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Environmental Processes
Substructure Reactivity Affecting the Manganese Dioxide Oxidation of Cephalosporin Ming-Hao Hsu, Ting-Hao Kuo, Yung-En Chen, Ching-Hua Huang, Cheng-Chih Hsu, and Angela Yu-Chen Lin Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.8b02448 • Publication Date (Web): 24 Jul 2018 Downloaded from http://pubs.acs.org on July 25, 2018
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Substructure Reactivity Affecting the Manganese Dioxide Oxidation of Cephalosporins
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Ming-Hao Hsu†, Ting-Hao Kuo‡, Yung-En Chen†, Ching-Hua Huang§, Cheng-Chih
4
Hsu‡, Angela Yu-Chen Lin*,†
5
†
6
71-Chou-shan Road, Taipei 106, Taiwan, ROC
7
‡
Department of Chemistry, National Taiwan University, Taipei 106, Taiwan, ROC
8
§
School of Civil and Environmental Engineering, Georgia Institute of Technology,
9
Atlanta, Georgia 30332, United States
1
10
Graduate Institute of Environmental Engineering, National Taiwan University,
(*Corresponding author:
[email protected] Tel.: ±886-2-3366-4386)
11 12
Submitted to
13
Environmental Science & Technology
14 15
ABSTRACT
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Cefotaxime (CTX), cephalexin (CFX), cephradine (CFD), cephapirin (CFP), and
17
cefazolin (CFZ), were selected as target cephalosporin antibiotics to study their
18
oxidative transformation by δ-MnO2. Although they all have the same core structure
19
(7-aminodesacetoxycephalosporanic acid), very different MnO2 oxidation rates were
20
observed at pH 4 (the initial reaction rate constant kinit ranged from 0.014 to 2.6 hr-1).
21
An extensive investigation of the substructure compounds and byproduct analysis
22
revealed that the oxidation mainly occurred at the following two sites on the core
23
structure: (1) the sulfur atom in the cephem ring and (2) the carbon-carbon double
24
bond (C=C) and its proximal carboxylic acid group. In the case of (2), when there is
25
an acetyloxymethyl group at the C-3 position of the core structure, the formation of
26
the keto-sulfone byproducts was inhibited. The overall results indicated that a
27
substituent at the C-3 position could stabilize the core structure, which would result in
28
a decrease in the oxidation rate; however, a substituent at the amine position of the
29
core structure might affect the overall degradation rate of the cephalosporin,
30
depending on its reactivity with MnO2. Thus, the apparent reaction rates varied widely
31
in the trend of CTX > CFP > CFD > core structure ≈ CFX > CFZ. The mechanistic
32
elucidation can also help explain the degradation rates of cephalosporin antibiotics in
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other oxidation processes. 1
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1. INTRODUCTION
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Among emerging contaminants, antibiotics are important due to their frequent
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prescription and usage in hospitals. When antibiotics are discharged into the
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environment, several adverse impacts can occur, including increased bacterial
39
resistance 1, expression of resistance genes in the environment 2, and even increased
40
toxicity during transformation in the natural environment 3. Cephalosporin is the
41
second most commonly used antibiotic class; for example, cefotaxime (CTX),
42
cephapirin (CFP), cephradine (CFD), cephalexin (CFX) and cefazolin (CFZ)
43
(Supporting Information Table S1 lists the physicochemical properties of the target
44
compounds) are members of the cephalosporin class of β-lactam antibiotics that can
45
act as penicillins to effectively interfere with the synthesis of gram-positive and
46
gram-negative organisms. Their inhibitory mechanism involves binding to and
47
inactivating enzymes that are needed for bacterial cell wall synthesis. Cephalosporin
48
compounds have been frequently detected in surface waters around the world at
49
concentrations of 0.076 µg/L to 1.117 µg/L 4, 5. In previous studies, the concentrations
50
detected in urban wastewater treatment plant influents and effluents ranged from 2.9
51
µg/L to 64 µg/L and 0.013 µg/L to 2.104 µg/L, respectively, indicating that these
52
compounds are not completely removed by wastewater treatment processes 4-10. In
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addition, higher concentrations of 0.01 µg/L to 42.9 µg/L have been detected in
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hospital effluents 4, 5. Cephalosporin molecules are relatively stable (t1/2 = 10-18 d) in
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terms of hydrolysis under typical environmental conditions (pH ≈ 7, T ≈ 20°C) 11, 12.
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Another study indicated that cephalosporins could not be biodegraded in China’s
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Xuanwu Lake in 7 days 13 and exhibited low octanol-water partitioning coefficients
58
(log Kow = −1.40 to −0.13) 14-16. Oxidative materials present in the environment,
59
mostly sediments, are thought to be relatively important for removing cephalosporin
60
antibiotics.
61
Oxidative transformation by manganese dioxide (MnO2) is considered to be one
62
of the most important natural attenuation processes in aqueous environments because
63
MnO2 has a high reduction potential (1.23 V)
64
degrade many organic compounds, and because it is ubiquitous in soils and sediments
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18, 19
17
, which enables it to effectively
. Several studies have demonstrated that MnO2 can be used as an oxidant to
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remove pharmaceuticals, such as phenol 20, aniline
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and triclosan 24, from aquatic systems.
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, aliphatic amines 22, codeine
23
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Several studies investigated the oxidative transformations of cephalosporins and
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β-lactam antibiotics, and the results indicated that these compounds can undergo
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hydrolytic cleavage or oxidation at the cephem ring during different oxidation
71
processes involving ClO2, dimethyldioxirane, hydrogen peroxide and chloramine-T
72
25-28
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two possible positions. Either the sulfur on the core structure is oxidized to sulfoxide
74
or the amide bond in the β-lactam ring is broken. Recently, Li et al. reported the
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transformation byproducts resulting from the MnO2 oxidation of one particular
76
cephalosporin, CFZ. Four major transformation byproducts of MnO2 oxidation were
77
identified, and degradation pathways involving thioether and olefin oxidation,
78
hydrolysis and acid-catalyzed decarboxylation were proposed 29.
. The pathways proposed in these studies suggest that oxidation mainly occurs at
79
To our knowledge, no study has comprehensively investigated the reactivity and
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associated mechanism among different cephalosporin antibiotics with MnO2. In
81
addition, no research has examined the oxidative sites of the core structure (the
82
common structure of cephalosporins). The objective of this study was to examine the
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reactivities of the core structure (7-aminodesacetoxycephalosporanic acid) and
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substructures (substituents at the C-3 and amine positions of the core structure) of
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cephalosporin, and to identify the oxidation products of the core structure to
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determine the effects of the structure on MnO2 oxidation.
87 88
2. MATERIALS AND METHODS
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2.1. Chemicals and Materials
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All the cephalosporin compounds (over 98% purity) were purchased from
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Sigma-Aldrich and Fluka. Individual stock solutions (100-1000 mg/L) were prepared
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with deionized water and stored at 4°C in amber glass bottles for a maximum of 14
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days. The detailed chemicals and standards used (including the suppliers and purities)
94
in this study are given in the Supporting Information Text S1 (including Table S2).
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The δ-MnO2 synthesis method was proposed by Murray
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Supporting Information (Text S2). The stoichiometry used during δ-MnO2 preparation
97
followed the equation 2 MnO4- + 3 Mn2+ + 2H2O → 5 MnO2(s) + 4H+. In brief, the
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synthesis method involved adding KMnO4 and MnCl2 into a large beaker, using 3
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. Details are given in the
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NaOH to maintain the alkaline state, and sparging the solution with N2 gas to liberate
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oxygen.
δ-MnO2 is consistent with natural birnessite. Detailed characterization data
101
for δ-MnO2 are given in Text S3 (including Table S4, Figure S1−S3).
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2.2. MnO2 Oxidation Experiments
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Oxidation experiments were conducted in 250 mL amber glass bottles loosely
104
covered with Teflon caps. The reaction batches were continuously stirred with
105
magnetic stir bars at 22±2°C. The reaction solutions were maintained at a constant pH
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with 10 mM of buffer, acetic acid and sodium acetate for pH 4 and pH 5,
107
4-morpholinepropanesulfonic acid (MOPS) and its sodium salt for pH 7, and
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2-(cyclohexylamino)ethanesulfonic acid (CHES) and its sodium salt for pH 9. Then,
109
NaCl (10 mM) was added to the solution to maintain a constant ionic strength.
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The oxidation rate of cephalosporin apparently increased with decreasing
111
solution pH in the following order: pH 4 > pH 5 > pH 7 ≈ pH 9 (Figure S4). To ensure
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that the degradation change could be clearly observed, the experiments investigating
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the effects of the substructure reactivity were all conducted at pH 4 under the fixed
114
conditions of 300 nM of cephalosporin and 4 mg/L of MnO2.
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The reaction batch volume was maintained at 100 mL. Two approaches were
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used to quench the reaction and collect samples during the oxidation process. In the
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first approach, aliquots were rapidly passed through 0.22 µm PVDF filter membranes
118
before analysis. In this case, the concentrations of the target compounds decreased
119
due to adsorption and oxidation by MnO2. If no obvious adsorption phenomena were
120
observed, most samples were quenched using this method. The second method was to
121
quench aliquots from the reaction by adding 5 µL of 0.5 M oxalic acid to 1 mL of
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sample. Oxalic acid reduced MnO2 and desorbed target compounds from the MnO2
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surface. Consequently, any loss in concentration was primarily attributed to oxidation.
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By comparing the results of these two methods, the amount of target compounds
125
adsorbed by MnO2 was determined.
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2.3. Analysis
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The target compounds, substructures and byproducts were prepared at a high
128
initial concentration (10 mg/L) to meet the high detection limit of LC-MS/MS. The
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target compounds and their substructures were analyzed using a Sciex API 4000
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LC-MS/MS with an electron-spray ionization (ESI) interface, and the byproduct
131
mixtures were chromatographically separated for quantification analysis using an 4
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Agilent 1200 module equipped with a ZORBAX Eclipse XDB-C18 column (150 ×
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4.6 mm, 5 µm).
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The target compounds and their substructures were detected through MS/MS in
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full-scan mode, which gave their mass spectra. Then, the analytical methods were
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modified to obtain the largest product ion signals in multiple-reaction monitoring
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transition mode (MRM) by adjusting three key parameters, the declustering potential
138
(DP), the collision energy (CE), and the collision cell exit potential (CXP), and using
139
established analytical methods for byproduct analysis. The parameters of the LC
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system, including the gradient of the mobile phase, the flow rate (1.0 mL/min), and
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the injection volume (20 µL), were adjusted to separate the analyte peaks. The mobile
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phase contained 0.1% formic acid (v/v) in DI water or methanol in positive ion mode.
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The byproducts were identified by comparing the chromatographic retention times
144
and ESI-MS spectral data with those of commercially available standards. The
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detailed LC gradients and mass spectrometry conditions of all analyzed compounds
146
are described in the Supporting Information Tables S5 and S6.
147
To precisely explore the oxidation byproducts of cephalosporins, Q Exactive
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Plus hybrid quadrupole-orbitrap mass spectrometry (Thermo Fisher Scientific, USA)
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coupled with a Dionex UltiMate 3000 UHPLC system was used to analyze the
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oxidized samples. Liquid chromatographic separation was conducted by injecting 10
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L of each sample through an Acquity UPLC BEH C18 column (1.7 m, 2.1×100
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mm). The column oven temperature was controlled at 40 °C. The binary solvent
153
system contained mobile phase A of water with 0.1% formic acid and mobile phase B
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of acetonitrile with 0.1% formic acid. The solvent flow rate was set at 0.25 mL/min.
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Each sample was injected with 10 L of solvent and then separated through a 10-min
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solvent gradient: 0-1 min 5% B; 1-4 min 5-95% B; 4-6.5 min 95% B; 6.5-7 min
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95-5% B; and 7-10 min 5% B. The ionization was performed through a heated ESI
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source (Thermo HESI-II probe) using the following parameters: sheath gas flow rate
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of 46 (A.U.), auxiliary gas flow rate of 11 (A.U.), sweep gas flow rate of 2 (A.U.),
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spray voltage of 3.50 kV, capillary temperature of 253 °C, S-lens RF level of 50.0 and
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auxiliary gas heater temperature of 406 °C. MS spectra were obtained in positive
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ionization mode via top-10 data-dependent acquisition, in which full MS spectra were
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acquired with a spectral resolution of 70,000 and scan range of 100-1000 m/z. The
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data-dependent MS/MS spectra were acquired with a spectral resolution of 17,500, 5
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isolation window of 2.0 m/z, normalized CE of 20 and dynamic exclusion of 5.0
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seconds. The resulting LC-MS/MS spectra were processed with Xcalibur Qual
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Browser 2.2 (Thermo).
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3. RESULTS AND DISCUSSION
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3.1. Efficacy of Cephalosporin Removal by MnO2
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This study used batch experiments to investigate the oxidative transformation of
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five cephalosporin antibiotics (CTX, CFP, CFD, CFX, and CFZ) by δ-MnO2. In the
173
absence of MnO2, all the target cephalosporins remained stable in water for 2 days.
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However, in the presence of MnO2, CTX, CFP and CFD were completely removed by
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4 mg/L of MnO2 within 12 hours. Approximately 90% of CFX and 20% of CFZ were
176
removed within 30 hours (Figure 1(a)). As the reaction progressed, the amount of
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cephalosporin rapidly decreased, and the reaction deviated from pseudo-first-order
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kinetics after the first few hours (Figure S5). Similar reaction kinetics were observed
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for reactions between organic compounds and MnO2 in previous studies
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this study, each cephalosporin had a different transformation rate, and the initial
181
reaction rate constant kinit (hr-1) was obtained by fitting the first few time data points
182
with pseudo-first-order kinetics.
20, 24, 31-35
. In
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In this work, the reaction was quenched by filtration and oxalic acid to determine
184
the effects of the sorption and oxidation of cephalosporins by MnO2. Filtration
185
removed MnO2 with chemicals adsorbed to the surface sites, thereby demonstrating
186
the effects of sorption and oxidation. In another batch, oxalic acid was added to the
187
solution to dissolve residual MnO2 and demonstrate the effect of adsorption. The
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results indicated that the residual cephalosporin concentration quenched by the
189
filtration method was approximately equal to that quenched by oxalic acid at pH 4
190
(Figure S6), indicating that the amount of unreactive cephalosporin adsorbed on
191
MnO2 surface sites was negligible. Consequently, oxidative transformation was the
192
main mechanism for cephalosporin removal in the reaction with MnO2.
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3.2. Manganese Dioxide Oxidation Mechanism for Cephalosporins
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All the cephalosporin compounds in this study have very similar structures and
195
contain the same cephem ring, but they have very different MnO2 oxidation rates (the
196
initial reaction rate constant kinit ranged from 0.014 to 2.6 hr-1). Under the same
197
reaction conditions, the degradation rates decreased as follows, as shown in Figure 6
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1(a): CTX > CFP > CFD > core structure ≈ CFX > 7-aminocephalosporanic acid
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(abbreviated 7-ACA) > CFZ. Thus, it was hypothesized that the substructure of a
200
cephalosporin affects its overall reactivity.
201
Figure 1 shows the reactivities of CFZ, CFX, CFD, CFP, CTX and their
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substructures (1H-tetrazole-5-acetic acid, 1-HTA; L-phenylglycine, LP; 2‐amino‐2‐
203
(cyclohexa‐1,4‐dien‐1‐yl)acetic acid, 2-ACAA; (4-pyridylthio)acetic acid, 4-PA;
204
2-amino-α-(methoxyimino)-4-thiazoleacetic acid, 2-AMTA) at the amine position. It
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was hypothesized that (1) the substituent R1 at C-3 stabilizes the core structure, which
206
leads to a decrease in the degradation rate, and (2) the substituent at the amine
207
position of the core structure might affect the overall degradation rate of the
208
cephalosporin, depending on its reactivity with MnO2. In the following sections, the
209
reactivities of the core structure with different substituents, the reactivities of different
210
portions of the substructures and the oxidation byproducts were examined to verify
211
these hypotheses.
212
3.2.1. Reactivity of the Core Structure with the Substituent R1 at the C-3 Position
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As shown in Figure 1(a), when there is an acetyloxymethyl group at the C-3
214
position of the core structure (in the case of CFP, CTX, and 7-ACA), the overall
215
degradation rate is significantly changed. This is clearly demonstrated by comparing
216
the rate of 7-ACA with that of the core structure. The structure of 7-ACA is simply an
217
acetyloxymethyl group bonded to the core structure at the C-3 position, and the
218
acetyloxymethyl group was clearly shown to decrease the degradation rate of the core
219
structure. This phenomenon can be potentially explained as follows: (1) the
220
substituent at the C-3 position may cause steric hindrance and block the reactive sites
221
of the core structure from contacting the MnO2 surface sites; and (2) the relationship
222
between the free energy and the kinetics may play a role in this process. According to
223
studies describing the relative reactivities of model compounds with manganese
224
oxides, the relative oxidation rate decreases as the reduction potential or Hammett
225
coefficient increases
226
substituents and is primarily used to connect the substituent properties with the
227
reactivity of aromatic compounds. Generally, compounds with electron-donating
228
substituents are more susceptible to oxidation than those with electron-withdrawing
229
substituents. The slow degradation rate of 7-ACA relative to the core structure may
230
occur because the acetyloxymethyl substituent on 7-ACA has a stronger
20, 31, 36
. The Hammett constant varies depending on the specific
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electron-withdrawing tendency than the methyl substituent on the core structure
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(Table S7
233
C-3 position (5-methyl-1,3,4-thiadiazole-2-thiol, 5-M) that might also cause steric
234
hindrance; therefore, this substituent likely stabilized the compound, leading to a
235
decrease in the overall rate of CFZ oxidation. Although CFP and CTX also have
236
acetyloxymethyl substituents attached, their overall extremely fast degradation rates
237
are a result of their additional R2 substituents at the amine position (4-PA and
238
2-AMTA), which will be explained in the next section.
239
3.2.2. Effect of the Substituent R2 at the Amine Position of the Core Structure
37
). In addition, CFZ also has an electron-withdrawing substituent at the
240
To test the hypothesis that a substituent at the amine position of the core
241
structure might affect the overall degradation rate of the cephalosporin, depending on
242
its reactivity with MnO2, several experiments were performed to compare the
243
substructure reactivities. The various substructures react with MnO2 at different rates,
244
which decrease in the following order: 2-AMTA > 2-ACAA > core structure > LP ≈
245
1-HTA ≈ 4-PA (inert to oxidation). Rate comparisons are shown in Figure 1(b). The
246
core structure can be oxidized by MnO2; however, depending on the reactivities of the
247
substructures, substructures such as 2-AMTA and 2-ACAA will be oxidized before
248
the core structure, thereby enhancing the overall oxidation rate.
249
In the case of CTX, which has the most reactive substructure, 2-AMTA, the
250
reactivity of the 2-AMTA substructure has the same oxidation rate as CTX, as shown
251
in Figure 2(a). Since CTX (initial rate = 7.8×10-7 M/hr) degrades much faster than the
252
core structure (initial rate = 5.7×10-8 M/hr) and 7-ACA (initial rate = 1.13×10-8 M/hr),
253
this result suggests that oxidation must occur first on 2-AMTA, which is degraded
254
before the core structure.
255
Another even more obvious case is when the MnO2 oxidation rate of the core
256
structure (initial rate = 5.7×10-8 M/hr) is compared to that of CFD (initial rate =
257
2.49×10-7 M/hr). With the addition of 2-ACAA (the second most reactive substructure)
258
at the amine position in CFD, the degradation rate was significantly enhanced. Similar
259
to the case of CTX, the oxidation of CFD occurs first on the 2-ACAA substructure,
260
which determines the overall decomposition rate. The unstable dienyl moiety (part of
261
the 2-ACAA substructure) is then oxidized and transformed into a phenyl group in
262
CFX. According to the byproduct analysis, we found that more than 90% of the CFD
263
is first oxidized to CFX and then gradually degraded by MnO2 (Figure 3). Since the 8
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phenyl group (LP substructure) of CFX is nonreactive toward MnO2 oxidation (Figure
265
2(b)), CFX has a similar MnO2 oxidation rate to that of the core structure.
266
Furthermore, LP formed after 3 hours of CFX oxidation, indicating that the core
267
structure decomposes first, and then LP is released as one of the byproducts, as shown
268
in Figure 3. Moreover, several of the CFX oxidation byproducts that are similar to the
269
core structure byproducts were identified to elucidate the oxidation sites on the core
270
structure (Table S8, Figure S9), and all of the core structure byproducts (Figure 4;
271
oxidation products 1, 2, 3, 4, and 5) were also detected during CFX degradation.
272
The fast oxidation rate (initial rate = 3.45×10-7 M/hr) of CFP, for which the
273
substructure 4-PA is relatively inert, is intriguing. As shown in Figure 2(b), 4-PA was
274
minimally degraded by MnO2 at pH 4; however, it was found to be the byproduct of
275
CFP degradation by MnO2. The only possible explanation is the cleavage of the amine
276
bond between 4-PA and the core structure. In addition, another oxidation product
277
((4-pyridylthio) acetamide, 4-PA-NH) formed by cleaving the C-N bond (near the
278
amide bond, at the amine position) was detected (Figure S7). This is another case that
279
demonstrates how the amine substituent affects the overall CFP degradation rate.
280
Of the five cephalosporins studied, CFZ is the only compound that degrades
281
more slowly than the core structure (and even 7-ACA) upon exposure to MnO2, as
282
shown in Figure 1(a), and its substructure 1-HTA is relatively nonreactive toward
283
MnO2 oxidation (Figure 1(b)). Similar to the degradation of CFX and CFP, CFZ was
284
degraded by the hydrolysis of the amide bond to form a carboxylic acid byproduct,
285
and only a trace amount of 1-HTA was formed. The result indicated that the
286
degradation of CFZ was slightly associated with amine bond breaking and that the
287
core structure is first decomposed. Collectively, these results suggested that the
288
degradation rate of CFZ was mainly slower due to the 5-M substituent at the C-3
289
position, not the 1-HTA substituent at the amine position. This finding further
290
supported the hypothesis that the steric hindrance and electron-withdrawing tendency
291
of the C-3 substituent can stabilize the core structure, leading to a decrease in the
292
degradation rate.
293
3.2.3 Oxidation Sites within the Core Structure
294
The oxidative transformations of some cephalosporin antibiotics have been 25-29, 38
295
identified
296
elucidated. Herein, we investigated the oxidation sites in the core structure by
, but those of the core structure compound have not yet been
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exploring its transformation byproducts during MnO2 oxidation. Five classes of
298
oxidation products, including keto-sulfone, keto-sulfoxide, sulfoxide, diketone, and
299
alcohol sulfoxide, were identified (Figure 4), and the results were further verified by
300
high-resolution MS/MS spectra (Table S8, Figure S8). In despite of the complexity of
301
these oxidation byproducts, generally oxygen addition and structural transformation
302
can occur at two sites. One site is the sulfur atom of the core structure. The lone
303
electron pair on the sulfur atom acts as a reactive nucleophile to attack the manganese
304
atom in MnO2, which is followed by an electron transfer event to form a sulfoxide
305
(S=O) or a sulfone (O=S=O)
306
formation of oxidation byproducts 1, 2, 3, and 5 in Figure 4. The second oxidation site
307
is the carbon-carbon double bond (C=C) in the core structure and its proximal
308
carboxylic acid group. The unsaturated C=C double bond could be readily attacked by
309
the nucleophilic oxygen of MnO2 to form an alcohol, diketone (through hydrolysis),
310
or ketone (through acid-catalyzed decarboxylation) (Figure 4; oxidation byproducts 1,
311
2, 4, and 5)
312
oxidation sites, such as for byproducts 1, 2, and 5.
29, 38
. This oxidation pathway was involved in the
29, 38
. Notably, the dual-oxidative transformation was observed at both
313
In addition to the core structure, the oxidation byproducts of cephalosporins
314
with one structural substituent at either the C-3 position (e.g., 7-ACA) or amine
315
position (e.g., CFX) were also investigated (Table S8, Figures S9 and S10). The
316
structural similarity among those oxidation byproducts suggests that during the
317
MnO2-based oxidation process, cephalosporins might possess similar oxidation
318
mechanisms. The proximity of the oxidation sites to the C-3 position indicates that the
319
C-3 substituent and its chemical properties, including its steric hindrance and
320
electron-withdrawing ability, might impact the oxidation process.
321
Figure 5 clearly demonstrates that the substituent R1 at the C-3 position inhibited
322
the formation of the keto-sulfone class of byproducts. The keto-sulfone class of
323
byproducts is one type of oxidation product of the core structure, and it is also found
324
in compounds such as CFX. However, when the acetyloxymethyl group was attached
325
to the C-3 position, as in 7-ACA, CFP, and CTX, the formation of keto-sulfone
326
byproducts was inhibited; only trace amounts of these byproducts were detected. This
327
result indicated that the reactivities of the oxidation sites on the core structure might
328
have been perturbed by the C-3 substituent and further supported the hypothesis that
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the C-3 substituent stabilizes the core structure, leading to a decrease in its
330
degradation rate.
331
In summary, this is the first study toward a comprehensive understanding of the
332
degradation of five cephalosporin antibiotics by MnO2. The analysis shows that these
333
compounds are easily oxidized at pH 4 in the presence of abundant MnO2. Moreover,
334
we elucidated the reactivities of the core structure and substituents and, consequently,
335
their overall effect on the reaction rate of the cephalosporins. The oxidation of CFX
336
mainly occurs in its core structure, but the oxidation of CFD, CFP, and CTX mainly
337
occurs in the substructure attached to the amine position of the core structure. In CFP,
338
the amide bond at the amine substituent is likely broken. In the case of CFZ, the
339
1-HTA moiety is not the oxidation site for CFZ degradation. Overall, the reactivities
340
of the amine substructures decreased in the following order: 2-AMTA > 2-ACAA >
341
core structure > LP ≈ 1-HTA ≈ 4-PA (inert to oxidation).
342
This study confirmed that a substituent at the C-3 position could stabilize the
343
reactivity of the core structure; however, the substituent at the amine position may
344
affect the overall degradation rate of the cephalosporins. This finding may help
345
predict the reactivity and rates of other cephalosporins with different types of
346
substructures. It is important to first compare the reactivity of the amine substituents
347
with that of the core structure; if the substituents are more reactive, they will be
348
oxidized first and thus determine the overall degradation rate of the cephalosporin. If
349
the substituent is less reactive than the core structure, oxidation will first occur at the
350
core structure. In addition, the presence of a substituent at C-3 position of the core
351
structure will very likely cause a further reduction in the rate of degradation.
352
The results from the substructure reactivity analysis in this study can possibly
353
help explain the degradation rates of cephalosporin antibiotics in other oxidation
354
processes.
355 356
357
Supporting Information
358
More information is available regarding the materials, the synthesis of δ-MnO2, and
359
the LC−MS/MS analysis process. This information is available free of charge via the
360
Internet at http://pubs.acs.org.
ASSOCIATED CONTENT
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Environmental Science & Technology
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This research was supported by funding from the Ministry of Science and Technology
364
(MOST) through the project (MOST 103-2221-E-002-240-MY5) and from National
365
Taiwan University (NTU) through the project (NTU-CCP- 106R890905).
ACKNOWLEDGMENTS
366 367
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368
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H3C
OH
O
N
O
N
S
N
C-7 H NH
H
4-PA (Substructure of CFP)
1-HTA (Substructure of CFZ)
OH
R2
S
N
C-3
N
R1
O
2-AMTA (Substructure of CTX)
OH H2N
LP (Substructure of CFX)
2-ACAA (Substructure of CFD)
(a)
CH3 N
5-M (Substructure of CFZ)
O
Oxidative transformation
NH2
S
HS
Core structure
O
HO
Acetyloxymethyl group (Substructure of CFP, CTX, 7-ACA)
Core structure
(b)
Core structure
1.0
1.0 7-ACA
0.8
0.8
1-HTA
CFZ C/C0
C/C0
0.6 CFX
0.6 LP 0.4
0.4
2-ACAA
CFD 0.2
0.2
4-PA
CFP 0.0
0.0 0
10
20
30
0
CTX
10
20
30
2-AMTA
Time (h)
Time (h)
Figure 1 Oxidation of (a) core structure, 7-ACA, CFZ, CFX, CFD, CFP, and CTX, (b) core structure and cephalosporin amine substituents (1-HTA, LP, 2-ACAA,4-PA, and 2-AMTA) ([MnO2]0 = 4 mg/L, [cephalosporin and substituents]0 = 3×10-7 M, pH 4).
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(a) 1.0
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(b) 1.2
70
1.0
60
0.8
50
0.6
C/C0
C/C0
0.8 CTX 2-AMTA
0.4
40 0.6 30 0.4
0.2
20
0.2
10
0.0
0.0 0
1
2
3 4 Time (h)
5
6
7
0 0
10
CFP
2-AMTA
CTX
4-PA from CFP degradation (nM)
Environmental Science & Technology
4-PA
20 Time (h)
4-PA
30
40
4-PA from CFP degradation
CFP
Figure 2 Oxidation tendencies of the (a) CTX and (b) CFP substructures at pH 4 ([cephalosporin]0 = 3×10-7 M).
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300
1.0 250
0.8
C/C0
150
0.4
100
0.2
50
0.0
0
0
5
10
15 Time (h)
20
25
30
35
CFD CFX LP CFX formation from CFD degradation LP formation from CFX degradation
CFX L−Phenylglycine (LP) Lp formation conc. (nM)
0.6
CFD
Byproduct formation (nM)
200
8 7 6 5 4 3 2 1 0 0
5
10
15
Time (h)
Figure 3 Oxidation tendency of the CFD, CFX, LP and the byproduct at pH 4 ([MnO2]0 = 4 mg/L, [cephalosporin and substructure]0 = 3×10-7.
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Figure 4 MnO2 oxidative byproducts of core structure.
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50
0h
Extracted ion chromatogram area (105)
45
0.66 h
2h
4h
9h
22 h
40 35 30 25 20 15 10 5 0
ks-core structure
ks-CFX
ks-7-ACA
Figure 5 Formation of keto-sulfone (ks) byproducts from cephalosporins.
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ks-CFP
ks-CTX