E. coli BL21 (DE3) for protein 142
expression. Protein expression and purification were carried out as described earlier (33). 143
Protein concentration was determined with Coomassie Protein Assay Kit (Pierce) using 144
bovine serum albumin as the standard. 145
Enzyme assays and detection of reaction products 146
Flavin reductase activity of the purified IifD protein was determined from the 147
decrease of the absorbance at 340 nm due to oxidation of NADH or NADPH (ε340 = 6220 148
M-1
cm-1
), using spectrophotometer and was performed at room temperature. A total 149
reaction volume of 1 ml contained 50 mM Tris-HCl, pH 7.5, variable amounts of NADH 150
or NADPH and flavins (FAD, FMN or riboflavin). Kinetic parameters for NADH and 151
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NADPH were determined using constant concentration of FAD (20 μM) and varying 152
concentrations of NAD(P)H (5–200 μM). In addition, varying concentrations of flavin 153
(1–40 μM) and a constant concentration of NADH (200 μM) were used for analysis of 154
the enzyme kinetics. Reactions were initiated by adding 0.3 μg of the enzyme. One unit 155
(U) of enzyme activity was defined as the amount of enzyme catalysing the oxidation of 156
1 μmol of NAD(P)H per minute. 157
Indole oxidation activity of IifC was determined as a function of indigo formation 158
in reaction mixture. An initial indole oxidation rather than spontaneous dimerization was 159
assumed to be a rate-limiting step. A typical reaction contained 50 mM Tris-HCl, pH 7.5, 160
100 μM flavin, 250 μM NADH or NADPH, varying concentrations of indole (10–500 161
μM) and was initiated by adding 3 μg of IifD as well as 3 μg of IifC. Reactions were 162
incubated at room temperature for 15 min and indigo particles were pelleted by 163
centrifugation at 16000 g for 5 min. Precipitant was dissolved in 100 μl of 164
dimethylformamide (DMF), dissolving was facilitated by incubating the mixture at 37 °C 165
for 15 min. Indigo concentration was determined as described (34), using a molar 166
absorptivity coefficient of ε620 = 14000 M-1
cm-1
. One unit of enzyme activity was 167
defined as the amount catalysing the formation of 1 μmol of indigo per minute. 168
Oxygenase activity of IifA was measured from the increase of absorbance at 315 169
nm (formation of anthranilic acid from 3-hydroxyindolin-2-one). A typical assay 170
contained varying concentrations (10–300 μM) of 3-hydroxyindolin-2-one (synthesized 171
as described below) in 50 mM Tris-HCl, pH 7.5, air-saturated (oxygen concentration ~ 172
250 μM) buffer. Reactions were initiated by adding 3 μg of IifA and the concentration of 173
anthranilic acid formed was determined using a molar absorptivity coefficient of ε315 = 174
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1600 M-1
cm-1
(calculated using Beer-Lambert Law and data on the absorbance of 0.05-5 175
mM anthranilic acid in 50 mM Tris-HCl, pH 7.5. One unit of enzyme activity was 176
defined as the amount catalysing the formation of 1 μmol of anthranilic acid per minute 177
at given conditions. All kinetic parameters were determined by fitting the data to 178
Lineweaver-Burk (double-reciprocal) plots and performing a linear regression. All 179
kinetic experiments were performed in duplicate and average means were derived. 180
Enzymatic conversion of indole by Iif proteins was analysed by monitoring 181
substrate consumption and formation of corresponding reaction products in in vitro 182
reactions. Under standard conditions, a total volume of 250 μl reaction mixture contained 183
50 mM Tris-HCl, pH 7.5, 50 μM flavin cofactor, 100 μM NAD(P)H, 1 mM indole and 3 184
μg of each purified Iif protein. The combinations of proteins tested were as depicted in 185
Fig. 4. Reaction mixtures were incubated at room temperature for 1 hour with shaking 186
(700 rpm, Eppendorf Thermomixer Comfort). Substrate consumption and formation of 187
products were analysed spectrophotometrically in PowerWave XS plate reader (BioTek 188
Instruments Inc.) or mixed with equal volume of acetonitrile, centrifuged at 16000 g for 189
5 min and analysed by HPLC/MS. 190
Oxygen consumption and anaerobic assay 191
The measurement of oxygen consumption was performed with a homemade 192
computer-assisted membrane oxygen electrode and 10.0 ml glass cell. The concentration 193
of oxygen was assumed to be 0.25 mM in air-saturated 50 mM Tris-HCl, pH 7.5, buffer 194
solution at 25 °C. Different concentrations of 3-hydroxyindolin-2-one (82, 136, and 273 195
μM) were used and reactions were initiated by adding 3 μg of IifA. 196
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Anaerobic conditions were generated in an air-restricted cell by argon bubbling of 197
Tris-HCl buffer solution, pH 7.5, at 25 °C for 10 min. Prior to bubbling, traces of oxygen 198
were eliminated from argon gas by passing through the solution of alkaline pyrogallol 199
(benzene-1,2,3-triol). 200
HPLC-MS 201
HPLC/MS analyses were performed using high performance liquid 202
chromatography system (CBM-20A controller, two LC-2020AD pumps, SIL-30AC auto 203
sampler and CTO-20AC column oven; Shimadzu, Japan) equipped with photodiode 204
array (PDA) detector (Shimadzu, Japan) and mass spectrometer (LCMS-2020, 205
Shimadzu, Japan) equipped with an ESI source. The chromatographic separation was 206
conducted using a YMC Pack Pro column, 3 × 150 mm (YMC, Japan) at 40 °C and a 207
mobile phase that consisted of 0.1% formic acid water solution (solvent A), and 208
acetonitrile (solvent B) delivered in the 0 → 60% gradient elution mode. Mass scans 209
were measured from m/z 10 up to m/z 700, at 350 °C interface temperature, 250 °C DL 210
temperature, ±4,500 V interface voltage, neutral DL/Qarray, using N2 as nebulizing and 211
drying gas. Mass spectrometry data was acquired in both positive and negative ionization 212
mode. The data was analysed using the LabSolutions LCMS software. 213
Chemical synthesis of 3-hydroxyindolin-2-one 214
Reduction of isatin to 3-hydroxyindolin-2-one was performed according to (35). 215
Isatin (1.5 mmol) was added in small portions to a stirred suspension of sodium 216
borohydride (0.75 mmol, 2 eq) in 20 mL of a 1:1 water/ethanol mixture at room 217
temperature. The mixture was vigorously stirred until the suspension became colourless 218
(about 10 min). The mixture was extracted with chloroform (3 x 10 mL). The combined 219
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organic extracts were dried (MgSO4) and the solvent evaporated under reduced pressure. 220
The residual material was dissolved in 5 mL deionized water and was purified by reverse 221
phase chromatography (12 g C-18 cartridge) to separate the 3-hydroxyindolin-2-one 222
from the pigments formed during the extraction and evaporation procedures. Prior the 223
purification the column was equilibrated with water. A mobile phase that consisted of 224
water and methanol was delivered in the gradient elution mode. The collected fractions 225
were analysed by HPLC/MS. The fractions containing a pure product were combined 226
and the solvent was removed under reduced pressure. 227
The structures of the bioconversion products were determined using 1H nuclear 228
magnetic resonance (NMR) and 13
C NMR. 1H NMR spectra were recorded in DMSO-d6 229
or CDCl3 on Bruker Ascend 400, 400 MHz, and 13
C NMR were recorded on Bruker 230
Ascend 400, 100 MHz. All products were dissolved in deuterated dimethyl sulfoxide. 231
Spectra were calibrated with respect to the solvent signal (CDCl3, 1H δ =7.26,
13C δ = 232
77.2; DMSO-d6, 1H δ = 2.50,
13C δ = 39.5). 233
Sequence alignments and structure modelling 234
Genome sequences containing genes with high sequence similarity to iif genes 235
were identified with blastn suite (https://blast.ncbi.nlm.nih.gov) by using each of the five 236
iif genes individually. Hits with E-value less than 5e-10 were pooled and used as 237
database in MultiGeneBlast (36). Homology search was performed using an iif locus of 238
A. guillouiae genomic DNA (ranging from nucleotide 1661941 to 1671563) as query 239
with default parameters except that maximum distance between genes in locus was 240
increased to 100 kb. Positive variants were manually proofread with respect to structural 241
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organization of iif and ant genes as well as possible orientation in separate DNA 242
fragments. 243
The model of tertiary structures of N-terminal (amino acids 1–233) and C-244
terminal (amino acids 252–374) domains of IifA protein was obtained using I-TASSER 245
platform (http://zhanglab.ccmb.med.umich.edu/I-TASSER) (37). Structures of 246
dienolactone hydrolases (PDB 1DIN and 1ZI8) were used as threading templates for 247
modelling of N-terminal domain and structures of putative polyketide cyclases (PDB 248
4LGQ and 3F9S) – as templates for C-terminal domain. Models with the highest C-score 249
(1.42 and 0.26 for N- and C-terminal domains, respectively) were selected for further 250
structural analysis and comparison with structures of cofactor-independent oxygenases. 251
Nucleotide sequence and bacterial strain accession numbers 252
Sequence data described in this paper have been submitted to GenBank database 253
under the following accession numbers: 16S rDNA of strain Acinetobacter sp. O153 - 254
KX955254, iifA - KX955255, iifB - KX955256, iifC - KX955257, iifD - KX955258, iifE 255
- KY700688. Strain Acinetobacter sp. O153 has been deposited to DSMZ under 256
accession number DSM 103907. 257
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RESULTS 258
259
Screening for indole-degrading bacteria 260
Numerous microbiome samples obtained from invertebrates as well as soil 261
samples were used for the screening of indole-degrading bacteria as these environments 262
potentially contain indole. Due to the known toxicity of indole, this compound was not 263
used as a sole carbon source for selection of indole-mineralizing bacteria in this study. 264
Instead, a derivative of indole was hypothesized to form a dead-end pigment in the 265
indole-degrading microorganisms. Such strategy enabled the selection of desirable 266
bacteria on the nutrient rich media supplemented with chromogenic substrate 5-267
bromoindoline. 268
A bacterial colony, isolated from the intestine of crustacean Orconectes limosus, 269
which is a widespread invasive species in Europe, was able to convert 5-bromoindoline 270
to insoluble indigoid pigment. The sequence of 16S rRNA gene of this strain showed 99 271
% similarity to 16S rRNA gene sequence of Acinetobacter guillouiae strain NBRC 272
110550 and therefore strain O153 was designated as Acinetobacter sp. O153. Notably, 273
this strain did not produce indigoid pigment when grown on LB agar plates with indole 274
(data not shown). 275
To test the ability of Acinetobacter sp. O153 to assimilate indole as carbon (C) 276
and/or nitrogen (N) source, cells of the strain O153 were cultured in minimal medium 277
with succinate or indole as C sources and NH4Cl or indole as N sources. No growth was 278
observed with indole as the only C source or the only source for both N and C (Fig. 1A). 279
However, moderate growth (up to 0.3 OD600 in 12 h) was achieved with indole (1 mM) 280
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as N source and succinate as sole carbon source. While this effect was observed with 281
indole concentrations ranging from 0.5 mM to 1.5 mM, no growth was recorded with 282
concentrations 0.1 mM and 2 mM (Fig. 1B), which were most likely insufficient and 283
toxic, respectively. 284
Figure 1 285
Whole-cell experiments were performed to determine whether the expression of 286
enzymes involved in indole metabolism are inducible or constitutive. After overnight 287
growth in a minimal medium with succinate and either with or without indole, cells of 288
the strain O153 were re-suspended in buffer containing 1 mM indole. Indole was 289
transformed immediately by indole-induced O153 cells (Fig 2). In contrast, uninduced 290
cells consumed indole significantly slower and with a lag period. These results indicated 291
that indole mineralization (biodegradation) was an inducible process. 292
Figure 2 293
Identification and characterization of genes involved in indole degradation 294
Screening of Acinetobacter sp. O153 genomic library using E. coli DH5α as a 295
host strain revealed one clone (O153H14) which was able to convert 5-bromoindoline to 296
a purple pigment, a characteristic feature of the wild-type strain O153. The clone 297
O153H14 was bearing a pUC19 vector with 12-kb genomic DNA fragment. The DNA 298
sequencing of this fragment revealed the presence of nine open reading frames (ORFs, 299
depicted in Fig. 3). Bioinformatic analysis of ORFs in this fragment using NCBI’s blastn 300
algorithm and Conserved Domain Database (38) allowed the identification of two 301
different sets of genes (Table 2). The iif cluster comprised the first set and the second set 302
encoded a multi-subunit anthranilate dioxygenase. The two sets were separated by a 303
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putative araC transcription regulator. Analysis of iif cluster suggested both high 304
sequence identity and structural similarity to iif genes, which were shown to comprise a 305
functional operon induced by indole in A. baumannii ATCC19606 (23). Hence, genes 306
and proteins presented here were given the same nomenclature and were called Iif 307
homologues. Five genes of the iif operon encoded putative enzymes as described by 308
conserved domain analysis: iifA – dienolactone hydrolase family protein, iifB – short-309
chain dehydrogenase, iifC – oxygenase, iifD – flavin reductase, iifE – putative phenol 310
degradation protein. The ant cluster was composed of three genes encoding different 311
subunits of the anthranilate dioxygenase and appeared to be of typical composition: antA 312
and antB encoded large and small subunits of anthranilate dioxygenase oxygenase 313
component, respectively, while antC coded for the electron transfer component protein. 314
Table 2 315
Distribution of iif homologs among bacterial genomes 316
The prevalence of iif operon genes as well as genes of anthranilate dioxygenase 317
among available microbial genomes was analysed. Mainly organisms from genus 318
Acinetobacter, Pseudomonas and Burkholderia were identified, including some 319
notoriously pathogenic strains of A. baumannii, P. fluorescens and P. syringiae (Fig. 3). 320
Spatial separation of the two operons was found to be a common indication outside 321
genus Acinetobacter, stretching to as long as 200 kb (B. cepacia ATCC 25416 and 322
Alcaligenes faecalis ZD02) or even separate replicons (B. contaminans MS14, 323
Cupriavidus metallidurans CH34 and C. basilensis 4G11). Also, aberrant composition of 324
the iif operon was predicted in several cases with four genomes (P. fluorescens NCIMB 325
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11764, C. metallidurans CH34, C. basilensis 4G11 and Ralstonia solanacearum PSI07) 326
lacking the iifE homolog. 327
Figure 3 328
Enzyme activity of recombinant Iif proteins 329
To identify the enzymatic functions of Iif proteins, iifA, iifB, iifC, iifD and iifE 330
genes were expressed in E. coli BL21 (DE3) with N-terminal His-tag, purified and tested 331
for activity towards indole, which was monitored by HPLC/MS. Molecular masses of the 332
purified proteins observed in SDS-PAGE corresponded well to the theoretical masses (46 333
kDa of IifA, 28.1 kDa for IifB, 46.3 kDa for IifC and 19.9 kDa for IifD, Fig. S1). 334
IifC was found to be capable of using indole as a substrate only in the presence of 335
IifD flavin reductase, FAD cofactor and NAD(P)H (Fig. 4, peak 3). The product of this 336
reaction was the blue insoluble indigoid pigment (Fig. S2). Next, when IifB was added to 337
the reaction mixture (IifC, IifD, FAD, NADPH, indole), an indigo formation was 338
abolished and a product with identical retention time (4.75 min) as 3-hydroxyindolin-2-339
one was observed (Fig. 4, peak 1). The UV-Vis absorption spectra of this compound and 340
3-hydroxyindolin-2-one were very similar with peaks at 211 nm, 253 and 291 nm (Fig.S 341
3, E and F). Also, both these compounds demonstrated identical molecular masses: 150 342
(3-hydroxyindolin-2-one + H+) and 132 (3-hydroxyindolin-2-one – H2O + H
+) (Fig. S3, 343
E and F). Moreover, 3-hydroxyindolin-2-one was consumed by wild-type indole-induced 344
Acinetobacter sp. O153 cells in a similar way to indole (Fig. 2). 3-hydroxyindolin-2-one 345
was rapidly transformed into anthranilic acid, which was then slowly consumed by 346
indole-induced cells. Meanwhile, no consumption was observed with uninduced cells. 347
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These results indicated that 3-hydroxyindolin-2-one was the reaction product of IifB-348
catalysed reaction and did not act as an inducer for indole-degrading proteins. 349
Figure 4 350
When four Iif proteins (IifC, IifD, IifB and IifA) were used in reaction with 351
indole, a compound with m/z 138 [M+H+] was identified, corresponding to [137+H
+] – a 352
molecular mass of anthranilic acid (Fig. S3, A and B). In addition, this reaction product 353
and anthranilic acid shared identical retention times (Fig. 4, peak 2) and UV-Vis 354
absorption spectra (Fig. S3, A and B). Importantly, IifA protein was also capable of 355
using 3-hydroxyindolin-2-one as substrate to form anthranilic acid (Fig. 4, bottom 356
curve). Notably, conversion of 3-hydroxyindolin-2-one to anthranilic acid by IifA did not 357
require any cofactor or metal ion and did not occur with other substrates of similar 358
structure (isatin, N-formyl-anthranilic acid). The presence of IifE protein in any above-359
mentioned reaction mixtures did not change the outcomes of the reactions. Thus, analysis 360
of reaction products formed by IifA both supported the involvement of 3-361
hydroxyindolin-2-one as an intermediate in indole degradation and showed the formation 362
of anthranilic acid, a possible end-product of IifCDBA-catalyzed indole biodegradation. 363
Table 3 364
The kinetic parameters of IifA, IifC and IifD proteins were determined (Table 3). 365
IifD flavin reductase showed the preference for FMN and NADH. In spite of that, FAD, 366
but not FMN or riboflavin was identified as the only flavin cofactor suitable for indole 367
oxidation performed by IifC (data not shown). 368
Identification of IifA as a possible cofactor-independent oxygenase 369
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Structural and functional approaches were used to analyse the enzymatic 370
mechanism of IifA. The conversion of 3-hydroxyindolin-2-one to anthranilic acid by 371
purified recombinant IifA did not require the addition of any cofactor or metal ions. No 372
cofactor – indicating peaks were observed in the UV-Vis spectrum of the purified IifA 373
protein (Fig. S4). Addition of 1 mM PMSF, 0.5 mM HgCl2 or 3 mM EDTA did not 374
inhibited the reaction suggesting a non-hydrolytic metal-ion-independent enzymatic 375
conversion. Moreover, oxygen was consumed in the abovementioned reaction in a 376
substrate-depending manner (Fig. 5A), i.e. an addition of 3-hydroxyindolin-2-one 377
equivalent to oxygen concentration resulted in a complete consumption of oxygen, while 378
1:2 molar ratio of substrate:oxygen consumed half of the oxygen present in air-restricted 379
reaction cell. Notably, the reaction did not occur in the absence of dioxygen (Fig. S5). 380
Oxidation of 3-hydroxyindolin-2-one to anthranilic acid by IifA was monitored 381
spectrophotometrically and a decrease in absorbance at 260 nm as well as an increase in 382
absorbance at 225 nm and 315 nm were observed (Fig. 5B). The presence of two 383
isosbestic points indicated that no intermediates were formed during this reaction. 384
Figure 5 385
Protein sequence analysis of IifA performed using CDD database indicated the 386
presence of two domains: N-terminal DLH-like domain and C-terminal SnoaL-like 387
domain (Fig. S6B). Attempts to obtain separate recombinant domains were unsuccessful 388
due to insolubility suggesting a major structural role of both domains during protein 389
folding. A three-dimensional model of IifA was generated with I-TASSER platform. A 390
standard α/β hydrolase fold was located in the N-terminal domain, composed of a β-sheet 391
of seven strands with the first strand antiparallel to the others. A typical catalytic triad, 392
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common to the majority of hydrolases, was located in this domain and was composed of 393
Cys124, Asp173 and His204 (Fig. S6A). Residues of this putative catalytic triad were 394
located close to each other in the three-dimensional model. Although the overall 395
sequence identity between the N-terminal domain of IifA and well-described cofactor-396
independent dioxygenases Hod and Qdo was low (17.9 % with Hod and 19.1 % with 397
Qdo), the structural resemblance was clearly evident (Fig. S7). 398
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DISCUSSION 399
The present article deals with identification of genes in Acinetobacter sp. strain 400
O153, required for degradation of N-heterocyclic compound, indole. These genes are 401
clustered into an Iif operon with five genes coding for potential enzymes. The initial 402
description of proteins encoded by genes of Iif operon clearly showed the ability of IifC 403
to oxidize indole leading to formation of indigo pigment (23). Here, the ability of IifC to 404
oxidize indole to indigo was confirmed, but no appearance of indigo was observed when 405
three proteins, namely IifC, IifD and IifB, were incubated with indole in vitro, though the 406
concentration of indole readily decreased. Incorporation of all four proteins (IifC, IifD, 407
IifB and IifA) into the reaction mixture resulted in the formation of anthranilic acid. 408
Importantly, genes encoding a multi-subunit anthranilate dioxygenase are located close 409
to the iif operon in most of the organisms, potentially capable of degrading indole, or 410
located in separate chromosomes, as in the case of Cupriavidus metallidurans CH34 and 411
C. basilensis 4G11 (Fig. 3). Anthranilate dioxygenase converts anthranilic acid to 412
catechol (42) which is then catabolized through a well-established β-ketoadipate pathway 413
(43). Such degradation pathway where indole is oxidized to metabolites, directly 414
reaching tricarboxylic acid cycle (TCA) might enable microorganisms to both counteract 415
the toxic effect of indole and use it as a carbon and energy source. Although this may be 416
true for some other microorganisms with reported indole utilization as sole carbon source 417
and iif-ant combination identified, the strain O153 did not grow with indole as the only 418
carbon source. This suggests difficulties in coping with toxic effects of indole (see 419
references in Introduction section) or insufficient metabolic activity to shuttle the indole 420
degradation products into TCA, for example, low expression levels or relatively poor 421
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catalytic efficiency of catechol dioxygenase (44, 45). Still, anthranilic acid was 422
consumed by the cells of the strain O153 with no product-indicating spectra suggesting 423
utilization of anthranilate in other cellular processes, possibly as a substrate for 424
anthranilate phosphoribosyltransferase during the synthesis of tryptophan (46). The strain 425
O153 used indole (ranging from 0.5 to 1.5 mM) as the sole nitrogen source indicating a 426
physiological benefit when occupying indole-containing environments. 427
Based on the results presented above, a scheme for indole biodegradation in 428
Acinetobacter sp. strain O153 is proposed (Fig. 6). Degradation starts with indole 429
oxidation at C2 and C3 positions, forming indole-2,3-dihydrodiol. This compound is 430
known to be rather unstable (22) and therefore was not detected. A spontaneous 431
dehydration of indole-2,3-dihydrodiol results in the formation of indoxyl, which is prone 432
to auto-oxidation and forms an insoluble indigo pigment. However, the loss of water 433
molecule could be prevented by IifB, forming a stable intermediate. The hypothetical 434
short-chain dehydrogenase IifB performs oxidation at C2 position to obtain 3-435
hydroxyindolin-2-one. Anthranilic acid, formed by IifA, is then the end product of 436
IifCDBA-catalysed indole biodegradation. 437
Figure 6 438
Proteins with notable sequence similarity to Iif proteins were described earlier 439
leading to coherent concepts and hypotheses. Firstly, MoxY (65 % sequence identity to 440
IifC) and MoxZ (38 % sequence identity to IifD) proteins with indole oxidation activity 441
were suggested to be involved in the production of quorum-sensing inducing compound 442
(47). Later, a genomic fragment of R. opacus 1CP containing several genes with high 443
structural similarity to Iif operon was published (48) emphasizing its role in styrene 444
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biodegradation. Monooxygenase activity of this fragment was detected by indole 445
oxidation to indigo and was attributed specifically to StyA2B, styrene-epoxidizing fusion 446
protein containing both oxidation and flavin-reduction activities (47 % sequence identity 447
between N-terminal segment of StyA2B and IifC, 52 % sequence identity between IifD 448
and C-terminal segment of StyA2B). ORFs 6 and 9, composing a possible structural 449
homologue of IifA of this fragment and forming a hypothetical dienolactone hydrolase, 450
were interrupted by transposase most likely rendering this protein inactive. A complete 451
set of Iif-homologous genes was then found in R. opacus MR11 including an adjacent 452
multi-subunit anthranilate dioxygenase leading to hypothesis that the locus described 453
therein might be involved in the degradation of heteroaromatic compounds (49). Finally, 454
indole-detoxification ability of IifC-IifD system as well as flavin-oxidoreductase activity 455
of IifD were demonstrated in representatives of genus Acinetobacter (23, 50). From 456
current perspective, it appears that Iif cluster was en route to the notion of a link between 457
indole as substrate for Iif proteins, high metabolic versatility of acinetobacters and 458
biodegradation. 459
In the proposed model of indole biodegradation, IifC should act as a dioxygenase, 460
incorporating oxygen atoms at both C2 and C3 positions. However, IifC appears to have 461
typical structural elements of flavin-containing monooxygenases (23). Although difficult 462
to detect experimentally, indole dioxygenation was reported for a number of bacterial 463
dioxygenases and monooxygenases (25, 51). Indole-2,3-dihydrodiol, a product of 464
possible dioxygenase attack was observed in the biotransformation of indole by 465
Cupriavidus sp. strain KK10 (52). Notably, several species of Cupriavidus were 466
identified to possess the iif-ant cluster (Fig. 3). Indole-2,3-dihydrodiol was not observed 467
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directly as a reaction intermediate during the indole degradation described here which 468
might be attributed to the instability of this compound (22). Importantly, the formation of 469
indigo from indole-2,3-dihydrodiol was declared in indole oxidation reaction catalysed 470
by naphthalene dioxygenase (22). A possible mechanism of indole-2,3-dihydrodiol 471
formation might be hydrolysis of indole 2,3-epoxide, which was identified as 472
intermediate during indole epoxidation performed by a styrene monooxygenase (53) and 473
was suggested to form 2,3-trans diol spontaneously or enzymatically (54). The opening 474
of the epoxide to a diol was presumed as plausible pathway for indole-2,3-dihydrodiol 475
formation (55). Moreover, the oxidation of several N-heterocyclic compounds catalysed 476
by monooxygenases when insertion of two oxygen atoms (one from oxygen, another 477
from water) took place was described recently (56-58). A similar mechanism for 478
bacterial degradation of indole acetic acid was described (59) involving the intermediate 479
dioxindole-3-acetic acid (DOAA), a structural analogue of 3-hydroxyindolin-2-one in 480
indole degradation. Formation of DOAA was not attributed to a single enzymatic step 481
and either second hydroxylation or hydroxy/keto oxidoreduction mechanisms were 482
suggested. Given these points, deciphering the mechanism of IifC requires further 483
structural studies. 484
The role of IifE in the degradation of indole remains poorly understood and might 485
even be ruled out based on several experimental evidence. First, no changes were 486
observed when recombinant IifE protein was added into reaction mixture consisting of 487
indole and other Iif proteins, i.e. such reaction still yielded anthranilic acid with complete 488
substrate consumption. Next, the expression levels of IifE did not change upon addition 489
of indole according to qRT-PCR results (23). Finally, the gene coding for IifE appears to 490
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be absent in genomes of several microorganisms that possess the iif operon. Interestingly, 491
the presence of a putative signal sequence was detected in this protein with cleavage site 492
between residues 24 and 25 (AQA-YD) using SignalP (60). Also, this protein showed 493
low sequence identity to Pput2725 membrane channel from P. putida F1. Taken 494
together, such inconsistent insights provide no precise functional description for this 495
protein; yet possible functions as facilitation of indole uptake or other metabolic 496
activities are suggested and worth exploring. 497
As already pointed out, a distinct group of extraordinary dioxygenases catalyses 498
the incorporation of oxygen atoms into organic substrates with no requirements for 499
cofactors. Structural and functional properties of IifA appear to be very similar to those 500
of the best described cofactor-independent dioxygenases such as 1H-3-hydroxy-4-501
oxoquinoline 2,4-dioxygenase (Qdo) from Pseudomonas putida 33/1 and 1H-3-hydroxy-502
4-oxoquinaldine 2,4-dioxygenase (Hod) from Arthrobacter ilicis Rü61a (61). All these 503
enzymes share an α/β structural fold and a speculative catalytic triad, which was 504
demonstrated to rather act as a dyad as mutants of catalytic Ser retained substantial 505
activity (18, 61). Catalytic properties of IifA also resemble those of cofactor-free 506
dioxygenase from an aerobic Gram-positive coccus participating in indole 507
biodegradation described by Fujioka and Wada (62). This cofactor-free dioxygenase was 508
able to convert 2-oxo-3-hydroxyinoline to stoichiometric amounts of anthranilic acid and 509
CO2 with the consumption of equivalent amounts of dioxygen (62). As it stands, the 510
establishment of IifA as oxygenase catalysing the ring-opening reaction requires 511
additional experiments in elucidation of the fate of C2 carbon atom of 3-hydroxyindolin-512
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2-one during oxidation process as well as site-directed mutagenesis to prove the role of 513
putative catalytic amino acid residues, which are currently under way. 514
Notably, a number of bacterial genera with iif and ant operons identified in this 515
work have already been described as indole degrading microorganisms. B. unamae strain 516
CK43B was found to degrade indole under aerobic conditions when supplemented with 517
gallic acid or pyrogallol (63) showing a similar cometabolic effect of indole degradation 518
as in the case of strain O153. Importantly, indoxyl was detected as the reaction 519
intermediate as well as compounds of β-ketoadipate pathway, anthranilic acid and 520
catechol, signifying the possible relationship between Iif proteins and indole 521
biodegradation in genus Burkholderia. Cupriavidus sp. strain SHE was also reported to 522
be able to perform indole biodegradation (28); however, no intermediates were 523
identified, except for isatin. A compound with m/z corresponding to isatin was also 524
observed during Iif-catalysed indole biodegradation. Nonetheless, based on results 525
presented here indicating that (i) in contrary to indole, isatin was not consumed by 526
resting cells during an uptake assay and (ii) isatin was not a substrate for any of the Iif 527
proteins described here, we suggest that isatin might not be an intermediate during Iif-528
catalysed indole degradation, but rather appeared as a dead-end product of spontaneous 529
oxidation or an experimental artefact. While indole biodegradation characteristics were 530
also evaluated for representatives of genus Pseudomonas (P. aeruginosa strain Gs) and 531
Alcaligenes (Alcaligenes sp. strain In 3) (26, 64), no data is available regarding the 532
biodegradation of indole in genus Acinetobacter to date. Such high prevalence of iif 533
operon might be explained by a dual beneficial effect of indole degradation. Indole, 534
produced mainly by E. coli in the intestine, can decrease virulence of P. aeruginosa (65). 535
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This effect was later attributed to the indole-caused inhibition of AHL-based quorum-536
sensing signalling by altering the folding of AqsR regulator (14, 66). Such effect was 537
reported for a number of Gram-negative bacteria, including Chromobacterium 538
violaceum, P. chlororaphis, Serratia marcescens (67) and A. oleivorans DR1 (14), a 539
strain which was identified here to possess the iif-ant operon combination (Fig. 3). In a 540
complex and competition-prone environment such as gastrointestinal tract, indole 541
production might become an advantage if the producer does not utilize AHL-based 542
signalling, which is the case for E. coli (68). The degradation of indole and utilization as 543
additional carbon and energy source using the Iif-AntABC enzymatic system described 544
here might be a possible solution for AHL-producers, including genus Acinetobacter 545
(69), to counteract the toxic indole effect and retain fitness. Taken together, the 546
accordance between de facto indole degrading microbial genera and the prevalence of iif 547
and ant operon combination suggests that proteins encoded by the iif operon might be 548
responsible for indole biodegradation in the majority of microorganisms, described to 549
date as indole-degraders. 550
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ACKNOWLEDGMENTS 551
The authors are grateful to dr. Regina Vidziunaite and I. Bratkovskaja for 552
technical assistance with oxygen consumption measurements and A. Laurynenas for 553
generation of anaerobic conditions. 554
Conflict of interest statement: none declared. 555
556
FUNDING INFORMATION 557
This work was supported by the Research Council of Lithuania (project No. MIP-558
042/2012). 559
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Cupriavidus sp. KK10 proceeds through N-heterocyclic and carbocyclic-aromatic 698
ring cleavage and production of indigoids. Int. Biodeter. Biodegr. 97:13–24. 699
53. O’Connor KE, Dobson ADW, Hartmans S. 1997. Indigo formation by 700
microorganisms expressing styrene monooxygenase activity. Appl. Environ. 701
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54. Allen CCR, Boyd DR, Larkin MJ, Reid KA, Sharma ND, Wilson K. 1997. 703
Metabolism of naphthalene, 1-naphtol, indene, and indole by Rhodococcus sp. strain 704
NCIMB 12038. Appl. Environ. Microbiol. 63:151–155. 705
55. Linhares M, Rebelo SLH, Simoes MMQ, Silva AMS, Neves MGPMS, Cavaleiro 706
JAS, Freire C. 2014. Biomimetic oxidation of indole by Mn(III)porphyrins. Appl. 707
Catal. A-Gen. 470:427–433. 708
56. Chaiyen P. 2010. Flavoenzymes catalyzing oxidative aromatic ring-cleavage 709
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57. Stanislauskienė R, Gasparaviciute R, Vaitekunas J, Meskiene R, Rutkiene R, Casaite 711
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investigation of their application for functional screening. FEMS Microbiol. Lett. 714
327:78–86. 715
58. Kutanovas S, Stankeviciute J, Urbelis G, Tauraite D, Rutkiene R, Meskys R. 2013. 716
Identification and characterization of tetramethylpyrazine catabolic pathway in 717
Rhodococcus jostii TMP1. Appl. Environ. Microbiol. 79:3649–3657. 718
59. Donoso R, Leiva-Novoa P, Zúñiga A, Timmermann T, Recabarren-Gajardo G, 719
González B. 2016. Biochemical and genetic bases of indole-3-acetic acid (auxin 720
phytohormone) degradation by the plant-growth-promoting rhizobacterium 721
Paraburkholderia phytofirmans PsJN. Appl. Environ. Microbiol. 722
83:10.1128/AEM.01991-16. 723
60. Petersen TN, Brunak S, von Heijne G, Nielsen H. 2011. SignalP 4.0: discriminating 724
signal peptides from transmembrane regions. Nat. Methods 8:785–786. 725
61. Fischer F, Kunne S, Fetzner S. 1999. Bacterial 2,4-Dioxygenases: New Members of 726
the α/β Hydrolase-Fold Superfamily of Enzymes Functionally Related to Serine 727
Hydrolases. J. Bacteriol. 18:5725–5733. 728
62. Fujioka M, Wada H. 1968. The bacterial oxidation of indole. Biochim. Biophys. 729
Acta 158:70–78. 730
63. Kim D, Rahman A, Sitepu IR, Hashidoko Y. 2014. Accelerated degradation of 731
exogenous indole by Burkholderia unamae strain CK43B exposed to pyrogallol-type 732
polyphenols. Biosci. Biotech. Biochem. 77:1722–1727. 733
64. Claus G, Kutzner HJ. .1983. Degradation of indole by Alcaligenes spec. Syst. Appl. 734
Microbiol. 4:169–180. 735
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65. Lee J, Attila C, Cirillo SLG, Cirillo JD, Wood TK. 2009. Indole and 7-736
hydroxyindole diminish Pseudomonas aeruginosa virulence. Microb. Biotechnol. 737
2:75–90. 738
66. Chu W, Zere TR, Weber MW, Wood TK, Whiteley M, Hidalgo-Romano B, 739
Valenzuela E, McLean RJC. 2011. Indole production promotes Escherichia coli 740
mixed-culture growth with Pseudomonas aeruginosa by inhibiting quorum 741
signaling. Appl. Environ. Microbiol. 78:411–419. 742
67. Hidalgo-Romano B, Gollihar J, Brown SA, Whiteley M, Valenzuela Jr.E, Kaplan 743
HB, Wood TK, McLean RJC. 2014. Indole inhibition of N-acylated homoserine 744
lactone-mediated quorum signaling is widespread in Gram-negative bacteria. 745
Microbiology 160:2464–2473. 746
68. Ahmer BM. 2004. Cell-to-cell signaling in Escherichia coli and Salmonella 747
enterica. Mol. Microbiol. 52:933–945. 748
69. Chan KG, Atkinson S, Mathee K, Sam C-K, Chhabra SR, Camara M, Koh C-L, 749
Williams P. 2011. Characterization of N-acetylhomoserine lactone-degrading 750
bacteria associated with the Zingiber officinale (ginger) rhizosphere: Co-existence of 751
quorum quenching and quorum sensing in Acinetobacter and Burkholderia. BMC 752
Microbiology 11:51. doi:10.1186/1471-2180-11-51. 753
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TABLE AND FIGURE LEGENDS 754
755
Table 1. Primers and plasmids used in this study. Underlined nucleotide sequences 756
are introduced sequences for recognition of restriction endonucleases. 757
Table 2. Predicted conserved domains and putative functions of proteins encoded by 758
genes identified in a 12-kb genomic fragment of Acinetobacter sp. O153. 759
Table 3. Kinetic parameters of IifD, IifC and IifA proteins. Presented are mean values ± 760
S.D. 761
Fig. 1. Growth kinetics of Acinetobacter sp. strain O153. A – growth in minimal medium with 762
different carbon and nitrogen sources, B – growth in minimal medium supplemented with 763
different concentrations of indole as nitrogen source and succinate as carbon source. Filled 764
squares – NH4Cl (5 g/L) and succinate (5 mM) (positive control), filled triangles – indole (1 mM) 765
and succinate, filled rhombus – NH4Cl and indole (1 mM), filled circles – indole (1 mM), squares 766
- no N source and succinate (negative control), empty circles – 0.1 mM indole, crosses – 0.5 mM 767
indole, triangles – 0.75 mM indole, rhombus – 1.5 mM indole, line-filled squares – 2 mM indole. 768
Dashed lines represent trendlines using moving average data approximation (period = 2). 769
Fig. 2. Whole-cell bioconversion assays using different substrates and cells of 770
Acinetobacter sp. O153. A – substrates without cells (negative control), B – 771
bioconversion with uninduced (overnight culture grown without indole) cells, C – 772
bioconversion with induced (overnight culture grown in the presence of 1 mM indole) 773
cells. Solid lines indicate spectra of initial and final products, dashed lines – spectra of 774
intermediate products during 6-hour bioconversion cycle. 775
Fig. 3. Organization and distribution of iif and ant genes in different microbial genomes. 776
Genes are represented by arrows (drawn to scale as indicated). Homologous genes are 777
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highlighted in the same pattern: rhombus grid – homologues of iifA, simple grid – iifB, 778
zigzag – iifC, horizontal lines – iifD, oblique bricks – iifE, vertical lines – araC, dotted 779
fill – antA, grey fill – araB, light grey fill – araC, white fill – indole degradation 780
unrelated / unknown. Strains and genomic fragments highlighted in solid lines indicate 781
reported activity of certain Iif-homologous proteins, dashed lines highlight strains for 782
which indole biodegradation activity was reported in genus level. Identities (%) of amino 783
acid sequence between Iif proteins of strain O153 and homologues are indicated under 784
the corresponding ORFs. 785
Fig. 4. Stacked HPLC chromatograms (211 nm) of enzymatic reaction products and 786
standards. Top three curves – standards, middle four curves – reaction products of indole 787
and Iif proteins as indicated at the right side, bottom curve – reaction product of 3-788
hydroxyindolin-2-one and IifA. Numbers indicate peaks of three major compounds – 3-789
hydroxyindolin-2-one (1), anthranilic acid (2) and indole (3). 790
Fig. 5. Functional characterization of IifA. A – oxygen consumption by IifA, red, green 791
and blue colours indicate different substrate concentrations as depicted, reactions were 792
initiated at 90 s; B – UV spectra of transition between 3-hydroxyindolin-2-one and 793
anthranilic acid, catalysed by IifA. Inset shows spectral difference between the substrate 794
and the product. 795
Fig. 6. Proposed indole biodegradation pathway in Acinetobacter sp. O153. 1 – indole, 2 796
– indole-2,3-dihydrodiol, 3 – 3-hydroxyindolin-2-one, 4 – anthranilic acid, 5 – isatin, 6 – 797
1H-indol-3-ol (indoxyl), 7 – indigo. Brackets indicate experimentally non-detected 798
intermediate. 799
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Primer name Sequence (5‘-3‘) Purpose Reference
CMBFNdeI GATCATATGTCAGGCCAAGATATTGAA Amplification
and cloning
of iifA gene
This work
CMBRXhoI CTCTCGAGTTAAAACGATTTGCCTTCA
SCDFNdeI GAGTGGCATATGGATATTGAATTGAATCAG Amplification
and cloning
of iifB gene
This work
SCDRXhoI ATCTCGAGTCACGCTTCATCGGCTA
APRLF GATCATATGCGTCGTATCGCTATAG Amplification
and cloning
of iifC gene
This work
APRLR CTACTCGAGTTAAGCCACTTTTTGAC
iifDFNheI TGGCTAGCATGAATATCAACACATC Amplification
and cloning
of iifD gene
This work
iifDRXhoI CTGCTCGAGTTAAATACTCAGTTC
MetAFNcoI CTCCATGGCCAATAATGTGATCAAAAG Amplification
and cloning
of iifE gene
This work
MetARHindIII GAAGCTTTCAGAAGTGATGAATATAAC
27F AGAGTTTGATCMTGGCTCAG Amplification
and
sequencing
of 16S rRNA
gene
(30)
1492R TACGGYTACCTTGTTACGACTT
Plasmid Description / purpose Source
pTZ57R/T TA cloning of PCR products ThermoFisher
Scientific
(Lithuania)
pUC19 Construction of genomic library ThermoFisher
Scientific
(Lithuania)
pET28-c(+) Expression of recombinant proteins Novagen
(Germany)
pET28-iifA iifA gene, amplificated by PCR with CMBFNdeI and
CMBRXhoI primers, digested with NdeI/XhoI and cloned
into pET28-c(+) for expression of recombinant Nterminally
6x His-tagged IifA
This work
pET28-iifB iifB gene, amplificated by PCR with SCDFNdeI and
SCDRXhoI primers, digested with NdeI/XhoI and cloned
into pET28-c(+) for expression of recombinant Nterminally
6x His-tagged IifB
This work
pET28-iifC iifC gene, amplificated by PCR with CMBFNdeI and
CMBRXhoI primers, digested with NdeI/XhoI and cloned
This work
into pET28-c(+) for expression of recombinant Nterminally
6x His-tagged IifC
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pET28-iifD iifD gene, amplificated by PCR with iifDFNheI and
iifDRXhoI primers, digested with NheI/XhoI and cloned
into pET28-c(+) for expression of recombinant Nterminally
6x His-tagged IifD
This work
pET21-iifE iifE gene, amplificated by PCR with MetAFNcoI and
MetARHindIII primers, digested with NcoI/HindIII and
cloned into pET28-c(+) for expression of recombinant IifE
This work
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Protein
Conserved domain
(family accession
number)
E-value
Closest homolog with known function
Protein
Locus tag or
protein ID
Function
Identity
(%)
Reference
IifA
α/β hydrolase
(COG0412)
2.3e-53
ClcD from P.
knackmussii
B13
AAB71539.1
Dienolactone
hydrolase
34 (39)
SnoaL-like
polyketide cyclase
(pfam07366)
0.04
IifB
Short-chain
dehydrogenase
(cd05233)
1.2e-56
FabG from
Vibrio
cholerae
N16961
VC2021
Reduction of β-
ketoacyl-ACP to 3-
hydroxyacyl-ACP
33 (40)
IifC - -
IifC from A.
baumannii
ATCC19606
F911_02004 Monooxygenase 82 (23)
IifD
Flavin reductase
(COG1853)
6.8e-40
IifD from A.
baumannii
ATCC19606
F911_02003 Flavin reductase 81 (23)
IifE
MetA-pathway of
phenol degradation
(cl01768)
1.3e-57
Pput2725
from P.
putida F1
4RL8
Outer membrane
channel of unknown
function
21 (41)
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IifR
AraC-binding-like
domain (pfam14525)
4e-39
IifR from A.
baumannii
ATCC19606
F911_02001
Transcriptional
regulator
74 (23)
AntA
Rieske non-heme iron
oxygenase (cd03469)
9e-46
AntA from
Acinetobacter
sp. ADP1
AAC34813.1
Oxygenase
component of
anthranilate
dioxygenase
93 (42) C-terminal catalytic
domain of the
oxygenase alpha
subunit (cd08879)
9e-83
AntB
Ring hydroxylating
beta subunit
(cd00667)
2e-51
AntB from
Acinetobacter
sp. ADP1
AAC34814.1
Oxygenase
component of
anthranilate
dioxygenase
94 (42)
AntC
Benzoate
dioxygenase
reductase FAD/NAD
binding domain
(cd06209)
3e-107 AntC from
Acinetobacter
sp. ADP1
AAC34815.1
Reductase
component of
anthranilate
dioxygenase
87 (42)
2Fe-2S cluster
(cd00207)
3e-21
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Protein / substrate or
cofactor
Km, μM Kcat, min-1
Kcat/Km,
min-1 μM-1
IifD
NADH 29 ± 0.1 1.21 ± 0.15 0.041
NADPH 7.9 ± 0.4 0.13 0.017
FMN 2.85 ± 0.19 2.7 ± 0.45 0.94
FAD 7.07 ± 0.12 7.02 ± 0.64 0.99
Riboflavin 8.35 ± 0.83 3.1 ± 0.43 0.38
IifC Indole 250 ± 13 0.11 ± 0.01 0.00047
IifA 3-hydroxyindolin-
2-one
281.7 ± 13.4 2476 ± 310 17.52
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