Subscriber access provided by The Chinese University of Hong Kong
Article
Enantioselective Metabolism of Flufiprole in Rat and Human Liver Microsomes Chunmian Lin, Yelong Miao, Mingrong Qian, Qiang Wang, and Hu Zhang J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.5b05853 • Publication Date (Web): 03 Mar 2016 Downloaded from http://pubs.acs.org on March 12, 2016
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Journal of Agricultural and Food Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 21
Journal of Agricultural and Food Chemistry
1
Enantioselective Metabolism of Flufiprole in Rat and
2
Human Liver Microsomes
3
Chunmian Lin , Yelong Miao , Mingrong Qian , Qiang Wang , Hu Zhang
†
†
4 5
†
‡
‡
*,‡
College of Biological and Environmental Engineering, Zhejiang University of Technology,
Hangzhou 310014, China ‡
6
Institute of Quality and Standard for Agricultural Products, Zhejiang Academy of Agricultural
7
Sciences, Hangzhou 310021, China
8
ABSTRACT: The enantioselective metabolism of flufiprole in rat and human liver
9
microsomes in vitro was investigated in this study. The separation and determination
10
were performed using a liquid chromatography system equipped with a triple
11
quadrupole mass spectrometer and a Lux Cellulose-2 chiral column. The
12
enantioselective metabolism of rac-flufiprole was dramatically different in rat and
13
human liver microsomes in the presence of β-Nicotinamide adenine dinucleotide
14
phosphate regenerating system. The half-life (t1/2) of flufiprole in rat and human liver
15
microsomes were 7.22 and 21.00 min, respectively, for R-(+)-flufiprole, while the
16
value were 11.75 and 17.75 min, respectively, for S-(-)-flufiprole. In addition, the Vmax
17
of R-(+)-flufiprole was about 3-fold of S-(-)-flufiprole in rat liver microsomes, while
18
its value in case of S-(-)-flufiprole was about 2-fold of R-(+)-flufiprole in human liver
19
microsomes. The CLint of rac-flufiprole also showed opposite enantioselectivy in rat
20
and human liver microsomes. The different compositions and contents of
21
metabolizing enzyme in the two liver microsomes might be the reasons for the
22
difference in the metabolic behavior of the two enantiomers.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
23
KEYWORDS:
24
HPLC-MS/MS
flufiprole,
enantioselective
metabolism,
ACS Paragon Plus Environment
Page 2 of 21
liver
microsomes,
Page 3 of 21
Journal of Agricultural and Food Chemistry
25
INTRODUCTION
26
Phenylpyrazole insecticides are widely used to protect a variety of crops, including
27
rice, fruits and vegetables, from insects such as ants, beetles, ticks and cockroaches1-3.
28
Another common phenylpyrazole insecticide, fipronil, has been banned in China in
29
2009, because of its high toxicity towards aquatic organisms, such as fish and
30
shrimp4-6. Flufiprole (or butene-fipronil), (R,S)-1-[2,6-dichloro-4-(trifluoromethyl)
31
phenyl]
32
sulfinyl]-pyrazole-3-carbonitrile (Figure 1), is a new kind of phenylprazole insecticide
33
introduced in 2002 by Dalian Raiser Pesticides Co., Ltd., China. It is a modified form
34
of fipronil with a similar effect against a broad spectrum of insect pests and has much
35
lower toxicity7-9. Both flufiprole and fipronil have a chiral sulfur atom consisting of
36
two enantiomers. In fact, although enantiomers have exactly the same physical and
37
chemical properties, they behave differently in bioactivity10-11, toxicity10,12 or
38
degradation10,13-14 when exposed to a chiral environment. In recent years, with the
39
intensive study of chiral pesticides all over the world, many papers about the
40
enantioselective degradation of chiral pesticides have been published15-18. For instance,
41
S-fipronil has been shown to degrade faster than R-fipronil in earthworms and natural
42
soil18. To our knowledge, there is no such report about the study on the metabolic
43
behavior of flufiprole at the enantiomer level, which may lead to potential
44
environmental risks.
-5-[N-(methallyl)
amino]-4-[(trifluoro-methyl)
45
Recently, it is popular to use in vitro models in pharmacology, toxicology and
46
toxicokinetic experiments, because there are fewer animals needed, fewer endogenous
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
47
interfering substrates and much shorter experiment time compared with in vivo
48
studies19-23. Liver is the major organ for the metabolism of many xenobiotics, where
49
the majority of drug metabolic enzymes exist. In previous studies, many researchers
50
have reported the stereoselective degradation of many chiral pesticides in rat, rabbit
51
and human liver microsomes (HLMs), including triazole fungicides24-25, benalaxyl26
52
and fluroxypyr methylheotyl ester27. Taking benalaxyl enantiomers as an example, the
53
t1/2 of R-benalaxyl in rat liver microsomes (RLMs) was about 2-fold of S-benalaxyl.
54
However, R-benalaxyl degraded faster than S-benalaxyl in rabbit liver microsomes, at
55
the same time there was no chiral inversion between R- and S-benalaxyl in both liver
56
microsomes26. To evaluate the environmental risk of flufiprole comprehensively, it is
57
necessary to evaluate the enantioselective metabolism of flufiprole in different liver
58
microsomes.
59
In this study, the metabolic behaviors of rac-flufiprole in RLMs and HLMs were
60
investigated to determine that if similar enantioselectivity occurred. The
61
determination of chiral flufiprole was achieved in high-performance liquid
62
chromatography-tandem mass spectrometry (HPLC-MS/MS) equipped with a Lux
63
Cellulose-2 chiral column. The significant kinetic parameters of the enantiomers, such
64
as half-life (t1/2), maximum velocity of metabolism (Vmax) and Michaelis constant
65
(CLint), were also calculated to explore the enantioselective behaviors of flufiprole.
66
The results might be helpful to understand the risks associated with flufiprole to
67
humans, animals and the environment.
68
MATERIALS AND METHODS
ACS Paragon Plus Environment
Page 4 of 21
Page 5 of 21
Journal of Agricultural and Food Chemistry
69
Chemicals and Materials. Flufiprole with a purity of 96.6% was obtained from
70
Dalian Raiser Pesticides Co., Ltd (Dalian, China). Two enantiomers of flufiproles
71
with purity ≥98.0% were obtained from Daicel (Shanghai, China). HPLC-grade
72
methanol and acetonitrile were purchased from Merck (Darmstadt, Germany). A stock
73
solution of racemic standard was prepared in methanol and stored at 4 °C. Working
74
standard solutions were obtained by dilutions of the stock solution in methanol.
75
Purified water was produced by a Milli-Q water purification system (Millipore
76
Bedford,
77
regenerating system, rat and human liver microsomes (20 mg/mL, 0.5 mL) were
78
purchased from XenoTech (Lenexa, KS). Acetic acid (99.7% purity) was purchased
79
from Sigma-Aldrich. All other chemicals and solvents were of analytical grade and
80
purchased from commercial sources. The chiral analytical column, cellulose tris
81
(3-chloro-4methylphenycarbamate)
82
Phenomenex (Torrance, CA), and the column was sized 150 mm × 2.0 mm i.d. and
83
packed with 3 µm particles.
MA).
β-Nicotinamide
adenine
(Lux
dinucleotide
Cellulose-2),
phosphate
was
(NADPH)
purchased
from
84
Incubation in Liver Microsomes. Substrate-depletion studies in vitro were
85
performed by incubation of rac-flufiprole (10 µM) for rat liver microsomes and
86
rac-flufiprole (5 µM) for human liver microsomes with 0.5 mg of microsomal protein
87
in 50 mM Tris-HCl buffer (pH 7.4) with 5.0 mM MgCl2. The concentrations of
88
flufiprole were chosen based on pre-experiments. Flufiprole was prepared in methanol
89
and added to the incubation media with the final methanol concentration not
90
exceeding 1.0% v/v. All reaction mixtures were preincubated in a heated water bath at
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
91
37 °C for 5 min before initiation of the reaction by addition of NADPH at a final
92
reaction concentration of 1.0 mM. Incubation mixtures without NADPH served as
93
controls (with deactivated microsomes). The final total reaction volume was 0.5 mL.
94
After incubation in a water bath (37 °C) for 5-90 min, the reactions were terminated
95
by adding 0.5 mL of ice-cold methanol and the sample was vortexed for 5 min. After
96
centrifugating at 4000 rpm for 5 min, the supernatant was filtered through the
97
membrane (PTFE, 0.22 µm) for enatioselective HPLC-MS/MS analysis. All
98
experiments were performed as three independent trials.
99
Kinetic metabolism Assays. The in vitro metabolic kinetics of flufiprole was
100
studied by adding variable concentrations of flufiprole stock solution to the incubation
101
mixtures. The final substrate concentrations were from 2 to 100 µM and the
102
incubation time was 10 min with liver microsomes (0.5 mg protein/mL). Then, the
103
sample preparation was performed according to the section above. The Vmax and Km
104
values were calculated from nonlinear regression analysis of experimental data
105
according to the Michaelis-Menten equation. Intrinsic clearance (CLint) was calculated
106
as a ratio of the Vmax and to the Km. Nonlinear regression analysis was performed with
107
Origin pro 8.5.
108
Enantioselective HPLC-MS/MS Analysis. The determination of flufiprole was
109
achieved on a Surveyor liquid chromatography (Thermo Fisher Scientific, Waltham,
110
MA, USA) equipped with a triple-quadrupole mass spectrometer. Xcalibur 2.0.7
111
(Thermo Fisher Scientific) software was used to process the quantitative data obtained
112
from calibration standards and samples. Complete chiral separation of flufiprole was
ACS Paragon Plus Environment
Page 6 of 21
Page 7 of 21
Journal of Agricultural and Food Chemistry
113
achieved on a Lux Cellulose-2 chiral column28. The mobile phase consisted of 65%
114
(v/v) (A) acetonitrile and 35% (v/v) (B) 2 mM ammonium acetate aqueous solution
115
containing 0.1% formic acid. The flow rate was set to 0.3 mL/min, and the injection
116
volume was 5 µL. The ESI-MS/MS interface (electrospray ionization coupled with
117
tandem mass spectrometry) was operated in the negative ion mode. ESI source
118
conditions were as follows: source temperature, 110 °C; desolvation temperature,
119
500 °C; desolvation gas (N2) flow rate, 12 mL/min; cone gas (N2) flow rate, 40 mL/Hr;
120
and collision gas (Ar) flow rate, 0.15 mL/min. Multiple reaction monitoring (MRM)
121
was applied for flufiprole determination; transition m/z 488.9→288 was used for
122
quantification, and m/z 488.9→249.9 was used for confirmation.
123
Method validation. Calibration standards were prepared by adding a series of
124
working standard solution of rac-flufiprole into the blank matrix (BM, the extracts
125
from the bovine serum protein). The preparing and extracting processes were the same
126
as incubation samples. The calibration curves were generated by plotting peak areas
127
of quantification ion transition against the concentration of each enantiomer from 0.1
128
to 50 µM with regression analysis. Linear regression analysis was performed with
129
Microsoft Excel 2007. The precision and accuracy of the method were calculated by
130
analyzing calibration standards at three concentration levels (0.5, 10 and 50 µM for
131
each flufiprole enantiomer) and comparing the predicted concentration (obtained from
132
the calibration curve) to the actual concentration of each enantiomer spiked in the BM.
133
Both intraday and interday precisions are presented as relative standard deviation
134
(RSD [SD/mean] × 100%). Limit of detection LOD (signal-to-noise ratio [S/N]=3)
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
135
and limit of quantification LOQ (S/N=10) were determined with the method using the
136
matrix-matched standards.
137
RESULTS AND DISCUSSION
138
Assay validation. Using m/z 488.9→288 as the quantification transition, linear
139
calibration curves were obtained over the concentration range of 0.1-50 µM in blank
140
matrix for R-flufiprole (y = 6.9227x × 10^4 - 29.9224, R2 = 0.9994) and S-flufiprole (y
141
= 6.9938x × 10^4 – 14.3144, R2 = 0.9996). The RSD was less than 7% at all
142
concentration.
143
The precision and accuracy of intraday and interday, expressed with the RSD and
144
the ratios of predicted concentration to acctural concentration, was shown in Table 1.
145
For both enantiomers, the accuracies obtained were in the acceptable range of 90.3%-
146
98.7% and the RSD ranged from 1.8% to 5.7%. The main recoveries ranged from
147
97.5% to 100.8% with 2.4%-6.9% RSD (Table 2). The LODs for both enantiomers
148
were estimated to be 0.005 µM, while the LOQs were 0.015 µM. In addition, the
149
extraction procedure did not cause epimerize of flufiprole enantiomers as shown in
150
Figure 2 F-G.
151
Data Ananlysis. Under the HPLC-MS/MS condition, the enantiomers of flufiprole
152
were separated completely on a Lux Cellulose-2 column (as shown in Figure 2A), and
153
no endogenous interference peaks eluted at retention times in blank samples (without
154
insecticides). The order elution was confirmed to be S-(-)-flufiprole for peak 1 and
155
R-(+)-flufiprole for peak 2 based on published data28.
156
The enantiomer fraction (EF) was used to measure the enantioselectivity of the
ACS Paragon Plus Environment
Page 8 of 21
Page 9 of 21
Journal of Agricultural and Food Chemistry
157
flufiprole enantiomers during incubation in the liver microsomes. EF was calculated
158
from the peak areas for the signals, defined by eq. 1. The EF values ranged from 0 to
159
1 with EF=0.5 representing the racemic mixture according to the equation.
160
EF= (S)-(-)-enantiomer / [(R)-(+)-enantiomer + (S)-(-)-enantiomer]
161
The metabolism of rac-flufiprole and its enantiomers was assumed to follow the
162
first-order kinetics model, and the degradation constants (k) were calculated by eq. 2
163
using regression analysis. The half-life (t1/2, min) was estimated from eq. 3. C = C0e-kt
164
t1/2 = ln2/k = 0.693/k
165 166 167
(1)
(2) (3)
C and C0 are the concentrations of the R-(+)- or S-(-)-enantiomer at time t and time 0, respectively.
168
Nonlinear regression of substrate concentration versus reaction velocity curves
169
were analyzed using Origin 8.5 software by fitting the experimental data to the
170
Michaelis-Menten equation. The in vitro kinetic parameters were determined by
171
fitting the data to eq. 4, and the intrinsic metabolic clearance (CLint) was calculated by
172
eq. 5.
173
V=Vmax×S/(Km+S)
(4)
174
CLint=Vmax/Km
(5)
175 176
V, S, Vmax and Km represent the velocity of metabolism, substrate concentration, maximum velocity of metabolism and Michaelis constant, respectively.
177
Metabolism of Racemic Flufiprole in RLMs and HLMs. The rac-flufiprole was
178
dissipated rapidly in RLMs and HLMs with NADPH, and did not degradate obviously
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
179
in the absence of NADPH. Typical chromatograms of extracts from the samples after
180
10 min incubation are displayed in Figures 2B-E. The concentrations of two
181
enantiomers were different from each other after incubation in RLMs and HLMs. The
182
R-(+)-flufiprole degraded faster than its antipode in RLMs, in contrast, the
183
S-(-)-flufiprole degraded faster in HLMs.
184
Concentration-time curves of R-(+)- and S-(-)-flufiprole after incubation in RLMs
185
with rac-flufiprole at 10 µM and HLMs with rac-flufiprole at 5 µM were shown in
186
Figure 3. The results demonstrated that the metabolisms of each enantiomer in RLMs
187
and HLMs were in accordance with the first-order kinetics decay model. Rate
188
constants (k), correlation coefficients (R2) and half-lives (t1/2) were calculated (Table
189
3). It was shown that the half-life t1/2 of R-(+)-flufiprole was 7.22 and 21 min in
190
RLMs and HLMs, while the half-life t1/2 of S-(-)-flufiprole was 11.75 and 15.75 min,
191
respectively. Thus, metabolism of R-(+)- and S-(-)-flufiprole was much faster in
192
RLMs, and indicated opposite enantioselectivity in RLMs and HLMs.
193
The enantioselective metabolic behavior could also be conducted by EFs. In the
194
experiment, the EF value of flufiprole increased from the initial 0.50 to 0.71 rapidly in
195
RLMs because R-(+)-flufiprole degradated much faster than S-(-)-flufiprole under the
196
same concentration. Then with the concentration of R-(+)-flufiprole decreasing
197
quickly, the degradation rate of R-(+)-flufiprole also decreased until it became smaller
198
than its value of S-(-)-flufiprole. As a result, the EF value decreased to 0.62
199
(concentration RS) gradually in HLMs, indicating that there
ACS Paragon Plus Environment
Page 10 of 21
Page 11 of 21
Journal of Agricultural and Food Chemistry
201
was significant enantioselectivity in the two kinds of liver microsomes.
202
Enzyme Kinetics of Flufiprole Enantiomers. The Michaelis-Menten model was
203
applied to different initial concentrations (5-100 µM) of rac-flufiprole using RLMs
204
and HLMs as examples to elucidate the mechanism of stereoselective toxicokinetics
205
of flufiprole. Metabolic rate constants (apparent Km and Vmax) were determined after a
206
10 min incubation period in liver microsomes. The Michalis-Menten plots are shown
207
in Figure 4. By nonlinear regression analysis, the values of Km, Vmax and CLint were
208
calculated and are shown in table 4. The Vmax of R-(+)-flufiprole (3906.3±80.6
209
µM/min/mg) was about 3-fold of S-(-)-flufiprole (1430.6±52.9 µM/min/mg) after
210
incubation for 10 min in RLMs, however, the opposite trendency was found after
211
incubation in HLMs. For the CLint, the ability of an organism to eliminate a particular
212
chemical demonstrated diversity, the CLint of rac-flufiprole also showed opposite
213
enantioselectivy in RLMs and HLMs. Besides, the CLint of R-(+)-flufiprole and
214
S-(-)-flufiprole in RLMs was higher than that in HLMs. These enzyme kinetic results
215
suggested that the rat liver microsomes in vitro had a stronger potency to eliminate
216
flufiprole than the human liver microsomes. Significant differences were found for the
217
stereoselective metabolism of rac-flufiprole in RLMs and HLMs.
218
In conclusion, we investigated the enantioselective metabolism of rac-flufiprole in
219
RLMs and HLMs. The degradation velocity of flufiprole in HLMs was slower than
220
that in RLMs. Moreover, there was significant opposite enantioselective behavior for
221
the metabolism of flufiprole enantiomers in the two liver microsomes. Some
222
studies24-27 verified that other fungicides, such as (2RS,3RS)-paclobutrazol,
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
223
tebuconazole, benalaxyl and fluroxypyr methylheotyl ester, exhibited stereoselectivity
224
of metabolism in liver microsomes. The reason for the difference in the metabolism
225
behavior of the two enantiomers might be the different compositions and contents of
226
metabolizing enzyme (especially cytochrome P450) in various species liver
227
microsomes26, 29-30. Future studies should be focused on the isoforms of cytochrome
228
P-450 (CYP) that contribute to its stereoselectivy. These data should be important to
229
elucidate the mechanism of stereoselective toxicokinetics of flufiprole in RLMs and
230
HLMs, and contribute to environmental and public health.
231
AUTHOR INFORMATION
232
Corresponding Author *
233
E-mail
[email protected] 234
Notes
235
The authors declare no competing financial interest.
236
ACKNOWLEDGEMENT
237
We acknowledge financial support from the National Natural Science Foundation of
238
China (21207118), the Project of Science and Technology Plan of Zhejiang Province,
239
China (2014C37103), and the Natural Science Foundation of Zhejiang Province,
240
China (Y15B070017).
241
REFENENCES
242
(1) Raveton, M.; Aajoud, A.; Willison, J. C.; Aouadi, H.; Tissut, M.; Ravanel, P.
243
Phototransformation of the insecticide fipronil: identification of novel photoproducts and evidence
244
for an alternative pathway of photodegradation. Environ. Sci. Technol. 2006, 40, 4151-4157.
245
(2) Kitulagodage, M.; Isanhart, J.; Buttemer, W. A.; Hooper, M. J.; Astheimer, L. B. Fipronil
ACS Paragon Plus Environment
Page 12 of 21
Page 13 of 21
Journal of Agricultural and Food Chemistry
246
toxicity in northern bobwhite quail Colinus virginianus: Reduced feeding behavior and sulfone
247
metabolite formation. Chemophere 2011, 83, 524-530.
248
(3) Zhang, Q.; Shi, H. H.; Gao, B. B.; Tian, M. M.; Hua, X. D.; Wang, M. H. Enantioseparation
249
and determination of the chiral phenylpyrazole insecticide ethiprole in agricultural and
250
environmental samples and its enantioselective degradation in soil. Sci. Total. Environ. 2016, 542,
251
845-853.
252
(4) Gunasekara, A. S.; Truong, T.; Goh, K. S.; Spurlock, F.; Tjeerdema, S. Environmental fate
253
and toxicology of fipronil. J. Pestic. Sci. 2007, 32, 189-199.
254
(5) Beggel, S.; Werner, I.; Connon, R. E.; Geist, J. P. Impacts of the phenylpyrazole insecticide
255
fipronil on larval fish:Time-series gene transcription responses in fathead minnow (Pimephales
256
promelas) following short-term exposure. Sci. Total. Environ. 2012, 426, 160-165.
257
(6) Wu, J.; Lu, J.; Lu, H.; Lin, Y. J.; Wilson, P. C. Occurrence and ecological risks from fipronil
258
in aquatic environments located within residential landscapes. Sci. Total. Environ. 2015, 519,
259
139-147.
260
(7) Niu, H. T.; Yan, L.; Zhong, J. P.; Wei, S. J.; Luo, W. C. A comparison on toxicity of fipronil
261
and butane-fipronil against diamondback moth larvae in laboratory. Agrochem. Res. App. 2007, 11,
262
28-30.
263
(8) Yu, R. X.; Wang, Y. H.; Wu, C. X.; Cang, T.; Chen, L. P.; Wu, S. G.; Zhao, X. P. Acute
264
toxicity and risk assessment of butane-fipronil to silkworm, bomyx mori. Asian J. Ecotoxicol.
265
2012, 7, 639-645.
266
(9) Arain, M. S.; Hu, X. X.; Li, G. Q. Assessment of toxicity and potential risk of butane-fipronil
267
using Drosophila melanogaster, in comparison to nine conventional insecticides. Bull. Environ.
268
Contam. Toxicol. 2014, 92, 190-195.
269
(10) Zhang, Q.; Hua, X. D.; Shi, H. Y.; Liu, J. S.; Tian, M. M; Wang, H. M. Enantioselective
270
bioactivity, acute toxicity and dissipation in vegetables of the chiral triazole fungicide flutriafol. J.
271
Hazard. Mater. 2015, 284, 65-72.
272
(11) Sun, J. Q.; Zhang, A. P.; Zhang, J.; Xie, X. M.; Liu, W. P. Enantiomeric resolution and
273
growth-retardant activity in rice seedlings of uniconazole. J. Agric. Food Chem. 2012, 60,
274
160-164.
275
(12) Lin, K. D.; Liu, W. P.; Li, L.; Gan, J. Single and joint acute toxicity of isocarbophos
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
276
Enantiomers to Daphnia magna. J. Agric. Food Chem. 2008, 56, 4273-4277.
277
(13) Wang, Y.; Xu, L.; Li, D. Z.; Teng, M. M.; Zhang, R. K.; Zhou, Z. Q.; Zhu, W. T.
278
Enantioselective bioaccumulation of hexaconazole and its toxic effects in adult zebrafish (Danio
279
rerio). Chemosphere 2015, 138, 798-805.
280
(14) Ribeiro, A. R.; Afonso, C. M.; Castro, P. M. L.; Tiritan, M. E. Enantioselective
281
biodegradation of pharmaceuticals, alprenolol and propranolol, by an activated sludge inoculums.
282
Ecotox. Environ. Safe. 2013, 87, 108-114.
283
(15) Tange, S.; Fujimoto, N.; Uramaru, N.; Sugihara, K.; Ohta, S.; Kitamura, S. In vitro
284
metabolism of cis- and trans-permethrin by rat liver microsomes, and its effect on estrogenic and
285
anti-androgenic activities. Environ. Toxicol. Phar. 2014, 37, 996-1005.
286
(16) Xu, Y. X.; Zhang, H.; Zhuang, S. L.; Yu, M.; Xiao, H.; Qian, M. R. Different enantioselective
287
degradation of pyraclofos in soils. J. Agric. Food Chem. 2012, 60, 4173-4178.
288
(17) Wang, X. Q.; Qi, P. P.; Zhang, H.; Xu, H.; Wang, X. Y.; Li, Z.; Wang, Z. Z.; Wang, Q.
289
Enantioselective analysis and dissipation of triazole fungicide penconazole in vegetables by liquid
290
chromatography-tandem mass spectrometry. J. Agric. Food Chem. 2014, 62, 11047-11053.
291
(18) Qu, H.; Wang, P.; Ma, R. X.; Qiu, X. X.; Xu, P.; Zhou, Z. Q.; Liu, D. H. Enantioselective
292
toxicity, bioaccumulation and degradation of the chiral insecticide fipronil in earthworms (Eisenia
293
feotida). Sci. Total. Environ. 2014, 486, 415-420.
294
(19) Lipscomn, J. C.; Poet, T. S. In vitro measurements of metabolism for application in
295
pharmacokinetic modeling. Pharmacol. Therapeut. 2008, 118, 82-103.
296
(20) Gómez, A. B.; Erratico, C. A.; Eede, N. V. D.; Ionas, A. C.; Leonards, P. E. G.; Covaci, A. In
297
vitro metabolism of 2-ethylhexyldiphenyl phosphate (EHDPHP) by human liver microsomes.
298
Toxicol. Lett. 2015, 232, 203-212.
299
(21) Eede, N. V. D.; Tomy, G.; Tao, F.; Halldorson, T.; Harrad, S.; Neels, H.; Covaci, A. Kinetics
300
of tris (1-chloro-2-propyl) phosphate (TCIPP) metabolism in human liver microsomes and serum.
301
Chemosphere 2016, 144, 1299-1305.
302
(22) Di, L.; Keefer, C.; Scott, D. O.; Strelevitz, T. J.; Chang, G.; Bi, Y. A.; Lai, Y. R.; Duckworth,
303
J.; Fenner, K.; Troutman, M. D.; Obach, R. S. Mechanistic insights from comparing intrinsic
304
clearance values between human liver microsomes and hepatocytes to guide drug design. Eur. J.
305
Med. Chem. 2012, 57, 441-448.
ACS Paragon Plus Environment
Page 14 of 21
Page 15 of 21
Journal of Agricultural and Food Chemistry
306
(23) Zielinski, J.; Mevissen, M. Inhibition of in vitro metabolism of testosterone in human, dog
307
and horse liver microsomes to investigate species differences. Toxicol. In Vitro. 2015, 29, 468-478.
308
(24) Wu, S. C.; Yu, M.; Zhang, H.; Han, J. Z.; Qian, M. R. Enantioselective degradation of (2RS,
309
3RS)-paclobutrazol in rat liver microsomes. Chirality 2015, 27, 344-348.
310
(25) Shen, Z. G.; Zhu, W. T.; Liu, D. H.; Xu, X. Y.; Zhang, P.; Zhou, Z. Q. Stereoselective
311
degradation of tebuconazole in rat liver microsomes. Chirality 2012, 24, 67-71.
312
(26) Zhang, P.; Zhu, W. T.; Dang, Z. H.; Shen, Z. G.; Xu, X. Y.; Huang, L. D.; Zhou, Z. Q.
313
Stereoselective metabolism of benalaxyl in liver microsomes from rat and rabbit. Chirality 2011,
314
23, 93-98.
315
(27) Xu, X. Y.; Jiang, J. Z.; Wang, X. R.; Shen, Z. G.; Li, R. H.; Zhou, Z. Q. Stereoselective
316
metabolism and toxicity of the herbicide fluroxypyr methylheptyl ester in rat hepatocytes.
317
Chirality 2011, 23, 960-866.
318
(28) Tian, M. M.; Zhang, Q.; Shi, H.Y.; Gao, B. B.; Hua, X. D.; Wang, M. H. Simultaneous
319
determination of chiral pesticide flufiprole enantiomers in vegetables, fruits, and soil by
320
high-performance liquid chromatography. Anal. Bioanal. Chem. 2015, 407, 3499-3507.
321
(29) Narimatsu, S.; Kobayashi, N.; Masubuchi, Y.; Horie, T.; Kakegawa, T.; Kobayashi, H.;
322
Hardwick, J. P.; Gonzalez, F. J.; Shimada, N.; Ohmori, S.; Kitada, M.; Asaoka, K.; Kataoka, H.;
323
Yamamoto, S.; Satoh, T. Species difference in enantioselectivity for the oxidation of propranolol
324
by cytochrome P450 2D enzymes. Chem. Biol. Interact. 2000, 127, 73-90.
325
(30) Arora, S.; Taneja, I.; Challagundla, M.; Raju, K. S. R.; Singh, S. P.; Wahajuddin, M. In vivo
326
prediction of CYP-mediated metabolic interaction potential of formononetin and biochanin A
327
using in vitro human and rat CYP450 inhibition data. Toxicol. Lett. 2015, 239, 1-8.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 16 of 21
FIGURE CAPTIONS NC
CN Cl
F 3C
N N HN Cl H3C
O
O S CF3 CH2
S F3C
H2C
N N NH Cl
Cl
CF3
CH3
mirror Figure 1. Chemical structure of flufiprole enantiomers (Asterisk indicated the chiral center).
ACS Paragon Plus Environment
Page 17 of 21
Journal of Agricultural and Food Chemistry
Figure 2. Representative HPLC-MS/MS chromatograms of (A) standard flufiprole, extract from (B) RLMs with 10 µM rac-flufiprole and (C) HLMs with 5 µM rac-flufiprole after incubation for 10min in the absence of NADPH, extract from (D) RLMs with 10 µM rac-flufiprole and (E) HLMs with 5 µM rac-flufiprole after incubation for 10min with NADPH, extract from RLMs with (F-G) individual flufiprole enantiomer.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Figure 3. Degradation of (A) rac-flufiprole (10 µM) in RLMs, (C) rac-flufiprole (5 µM) in HLMs for 90 min. The changes of EF values in (B) RLMs and (D) HLMs.
Figure 4. Michaelis-Menten kinetic analyses of rac-flufiprole (A) in RLMs and (B) in HLMs after 10min incubation.
ACS Paragon Plus Environment
Page 18 of 21
Page 19 of 21
Journal of Agricultural and Food Chemistry
TABLE CAPTIONS Table 1. . Accuracy and Precision of Assay Method for Measurement of Flufiprole Enantiomers (n = 6) Intraday Concentration (µM) R-flufiprole 0.1 10 50 S-flufiprole 0.1 10 50
Interday
Accuracy (%)
RSD (%)
Accuracy (%)
RSD (%)
91.9 96.7 97.5
1.8 5.0 5.7
90.3 93.0 95.5
1.4 4.5 4.7
91.9 95.2 97.7
2.7 4.7 3.5
92.6 94.9 98.7
2.3 5.4 4.9
Table 2. . Method Recovery for Meassurement of Flufiprole Enantiomers (n = 3) R-flufiprole
S-flufiprole
Concentration (µM)
Accuracy (%)
RSD (%)
Accuracy (%)
RSD (%)
0.1 10 50
100.4 97.5 100.8
2.4 2.6 3.1
99.1 97.7 100.7
2.7 6.9 2.5
Table 3 . Degradation Rate Constant (k), Half-Life (t1/2) and Correlation Coefficients (R2) Values for the Metabolism of rac-Flufiprole in Liver Microsomes Liver microsomes
spiked compd
RLMs
rac-flufiprole
HLMs
rac-flufiprole
detected compd
k (min-1)
t1/2(min)
R2
R-(+)-flufiprole S-(-)-flufiprole R-(+)-flufiprole S-(-)-flufiprole
0.096 0.059 0.033 0.044
7.22 11.75 21.00 15.75
0.885 0.889 0.991 0.915
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 20 of 21
Table 4. . Metabolic Parameters of rac-Flufiprole Incubated in RLMs and HLMs Sample RLMs R-(+)-flufiprole S-(-)-flufiprole HLMs R-(+)-flufiprole S-(-)-flufiprole
Vmax (µM/min/mg)
Km (µM)
CLint (mL/min/mg protein)
R2
3906.3±80.6 1430.6±52.9
43.12±1.53 17.22±0.84
90.58 83.06
0.99 0.99
961.5±52.7 1785.7±86.3
27.12±2.49 35.18±2.34
35.45 50.76
0.98 0.99
ACS Paragon Plus Environment
Page 21 of 21
Journal of Agricultural and Food Chemistry
ABSTRACT GRAPHICS
ACS Paragon Plus Environment