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Applied and Environmental Microbiology, June 2000, p. 2664-2667, Vol. 66, No. 6
Division of
Microbiology1 and Division of
Chemistry,2 National Center for Toxicological
Research, U.S. Food and Drug Administration, Jefferson, Arkansas
72079
Received 14 December 1999/Accepted 21 March 2000
Enrofloxacin metabolism by Mucor ramannianus was
investigated as a model for the biotransformation of veterinary
fluoroquinolones. Cultures grown in sucrose-peptone broth were dosed
with enrofloxacin. After 21 days, 22% of the enrofloxacin remained.
Three metabolites were identified: enrofloxacin N-oxide
(62% of the total absorbance), N-acetylciprofloxacin
(8.0%), and desethylene-enrofloxacin (3.5%).
Fluoroquinolones are synthetic
antimicrobial agents that are active against a broad spectrum of
pathogenic gram-negative bacteria as well as some gram-positive
bacteria and mycoplasmas (10). Several fluoroquinolones are
used in clinical medicine, and enrofloxacin and sarafloxacin have been
approved in the United States for veterinary use (4). The
major metabolite of enrofloxacin in animals is ciprofloxacin, produced
by N deethylation of the ethylpiperazine ring (21).
The persistence of veterinary fluoroquinolones and the types of
metabolites that result from their microbial conversion in the
environment have been little known until recent years (6, 12,
22, 23; H. G. Wetzstein, Abstr. 99th Gen. Meet. Am. Soc.
Microbiol. abstr. Q-262, p. 583, 1999). Currently, there is a question
as to whether the use of fluoroquinolones in poultry causes the
replacement of fluoroquinolone-sensitive coliform bacteria by resistant
strains (2, 13).
Cultures of wood-decaying basidiomycetes, including strains found in
manure, have been shown to convert enrofloxacin to CO2 and
at least 11 other metabolites (12, 22). Since other pathways are likely to be used by different organisms involved in the
bioconversion of fluoroquinolones in the environment, we investigated
the transformation of enrofloxacin by a typical zygomycetous soil fungus.
Mucor ramannianus strain R-56, which had been isolated from
a mushroom collected in a forest in Arkansas (17), was
maintained on agar slants (14, 18). Triplicate cultures for
experiments were grown in sucrose-peptone broth (17) for 2 days. Enrofloxacin [1-cyclopropyl-7-(4-ethyl-1-piperazinyl)-6-fluoro-4-oxo-1,4-dihydroquinoline-3-carboxylic acid], as the hydrochloride, was a gift from Bayer Corp., Shawnee, Kans. Enrofloxacin hydrochloride was dissolved in 20 mM aqueous KOH and
filter sterilized; 1.0 ml was added to each flask to make a final
concentration of 253 µM enrofloxacin. The cultures were then
incubated for an additional 21 days. Cultures without enrofloxacin and
dosed, noninoculated controls were also incubated.
Methylene chloride extracts of cultures and controls were analyzed by
high-performance liquid chromatography (HPLC) (17), using a
Phenomenex (Torrance, Calif.) Prodigy 5-µm ODS-3 column (10 by 250 mm) with a water-acetic acid-methanol gradient (17). The
flow rate was 2.5 ml min For direct exposure probe-electron ionization (DEP/EI) mass
spectrometry (17), the quadrupole was scanned from
m/z 50 to 650. For liquid chromatography-electrospray
ionization (LC/ESI) mass spectrometry (17), a Vydac RP-18
pharmaceutical (5-µm) microbore column (1 by 250 mm; Separations
Group, Hesperia, Calif.) was used. The mobile-phase components
consisted of 5% methanol with 0.1% formic acid (A) and 95% methanol
with 0.1% formic acid (B). The mobile phase was 10% B for 5 min,
followed by a linear gradient of 10 to 90% B over 10 min at a flow
rate of 70 µl min Metabolites to be analyzed by 1H nuclear magnetic resonance
(NMR) spectrometry (17) were dissolved in D2O
containing 20 mM KOD.
HPLC analysis of the methylene chloride extracts from cultures of
M. ramannianus dosed with enrofloxacin (Fig.
1) showed that enrofloxacin eluted from
the HPLC column at 13.9 min and three metabolites eluted at 13.3, 16.2, and 33.2 min. By 21 days, the levels of all three metabolites had
reached plateaus (data not shown). Then, as shown by the peak area
(A280), only 22% of the enrofloxacin remained.
0099-2240/00/$04.00+0
Microbiological Transformation of Enrofloxacin by
the Fungus Mucor ramannianus
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1; metabolites were quantified by
the peak areas at 280 nm.
1. For tandem mass spectrometry
(MS/MS) (17), the apparent protonated molecules were mass
selected in Q1 and fragmented in the collision cell, with the product
ions separated in Q3. With one metabolite, in-source collision-induced
dissociation (CID) at 10 eV was used in conjunction with LC/ESI/MS to
increase the yield of fragment ions.

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FIG. 1.
HPLC chromatogram, obtained at 280 nm, for the
metabolites (I to III) produced from enrofloxacin by M. ramannianus.
Enrofloxacin had a UV spectrum nearly identical to that reported by
Wetzstein et al. (22). The DEP/EI mass spectrum had significant ions at m/z 359 [M]+·, 344, and
315, and the negative-ion chemical ionization (DEP/NICI) mass spectrum
had a radical anion at m/z 359 with an apparent O2 adduct at m/z 391. The LC/ESI/MS and
ESI/MS/MS mass spectra for enrofloxacin are shown in Table
1, and the 1H NMR spectral
data appear in Table 2.
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Metabolite I eluted from the HPLC column at 13.3 min (Fig. 1), with a peak area of 3.5% of the total A280 and a UV spectrum nearly identical to that of the desethylene-enrofloxacin metabolite F-4 of Wetzstein et al. (22). The positive-ion chemical ionization (DEP/PICI) mass spectrum of metabolite I had an apparent protonated molecule at m/z 334 [MH]+ and a fragment ion at m/z 276; the DEP/NICI mass spectrum consisted primarily of a molecular anion at m/z 333. The LC/ESI/MS and ESI/MS/MS mass spectra for metabolite I are shown in Table 1.
In the 1H NMR data for metabolite I (Table 2), all of the
aromatic resonances were shifted with respect to enrofloxacin. The resonance of proton H8 was shifted to 7.15 ppm from 7.56 ppm for enrofloxacin. Four of the piperazine protons of enrofloxacin were missing in metabolite I. Two of the remaining piperazine protons, now
called the ethylidene
protons, were shifted to 3.09 ppm from 3.28 ppm for enrofloxacin. The other two, now called the ethylidene
protons, were shifted to 2.86 ppm from 2.57 ppm for enrofloxacin. The
CH2 protons of the ethyl group were shifted to 3.60 ppm
from 2.40 ppm for enrofloxacin, and the CH3 protons were
shifted to 1.17 ppm from 1.06 ppm for enrofloxacin. The results are consistent with the assignment of metabolite I as
1-cyclopropyl-7-{[2-(ethylamino)-ethyl]-amino}-6-fluoro-4-oxo-1,4-dihydroquinoline-3- carboxylic
acid (desethylene-enrofloxacin) (Fig. 2).
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Metabolite II eluted from the HPLC column at 16.2 min (Fig. 1), with a
peak area of 62% of the total A280. The UV
spectrum of metabolite II had
max values of 284, 319, and 331 nm. A background-subtracted, full-scan LC/ESI/MS mass spectrum
of metabolite II (Table 1) showed three significant ions at
m/z 376 [MH]+, 360, and 316. The ion at
m/z 360, corresponding to the loss of an oxygen atom from
the protonated molecule, was consistent with an N-oxide. The ion at
m/z 376 was selected for ESI/MS/MS, and a product-ion mass
spectrum was obtained (Table 1); a major fragment ion appeared at
m/z 315 [MH-CH3CH2N(O)H2]+.
The 1H NMR data for metabolite II (Table 2) show the same number of protons as in enrofloxacin. In metabolite II, six of the eight piperazine proton resonances were degenerate at 3.61 ppm and the other two were at 3.37 ppm. The CH2 protons of the ethyl group of metabolite II were shifted to 3.46 ppm from 2.40 ppm for enrofloxacin. The CH3 of the ethyl group of metabolite II was shifted to 1.40 ppm from 1.06 ppm for enrofloxacin. The resonance of proton H8 was shifted to 7.67 ppm from 7.56 ppm for enrofloxacin. All the results of integration, dipolar coupling, and nuclear Overhauser effect difference experiments were consistent with 1-cyclopropyl-7- (4-ethyl-4-oxopiperazinyl)-6-fluoro-4-oxo-1,4-dihydroquinoline-3-carboxylic acid (enrofloxacin N-oxide), with the oxygen attached to the terminal nitrogen of the piperazine ring (Fig. 2).
Metabolite III eluted from the HPLC column at 33.2 min (Fig. 1), with a peak area of 8.0% of the total A280. The UV and LC/ESI mass spectra were identical to those of N-acetylciprofloxacin (17). When in-source CID was used to produce fragments in an LC/ESI/MS experiment (Table 1), the signal for the protonated molecule at m/z 374 decreased and a single major fragment was observed at m/z 356, corresponding to a loss of water [MH-H2O]+ from the carboxylic acid moiety.
The 1H NMR chemical shifts for metabolite III (Table 2) were the same as those of N-acetylciprofloxacin (17).
The proton-decoupled 19F NMR spectrum of enrofloxacin and that of each of the metabolites (not shown) had only one resonance peak, representing a single F atom.
The biotransformation of drugs by different organisms may proceed by
different pathways. In animals, fluoroquinolones are usually attacked
at the piperazine or the N-methylpiperazine ring, if either
is present, or at the carboxyl group (3). For example, ofloxacin, pefloxacin, and fleroxacin may be modified by N oxidation of
the methylpiperazine rings (11, 16, 20). Enoxacin may be
metabolized in animals by N acetylation, by the removal of two ethylene
carbons from the piperazine ring, and by other reactions (15). The N dealkylation of enrofloxacin to ciprofloxacin in animals (21) may occur by the monooxygenase-mediated
-hydroxylation of the ethyl group via an unstable hemiaminal
intermediate (1).
Several fungi already have been shown to metabolize fluoroquinolones. For instance, the zygomycete Rhizopus arrhizus demethylates the N-methylpiperazine ring of danofloxacin (6). Gloeophyllum striatum and other wood-decaying basidiomycetes metabolize enrofloxacin and ciprofloxacin by hydroxylation, decarboxylation, defluorination, and removal of part or all of the piperazine ring (12, 22, 23). One of the enrofloxacin metabolites of G. striatum, produced by removing two ethylene carbons from the piperazine ring (22), was also a metabolite of M. ramannianus. Ciprofloxacin is metabolized by M. ramannianus to N-acetylciprofloxacin (17), which has now also been identified as a metabolite of enrofloxacin. We propose that enrofloxacin is first converted to ciprofloxacin by N dealkylation and that the resulting ciprofloxacin is N acetylated to give N-acetylciprofloxacin. Ciprofloxacin was not detected in our experiments, presumably because the acetylation step (17) occurred quickly.
In addition to R. arrhizus and M. ramannianus,
other zygomycetous fungi perform drug biotransformations. For
example, four species of Cunninghamella transform the
N-methylpiperidine ring of codeine by demethylation
(19), and Cunninghamella elegans transforms
pyrilamine maleate, thenyldiamine, methapyrilene, and tripelennamine by
N oxidation and N demethylation (5, 9). It is noteworthy
that during the transformation of (
)-deprenyl and pargyline by
Cunninghamella echinulata (7), N
dealkylation is followed by N acetylation.
The transformation of enrofloxacin by M. ramannianus, including N oxidation, N dealkylation, N acetylation, and the breakdown of the piperazine ring, is similar to the mammalian metabolism of other fluoroquinolones (3, 15, 20). For ciprofloxacin, the major mammalian metabolites have significantly less antibacterial activity than the parent compound (24). The fungal enrofloxacin metabolites previously reported also appear to have less antibacterial activity (22).
Since Mucor and Rhizopus species are common in soil and decaying organic matter (8), the biotransformations of veterinary drug residues by zygomycetous fungi are likely to be ecologically significant.
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ACKNOWLEDGMENTS |
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We thank C. E. Cerniglia, T. M. Heinze, E. B. Hansen, Jr., J. D. Moody, and V. V. Lashin for helpful discussions. We also thank Bayer Corp. for kindly providing the enrofloxacin for these experiments.
This work was supported in part by an appointment to the Postgraduate Research Program at the National Center for Toxicological Research administered by the Oak Ridge Institute for Science and Education through an interagency agreement between the U.S. Department of Energy and the U.S. Food and Drug Administration.
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FOOTNOTES |
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* Corresponding author. Mailing address: Division of Microbiology, National Center for Toxicological Research, Jefferson, AR 72079-9502. Phone: (870) 543-7059. Fax: (870) 543-7307. E-mail: jsutherland{at}nctr.fda.gov.
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