Subscriber access provided by UNIVERSITY OF THE SUNSHINE COAST
Agricultural and Environmental Chemistry
Mechanistic insights into stereospecific bioactivity and dissipation of chiral fungicide triticonazole in agricultural management Qing Zhang, Zhaoxian Zhang, Bowen Tang, Beibei Gao, Mingming Tian, Edmond Sanganyado, Hai-yan Shi, and MingHua Wang J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b01771 • Publication Date (Web): 26 Jun 2018 Downloaded from http://pubs.acs.org on June 27, 2018
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 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 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.
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 35
Journal of Agricultural and Food Chemistry
1
Mechanistic insights into stereospecific bioactivity and
2
dissipation of chiral fungicide triticonazole in agricultural
3
management
4
Qing Zhang †, ‡, Zhaoxian Zhang †, ‡, Bowen Tang §, Beibei Gao
5
Edmond Sanganyado ┴, Haiyan Shi †, ‡, Minghua Wang †, ‡, *,
6
†
7
University, Nanjing 210095, P. R. China
8
‡
9
Application, Nanjing 210095, P. R. China
†, ‡
, Mingming Tian #,
Department of Pesticide Science, College of Plant Protection, Nanjing Agricultural
State & Local Joint Engineering Research Center of Green Pesticide Invention and
10
§
11
China
12
#
13
Environment, Nanjing University, Nanjing 210023, P. R. China
14
┴
15
*Corresponding Author: E-mail:
[email protected]. Phone: +86 25 84395479.
16
Fax: +86 25 84395479.
College of Pharmaceutical Sciences, Xiamen University, Xiamen 361102, P. R.
State Key Laboratory of Pollution Control & Resource Reuse, School of the
Marine Biology Institute, Shantou University, Shantou 515063, P. R. China
1
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
17
ABSTRACT:
18
Research interest on chiral pesticides has increased probably because
19
enantiomers often exhibit different environmental fate and toxicity. An investigation
20
into the enantiomer-specific bioactivity of chiral triticonazole enantiomers in
21
agricultural systems revealed intriguing experimental and theoretical evidence. For
22
nine of the phytopathogens studied (Rhizoctonia solani, Fusarium verticillioide,
23
Botrytis cinerea (strawberry and tomato), Rhizoctonia cereali, Alternaria solani,
24
Gibberella zeae, Sclerotinia sclerotiorum, Pyricularia grisea), the fungicidal activity
25
data showed (R)-triticonazole was 3.11-82.89 times more potent than the
26
(S)-enantiomer. Furthermore, (R)-triticonazole inhibited ergosterol biosynthesis and
27
cell membrane synthesis more 1.80-7.34 times higher than its antipode. Homology
28
modeling and molecular docking studies suggested the distinct bioactivities of the
29
enantiomers of triticonazole were probably due to their different binding modes and
30
affinities to CYP51b. However, field studies demonstrated that (S)-triticonazole was
31
more persistent than (R)-triticonazole in fruits and vegetables. The results showed that
32
application of pure (R)-triticonazole, with its high bioactivity and relatively low
33
resistance risk, instead of the racemate in agricultural management would reduce the
34
application dosage required to eliminate carcinogenic mycotoxins and any
35
environmental risks associated with this fungicide, yielding benefits in food safety
36
and environmental protection.
37
KEYWORDS: chiral triticonazole; enantioselective bioactivities; stereoselective
38
dissipation; agricultural management; environmental protection
39 2
ACS Paragon Plus Environment
Page 2 of 35
Page 3 of 35
Journal of Agricultural and Food Chemistry
40
INTRODUCTION
41
Chirality is a ubiquitous concept in many scientific fields, including biology,
42
medicine, environmental science, chemistry, and agriculture 1. Numerous chiral
43
molecules generally interact with enzymes and biological receptors in an
44
enantioselective fashion 2. The tertiary stereocenters of chiral enantiomers are
45
important core structures which affect the molecule’s biological and pharmacological
46
properties
47
binding to one of the enantiomers in biological systems, which might lead to distinct
48
therapeutic or adverse effects
49
variety of plant pathogens for the purpose of crop protection. This class of fungicides
50
contains one or two chiral centers, but they are primarily applied as mixtures of
51
racemates for chemosynthetic and economic reasons. These compounds are known to
52
inhibit a cytochrome P450-dependent lanosterol 14α-demethylase (CYP51) via a
53
mechanism in which the heterocyclic nitrogen atom binds to the heme iron atom in
54
the binding site of the enzyme 8. It has been shown that the enantiomers of triazole
55
fungicides display dramatically different toxicities and biological activities in chiral
56
environments
57
systematic biological evaluation of all enantiomers for pharmaceutical candidates
58
Therefore, it is necessary to understand the bioactivity of each pure enantiomer for
59
chiral triazole fungicides and to study the molecular mechanisms of their
60
stereospecific bioactivity to gain a better understanding of plant diseases 11, 12.
61
3-6
. Chiral macromolecules might exhibit preferential metabolism of or
9, 10
2, 7
. Triazole fungicides are widely used to combat a
. Additionally, the US Food and Drug Administration requires a 2, 4
.
Plant pathogens cause extensive annual yield losses of staple crops worldwide 13. 3
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 4 of 35
62
In addition, some of these pathogens not only reduce the yield and quality of infected
63
grain, but also produce a number of mycotoxins, such as deoxynivalenol and
64
zearalenone
65
mammals and negatively impact human health. Triazole fungicides are well known
66
for their excellent antifungal activity and relatively low resistance risk compared to
67
other commonly used fungicides, and they are thus considered the mainstay of
68
modern fungicides in agrochemical applications 15. Studies so far have shown that the
69
degradation of chiral triazole fungicides is commonly enantioselective in soil
70
For example, the microbial transformation of triadimefon to triadimenol was
71
enantioselective, with the (S)-enantiomer being preferentially transformed in soils 18.
72
In addition, (R)-flutriafol exhibited a longer elimination half-life than its antipode,
73
resulting in the accumulation of the (S)-isomer in rabbits
74
enantioselective plant uptake and accumulation of chiral triazole fungicides in crops 9,
75
10
76
chiral triazole fungicides in agricultural systems is lacking.
14
. Mycotoxins may cause adverse toxicological effects in exposed
19
9, 16-18
.
. Little is known about
. Although these compounds are widely used, vital stereospecific knowledge of the
77
To better understand the enantioselective bioactivity and degradation of chiral
78
triazole fungicides in agriculture, one of the broad-spectrum, systemic chiral triazole
79
fungicides triticonazole was investigated at length. In the present study,
80
stereoselectivity was evaluated during biodegradation in four kinds of fruits and
81
vegetables by applying racemic triticonazole in field conditions. Individual
82
enantiomers were used for characterizing their stereospecific bioactivity to nine
83
common plant pathogens in lab conditions. Furthermore, structural analysis and 4
ACS Paragon Plus Environment
Page 5 of 35
Journal of Agricultural and Food Chemistry
84
computer modeling technology was used to investigate how the selective interactions
85
of triticonazole enantiomers with cytochrome P450 14α-sterol demethylases (CYP51)
86
in plant pathogens lead to their enantioselective bioactivity. The results of this
87
research will be helpful in elucidating the molecular mechanisms of the
88
enantioselective inhibition of fungal cell-wall synthesis in plant pathogens targeted by
89
chiral triazole fungicides possessing multiple chiral centers. This knowledge will also
90
establish a more complete understanding of the different therapeutic or adverse effects
91
which characterize each enantiomer. The insight gained from this study will be helpful
92
in promoting the application of bioactive enantiomers while reducing the unwanted
93
effects of invalid enantiomers as high-risk pollutants in agricultural management.
94
MATERIALS AND METHODS
95
Chemicals, phytopathogens, and culture conditions. Racemic triticonazole
96
(98.2% purity), rac-(E)-5-[ (4-chlorophenyl) methylidene]-2,2-dimethyl-1-(1H-1,2,4-
97
triazol-1-ylmethyl) cyclopentanol (Fig. S1), and ergosterol (98.0% purity) were
98
purchased from the China Standard Material Center (Beijing, China). Two pure
99
enantiomers of triticonazole (purity ≥99.0%) were prepared from the Shanghai
100
Chiralway Biotech Co., Ltd (Shanghai, China). The ee value of (R)-triticonazole and
101
(S)-triticonazole were 99.72% and 99.52%, respectively. The cellulose tris
102
(3-chloro-4-methylphenylcarbamate) chromatographic column (Lux Cellulose-2,
103
Phenomenex, Torrance, USA) packed with 3-μm particles (250 mm×4.6 mm i.d.) was
104
used for the chiral separation of triticonazole. For achiral analysis, a C18 column
105
(150×4.6 mm, 4.6 µm) was used. Sample extraction was conducted using a Cleanert 5
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
106
Florisil-SPE cartridges (500 mg, 6 mL) obtained from Agela Technologies (Tianjin,
107
China). All chromatographic solutions (acetonitrile, methanol, and n-hexane) were
108
purchased from Tedia (Fairfield, USA). Analytical grade reagents (sodium chloride,
109
potassium hydroxide, anhydrous sodium sulfate, and anhydrous magnesium sulfate)
110
were purchased from commercial sources. Purified water was prepared using a
111
MUL-9000 water purification system (Nanjing Zongxin Water Equipment Co. Ltd,
112
China). The stock solution of (R)-, (S), and rac-triticonazole were each stored at
113
-20 °C, and the two enantiopure standards were found to be stable over six months.
114
Nine of the test phytopathogens (Rhizoctonia solani, Fusarium verticillioide,
115
Botrytis cinerea (strawberry and tomato), Rhizoctonia cereali, Alternaria solani,
116
Gibberella zeae, Sclerotinia sclerotiorum, Pyricularia grisea) were obtained from the
117
Key Laboratory of Pesticides, Nanjing Agricultural University (Nanjing, China).The
118
Potato Dextrose Agar (PDA) consisted of 200 g of potato, 20 g of agar, and 20 g of
119
dextrose for every 1 L of distilled water, and the Potato Dextrose (PD) was based on
120
PDA without the agar.
121
Bioassay of fungicidal activities. Rac-triticonazole and its enantiomers were
122
prepared in acetone solvent. A high concentration of (R)-, (S)- and rac-triticonazole
123
were added into separate unsolidified PDA after the autoclaved media had reached a
124
temperature of approximately 45-50 °C. Both of enantiomers are not interconversion
125
and racemization in PDA solution. To avoid the influence of acetone solvent on the
126
growth of phytopathogens, the concentration of acetone in the PDA medium was kept
127
below 0.1 ml L-1. Mycelial plugs (5 mm in diameter) from the margins of actively 6
ACS Paragon Plus Environment
Page 6 of 35
Page 7 of 35
Journal of Agricultural and Food Chemistry
128
growing colonies were transferred to solidified PDA plates which contained different
129
concentrations of (R), (S), and rac-triticonazole in aseptic conditions. The same
130
concentration of acetone was added into plates as a positive control. Each isolate was
131
incubated in the dark at 25 °C with three replicates. Since, the growth rate of each
132
phytopathogen was different, all colony diameters were determined when the control
133
colony diameter had reached approximately 7 cm. The percent growth inhibition was
134
calculated according to the following equation 9, 10:
135
Inhibition (%) = (colony diameter in the control - colony diameter in the treatment) ×
136
100 / (colony diameter in the control-5 mm)
(1)
137
The median effective concentrations (EC50) of (R), (S), and rac-triticonazole for
138
the nine phytopathogens were calculated by a linear regression of the colony diameter
139
to a log of the transformed chemical concentration using DPS data-processing
140
software.
141
Extraction and analysis of ergosterol in phytopathogens. Mycelia of nine
142
phytopathogens were cultured in 1000-mL flasks (15 mycelial plugs per flask)
143
containing 400 mL of liquid potato dextrose (PD) in a rotary shaker (160 rpm) at 25°C,
144
whereas the mycelial plugs (5 mm diameter) were harvested from actively growing
145
colonies. When the mycelial plugs grew to the appropriate size after several days, the
146
different triticonazole enantiomers were separately added into liquid potato dextrose
147
(PD). The spiking concentrations of (R), (S), and rac-triticonazole were close to the
148
EC90 values for each pathogen and described in the Table S1. The liquid potato
149
dextrose without triticonazole served as a control and all treatments were in triplicate. 7
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 8 of 35
150
After a 72 h incubation, ergosterol was extracted from each phytopathogen according
151
to previous research with some modifications, and then ergosterol concentrations were
152
determined using high performance liquid chromatography (HPLC)
153
mycelia were collected by filtration and washed with sterile water several times, and
154
the mycelia were dried in a vacuum freeze drier. Approximately 0.5 g of dry mycelia
155
were broken with liquid nitrogen and subsequently suspended in 20 mL of freshly
156
prepared methanolic KOH (10 %, w/v) solvent. The mixtures was homogenized for 1
157
min, sonicated for 10 min, and then saponified at 80 °C for 90 minutes. To extract
158
ergosterol, a mixture of 5 mL distilled water and 10 mL n-hexane was added followed
159
by vigorous vortexing for 1 min. The samples were then centrifuged for 5 min at 3000
160
rpm. The ergosterol extraction procedure was repeated three times, then the n-hexane
161
supernatants from each extraction stage were pooled, evaporated to dryness, and then
162
re-dissolved in 10 mL of methanol-water (98:2, v/v). Before analysis, the samples
163
were filtered through a 0.22-µm filter membrane (Tengda, Tianjin, China). HPLC
164
analyses were conducted on an Agilent 1200 HPLC system (Agilent, USA) with a
165
ultraviolet detector. The separation of ergosterol was accomplished on a C18 column
166
(150×4.6 mm, 4.6 µm). Isocratic elution was conducted using a mobile phase
167
comprising of methanol and water (98:2, v/v) at a flow rate of 1.0 mL min-1. The
168
injection volume was 20 μL and the detection wavelength was set at 282 nm.
20-23
. Briefly,
169
Cell membrane permeability of phytopathogens. Prior to collection of plant
170
pathogen mycelia, the same concentration of triticonazole enantiomers as used in the
171
last experiment was separately added into liquid PD and incubated for 36 h (Table S1). 8
ACS Paragon Plus Environment
Page 9 of 35
Journal of Agricultural and Food Chemistry
172
After incubation, the mycelia were filtered on a double gauze, and thoroughly washed
173
using distilled water. The mycelia (0.500 g) were suspended in separate centrifuge
174
tubes containing 20 mL of double-distilled water 24. All treatments were performed in
175
triplicate at each time point. Then, the electrical conductivity in this system was
176
assessed by determining the cell membrane permeability at different time intervals
177
using a conductivity meter (CON510 Eutech/Oakton, Singapore). Finally, the
178
centrifuge tubes were put into boiling water for 5 min to allow for thorough
179
breakdown of the cell membrane, and final conductivity was determined. The relative
180
conductivity of the various mycelia was calculated according to the following
181
equation:
182 183
Relative conductivity (%) = Conductivity at different time points / Final conductivity × 100
(2)
184
Field experiments. Four kinds of vegetables (tomatoes, cucumbers, spinach,
185
Chinese cabbage) were prepared under field conditions in Nanjing, China. An
186
experimental field with no application history of triazole fungicide was divided into
187
several plots, each with an area of 30 m2 and insulated with a buffer zone. When the
188
vegetables are grown in appropriate stages according to the BBCH-scale, triticonazole
189
(2.5%, FS) was used as a foliar treatment with an application rate of approximately
190
400 g a.i. ha-1 (two times the recommended dose). Besides triticonazole, no other
191
triazole fungicides were applied to the crops during the field trials. Each field
192
experimental treatment was set up in triplicate for the dissipation rate study.
193
Representative vegetable samples were collected at different periods of time after 9
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
194
spraying. All samples were separately ground and stored in glass containers at -20 °C.
195
Extraction and analysis for vegetables. A 20 g aliquot of each vegetable
196
sample was extracted using 50 mL of ethyl acetate in a 100 mL Teflon centrifuge tube.
197
The extraction and cleanup procedures for chiral triticonazole were based on a
198
previous method with modifications
199
min followed by sonication for 15 min. After that, triticonazole was salted out from
200
the aqueous phase using 2.0 g of sodium chloride. The extraction mixture was
201
vigorously vortexed for 1 min and then centrifuged at 4,000 rpm for 5 min. The ethyl
202
acetate supernatant (~25-mL) was collected and evaporated prior to sample
203
purification using Florisil-SPE. Following purification, the sample was filtered
204
through a 0.22 μm filter before HPLC analysis. The chiral separation and
205
determination of enantiomers were according the previous established methods25.
206 207 208
25
. Briefly, the samples were homogenized for 3
Enantiomeric fraction (EF) described the enantiomeric composition of chiral compounds via the following equation 9: EF = R/(R + S)
(3)
209
where (S)-(+)-triticonazole was eluted first, followed by (R)-(-)-triticonazole on the
210
chiral chromatographic column. The R and S in this equation was the concentration of
211
(R) and (S) enantiomers, respectively.
212
Homology modeling and molecular docking. Cytochrome P450 14α-sterol
213
demethylases (CYP51) are essential enzymes in the process of sterol biosynthesis in
214
phytopathogens [26]. Triazole fungicides used in treatment of topical and systemic
215
mycoses function as inhibitors of CYP51, thus it is important to further explore the 10
ACS Paragon Plus Environment
Page 10 of 35
Page 11 of 35
Journal of Agricultural and Food Chemistry
216
mechanisms of triticonazole’s enantioselective bioactivity. The primary sequences of
217
nine phytopathogens are very similar to those of Aspergillus fumigatus, with the
218
sequences of six plant pathogens being over 58.5% similar, and the remaining three
219
being over 22.2% similar (Table S2). Therefore, the crystal structure (PDB: 4UYM)
220
of template proteins (CYP51B) for Aspergillus fumigatus was used for homology
221
modeling. Three-dimensional models of CYP51B in six plant pathogens with high
222
sequence similarity (Botrytis cinerea (strawberry and tomato), Gibberella zeae,
223
Fusarium verticillioide, Sclerotinia sclerotiorum, Pyricularia grisea) were built based
224
on the aligned sequences by homology modeling using the Prime application in
225
Schrodinger Maestro Suite 2015 (Prime, version 3.9, Schrodinger, LLC, New York,
226
NY, 2015). The initial three-dimensional structural models were selected and
227
energy-minimized for further refinement using the OPLS 2005 force field in
228
Schrodinger Prime. The validated models were optimized using the Protein
229
Preparation Wizard in Schrodinger Maestro Suite 2015 prior to simulated docking
230
with chiral triticonazole.
231
The docking between the CYP51b models from five types of plant pathogens and
232
chiral triticonazole enantiomers was performed using the Glide approach integrated in
233
Maestro 10.1 (Schrodinger, LLC, 2015), with standard precision mode. The binding
234
site was centered on the co-factor HEM (heme) and the metal-ligand interactions were
235
set as docking constraints in the Glide grid generation process, in which the remaining
236
settings used default parameters. Two enantiomers of chiral triticonazole were
237
separately docked into the binding site after preparation using LigPrep with the 11
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 12 of 35
238
docking protocol. Glide Score (GScore) as a scoring function is used to describe each
239
docking complex conformation, and the values generated are negative values. The
240
best-ranked complex conformation of each enantiomer by GScore was selected to
241
analyze the different binding modes with CYP51b for chiral triticonazole. A higher
242
absolute docking value of GScore means that the docking between ligand and receptor
243
is more stable 27, 28.
244
RESULTS AND DISCUSSION
245
Enantioselective
bioactivity
in
phytopathogens.
The
stereochemical
246
bioactivity of chiral triticonazole for nine phytopathogens was determined using a
247
biological assay based on the inhibition of bacteriostatic circle method. The racemic
248
mixture, rac-triticonazole, exhibited antifungal activity against all phytopathogens
249
with EC50 values of less than 1.00 mg kg-1, exhibited antifungal activity against all
250
phytopathogens with EC50 values less than 1.00mg kg-1, except for Pyriculariagrisea
251
where an EC50 value of 2.16 mg kg-1 was obtained (Table 1). Furthermore, the
252
antifungal activity of rac-triticonazole against Botrytis cinereal varied between
253
different host plant species. For example, based on EC50 values, rac-triticonazole was
254
2.33 times more effective in Botrytis cinereal infected strawberry plants than tomato.
255
As shown in Table 1, the two enantiomers of triticonazole possessed different
256
fungicidal activities and the order of potency was (R)-triticonazole > rac-triticonazole >
257
(S)-triticonazole in all bioassays. It was observed (R)-triticonazole was 3.11-82.89
258
times more active than the (S)-enantiomer. However, enantioselective bioactivity was
259
low against Pyriculariagrisea with the (R)-enantiomer only 3.11 times more potent 12
ACS Paragon Plus Environment
Page 13 of 35
Journal of Agricultural and Food Chemistry
260
than its antipode. In addition, the (R)-enantiomer was significantly more bioactivity
261
against Fusarium verticillioide and Rhizoctoniasolani with EC50 values 43.65-82.89
262
times higher than the (S)-enantiomer. Thus, the antifungal activity of triticonazole
263
may be attributed primarily to the (R)-enantiomer. The EC50 values of triticonazole
264
from the experiment showed in eight phytopathogens (Rhizoctoniasolani, Fusarium
265
verticillioide, Botrytis cinerea (strawberry and tomato), Rhizoctoniacereali,
266
Alternaria
267
contributed approximately 92.07-98.81% of the activity against plant pathogens in the
268
racemate. In previous studies on triazole fungicides, a 24.2-fold and 1000-fold
269
difference was observed between the chiral enantiomers of difenoconazole and
270
paclobutrazol, respectively 9, 29. Therefore, only one of the enantiomers of current-use
271
chiral fungicides may exhibit pathogenic control properties in agricultural
272
management.
solani,
Gibberellazeae,
Sclerotiniasclerotiorum),
(R)-enantiomer
273
Enantioselectivity in ergosterol biosynthesis. To further explore the underlying
274
mechanism of triticonazole’s enantioselective bioactivity on phytopathogens, the
275
inhibition of ergosterol biosynthesis by chiral enantiomers was investigated using the
276
chromatographic analysis. The concentrations of ergosterol for all treatments are
277
shown in Fig. 1. All triticonazole treatments significantly affected the ability of
278
pathogenic
279
Enantioselectivity was observed in the inhibitory effects on ergosterol biosynthesis in
280
nine phytopathogens for the two enantiomers (Table S3). Compared to the control,
281
around 25.63-77.58%, 18.23-64.27%, and 3.63-36.52% of ergosterol biosynthesis was
cells
to
synthesize
ergosterol
following
13
ACS Paragon Plus Environment
exposure
for
72
h.
Journal of Agricultural and Food Chemistry
282
inhibited by (R), (rac), and (S)-triticonazole, respectively. The inhibition of ergosterol
283
production was generally higher (1.80-7.34 times) following (R)-triticonazole
284
exposure than (S)-triticonazole against the nine pathogens. The enantioselective
285
inhibition of ergosterol production observed was in agreement with the
286
enantioselective bioactivity found in exposed phytopathogens. A positive correlation
287
(r=0.86) between the enantioselective bioactivity of the nine phytopathogens and the
288
inhibition of ergosterol biosynthesis for the triticonazole enantiomers was obtained by
289
fitting the bioactive ratio value (R/S) to the corresponding inhibition of ergosterol
290
ratio value in Fig. 2. The results suggest that the distinct bioactivities observed for
291
chiral triazole fungicides was mainly caused by the loss of the ability to synthesize
292
ergosterol in phytopathogenic cells.
293
Enantioselectivity in cell membrane permeability. Many commercial chiral
294
triazole fungicides are capable of affecting gene expression and may thus further
295
block the process of ergosterol biosynthesis
296
process for some commercial chiral triazole fungicides which are designed to
297
eliminate plant pathogens
298
substances in fungal cell membranes. Chiral triazole fungicides inhibit the formation
299
of cell membranes and ultimately the exchange of substances across the membrane,
300
resulting in cell death
301
concentrations of racemic and enantiopure triticonazole (Table S1), and the electrical
302
conductivity was detected after different exposure times. Following triticonazole
303
treatment, electrical conductivity gradually increased with increasing treatment time
20
21
. Ergosterol biosynthesis is the target
26
. This is significant since ergosterols are essential
. Nine plant pathogenic cells were treated with appropriate
14
ACS Paragon Plus Environment
Page 14 of 35
Page 15 of 35
Journal of Agricultural and Food Chemistry
304
and finally reached equilibrium after incubating for 180 h (Fig. S2). The results show
305
that (R)-, (S)-and, rac-triticonazole differentially enhanced the electrical conductivity
306
of the pathogenic cells. However, the electrical conductivity of nine plant pathogenic
307
cells amended with (S)-triticonazole were not significantly different from the control
308
for some of the plant pathogens (i.e. Botrytis cinerea, Pyricularia grisea, Sclerotinia
309
sclerotiorum). Furthermore, (R)-triticonazole substantially increased electrical
310
conductivity by 21.72 to 76.42% under the same treatment conditions, indicating that
311
the (R)-isomer is more potent in this regard (Table 2). Therefore, the enantioselective
312
cell membrane permeability for plant pathogenic cells may offer a more
313
comprehensive insight on the mechanism of enantioselective bioactivity caused by
314
chiral triazole fungicides. Cytochrome P450 enzyme are essential catalytic enzymes in
315
fungal ergosterol biosynthesis
316
against plant pathogenic cell requires further research to be understood, especially in
317
regard to the enantioselective relationship between chiral triazole fungicides and
318
phytopathogenic CYP51b.
30
. The precise impact of chiral triazole fungicides
319
Molecular interactions between chiral triticonazole enantiomers and
320
CYP51b. The homology modeling and molecular docking techniques are performed
321
to further explain the stereoselective molecular interactions for chiral enantiomers in
322
the phytopathogens. The composition of the three dimensional active group (i.e.
323
hydroxy, benzene, and pyrazolone ring) in triticonazole enantiomers strongly affects
324
their binding affinities to CYP51b enzymes. Both enantiomers can be tightly bound to
325
the active cavities of CYP51b, and the enantiomers are shown at different distances 15
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
326
from the key amino acids present (Fig. 3). For five of the phytopathogens studied (i.e.
327
Botrytis cinerea, Gibberella zeae, Fusarium verticillioide, Sclerotinia sclerotiorum,
328
Pyricularia grisea), several residues are in the active site of CYP51b within a distance
329
of 4 Å and 5 Å for three-dimensional and two-dimensional representations,
330
respectively (Fig. 3). All active site residues are summarized in Table S4. These
331
residues are closely related to the observed binding affinities for triticonazole
332
enantiomers since they determine the three-dimensional conformation of the
333
enzyme-ligand interaction. The binding affinities depend on the structure of chiral
334
compounds and of the receptor proteins themselves
335
groups (i.e. hydroxy and benzene) present in chiral triticonazole easily generate
336
hydrogen bonds and Pi-Pi stacking interactions with amino acid residues in the
337
enzyme active site. In addition, the ferric ions of heme are present in the active pocket
338
of CYP51b, allowing for Pi-cation and metal coordination interactions in the presence
339
of triticonazole. Furthermore, hydrophobic effects play an important role in
340
combining the hydrophobic functional groups of triticonazole with amino acid
341
residues 33, 34.
25, 31, 32
. Some of the functional
342
For five phytopathogens with high sequence similarity, the binding activity of
343
the association between the two enantiomers and CYP51b was investigated in terms
344
of their docking energy 31, 33. The top scored protonation formed between triticonazole
345
and CYP51b was selected, since docking score includes both binding affinity and
346
tautomeric ratio 35, 36. The two enantiomers showed distinct binding modes with amino
347
acid residues in the enzyme active site (Fig. 3). The binding affinity values of the 16
ACS Paragon Plus Environment
Page 16 of 35
Page 17 of 35
Journal of Agricultural and Food Chemistry
348
(R)-enantiomer were consistently lower than those of the (S)-isomer, suggesting that
349
(R) bound strongly to CYP51b, while (S) had poor binding activity to CYP51b in
350
phytopathogens (Table S4). The different binding activity with chiral triticonazole
351
could be synthetically caused by H-bonds, Pi-Pi stacking, Pi-cation interactions, metal
352
coordination, and hydrophobic effects, which are critical for stereoselective molecular
353
recognition
354
(R)-enantiomer exhibited greater bioactivity against common plant pathogens.
355
Therefore, the distinct bioactivities of chiral enantiomers in triazole fungicides may
356
derive from variable binding affinities and binding modes to CYP51b.
37, 38
. The results were consistent with the experimental results that the
357
Enantioselective dissipation in fruits and vegetables. The change of the value
358
of EF is a powerful metric to indicate enantioselective behavior of chiral pollution in
359
biological processes, and it was used to evaluate the enantioselective dissipation of
360
chiral triticonazole in vegetables under field conditions
361
relatively high concentrations of triticonazole after the foliar spray treatment,
362
followed by a gradual decreased with time. The dissipation of triticonazole
363
enantiomers followed first order kinetics (R2 ≥ 0.927), and the half-lives for both
364
enantiomers are shown in Table S5. The half-lives of the more bioactive
365
(R)-enantiomer were consistently shorter than those of (S)-triticonazole in the fruits
366
and vegetables studied. The average EF value for triticonazole remained constant (EF
367
= 0.5) at the beginning of the foliar spray treatment (0-5d for cucumber, 0-7d for
368
Chinese cabbage and tomato, and 0-14 d for spinach) in four plants (Fig. 4), but the
369
EF value instantly increased to 0.576-0.675 in the late stages (0.576 for tomatoes, 17
ACS Paragon Plus Environment
21
. The vegetables contained
Journal of Agricultural and Food Chemistry
Page 18 of 35
370
0.609 for spinach, 0.624 for Chinese cabbage and 0.675 for cucumbers). Preferential
371
dissipation of the (R)-enantiomer resulted in relative enrichment of the (S)-enantiomer.
372
Hence, the less bioactive (S)-enantiomer is more persistent in fruits and vegetables,
373
thus humans may be exposed to it through dietary intake. Chiral switching to
374
(R)-triticonazole from the commercial racemate will probably help in crop protection
375
against pathogens while reducing potential public health risks. The enzymatic systems
376
in plants have been shown in previous studies to play an important role in the
377
stereoselective degradation, metabolism, and accumulation of chiral pollutants
378
The absence of enantioselectivity at the beginning of the foliar spray treatment may be
379
due to the fact that the system of stereoselective enzymes had limited contact with
380
chiral triticonazole during this initial period. After this initial lag period following
381
pesticide application, the transportation and distribution of triticonazole throughout
382
the plant tissues increased in fruits and vegetables. Therefore, the system of
383
stereoselective enzymes was exposed to the chiral fungicides, resulting in a significant
384
enantioselective dissipation of the enantiomers in the vegetables.
9, 39
.
385
In this present work, Cell membrane permeability, ergosterol biosynthesis, and
386
molecular interaction investigations revealed significant differences between (R)-, (S)-,
387
and rac-triticonazole. Thus, the current study demonstrated the bioactivity and
388
dissipation of chiral triticonazole in agricultural ecosystems was enantiomer-specific.
389
The different binding affinities between the individual triticonazole enantiomers and
390
receptor proteins of CYP51b demonstrated the enantioselective bioactivities of chiral
391
triazole fungicides at molecular level. In addition, although (R)-triticonazole was 18
ACS Paragon Plus Environment
Page 19 of 35
Journal of Agricultural and Food Chemistry
392
found to be more bioactive than (S)-triticonazole against nine phytopathogens,
393
(R)-triticonazole was less persistent than (S)-triticonazole in various kinds of fruits
394
and vegetables under field conditions. Therefore, chiral switching to the more
395
bioactive and less persistent (R)-triticonazole from the currently used racemate would
396
reduce the required application dosage and hence the associated environmental risks
397
while still maintaining the fungicidal efficacy. Enantioselectivity is commonly
398
observed in several aspects of environmental science (i.e. adsorption, degradation,
399
transportation, excretion and ecotoxicology) for numerous chiral pesticides. Therefore,
400
the significance of enantioselective effects for chiral agrochemicals must be
401
considered in order to improve their risk assessment and minimize dangers to public
402
health.
403
ABBREVIATIONS USED
404
PDA, potato dextrose agar; PD, potato dextrose; EC50, effective concentrations;
405
HPLC, high performance liquid chromatography; GScore, glide score; EF,
406
enantiomeric fraction.
407
AUTHOR INFORMATION
408
Corresponding Author
409
*Phone: +86 25 84395479. Fax: +86 25 84395479. E-mail:
[email protected].
410
Funding
411
This study was supported by the National Key Research and Development Program of
412
China (2016YFD0200207).
413
Notes 19
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
414
Conflicts of interest the authors do not have any potential conflict of interest to
415
declare.
416
ASSOCIATED CONTENT
417
Supporting Information
418
Supporting materials (Fig. S1-S2 and Table S1-S5) are available free of charge via the
419
Internet at http://pubs.acs.org.
420 421
REFERENCES
422
[1] Morris, R. E.; Bu, X. Induction of chiral porous solids containing only achiral
423 424 425
building blocks. Nat. chem. 2010, 2, 353-361. [2] Shi, S.; Wong, Z.; Buchwald, S. L. Copper-catalysed enantioselective stereodivergent synthesis of amino alcohols. Nature 2016, 532, 353-356.
426
[3] Wu, L.; Wang, F.; Wan, X.; Wang, D.; Chen, P.; Liu, G. Asymmetric cu-catalyzed
427
intermolecular trifluoromethylarylation of styrenes: enantioselective arylation of
428
benzylic radicals. J. Am. Chem. Soc. 2017, 139, 2904-2907.
429
[4] Xu, S.; Oda, A.; Kamada, H.; Negishi, E. Highly enantioselective synthesis of γ-,
430
δ-, and ε-chiral 1-alkanols via Zr-catalyzed asymmetric carboalumination of
431
alkenes (ZACA)-Cu- or Pd-catalyzed cross-coupling. P. Natl. Acad. Sci. 2014,
432
111, 8368-8373.
433
[5] Sanganyado, E.; Lu, Z.; Fu, Q.; Daniel, S.; Jay, G. Chiral pharmaceuticals: A
434
review on their environmental occurrence and fate processes. Water Res. 2017,
435
527-542. 20
ACS Paragon Plus Environment
Page 20 of 35
Page 21 of 35
436 437
Journal of Agricultural and Food Chemistry
[6] Jin, B.; Rolle, M. Joint interpretation of enantiomer and stable isotope fractionation for chiral pesticides degradation. Water Res. 2016, 178-186.
438
[7] Lawrence, L. J.; Casida,BJ.E. Stereospecific action of pyrethroid insecticides on
439
the gamma-aminobutyric acid receptor-ionophore complex. Science. 1983, 221,
440
1399-1401.
441
[8] Lepesheva, G.I.; Waterman, M.R. Sterol 14α-demethylase cytochrome P450
442
(CYP51), a P450 in all biological kingdoms. Bba-Gen. Subjects. 2007, 1770,
443
467-477.
444
[9] Dong, F.; Li, J.; Chankvetadze, B.; Cheng, Y.; Xu, J.; Liu, X.; Li, Y.; Chen, X.;
445
Bertucci, C.; Tedesco, D.; Zanasi, R.; Zheng, Y. Chiral triazole fungicide
446
difenoconazole: Absolute stereochemistry, stereoselective bioactivity, aquatic
447
toxicity, and environmental behavior in vegetables and soil. Environ. Sci.
448
Technol. 2013, 47, 3386-3394.
449
[10] Zhang, Q.; Hua, X.; Shi, H.; Liu, J.; Tian, M.; Wang, M. Enantioselective
450
bioactivity, acute toxicity and dissipation in vegetables of the chiral triazole
451
fungicide flutriafol. J. Hazard. Mater. 2015, 284, 65-72.
452 453
[11] Corić, I.; List, B. Asymmetric spiroacetalization catalysed by confined Bronsted acids. Nature. 2012, 483, 315-319.
454
[12] Lewis, D.L.; Garrison, A.W.; Wommack, K.E.; Whittemore, A.; Steudler, P.;
455
Melillo, J. Influence of environmental changes on degradation of chiral
456
pollutants in soils. Nature. 1999, 401, 898-901.
457
[13] Giraldo, M.C. Valent, B. Filamentous plant pathogen effectors in action. Nature 21
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
458
Reviews Microbiology. 2013, 11, 800-814.
459
[14] Proctor, R.H.; Hohn, T. M.; Mccormick, S.P. Reduced virulence of gibberella
460
zeae caused by disruption of a trichothecene toxin biosynthetic gene. Mol. Plant
461
Microbe. In. 1995, 8, 593-601.
462
[15] Mazur, C.S.; Kenneke, J. F. Cross-species comparison of conazole fungicide
463
metabolites using rat and rainbow trout (onchorhynchus mykiss) hepatic
464
microsomes and purified human CYP 3A4. Environ. Sci. Technol. 2008, 42,
465
947-954.
466
[16] Li, Y.; Dong, F.; Liu, X.; Xu, J.; Li, J.; Kong, Z.; Chen, X.; Zheng, Y.
467
Environmental behavior of the chiral triazole fungicide fenbuconazole and its
468
chiral metabolites: enantioselective transformation and degradation in soils.
469
Environ. Sci. Technol. 2012, 46, 2675-2683.
470
[17] Buerge, I.J.; Poiger, T.; Müller, D. M.; Buser, H. R. Influence of pH on the
471
stereoselective degradation of the fungicides epoxiconazole and cyproconazole
472
in soils. Environ. Sci. Technol. 2006, 40, 5443-5050.
473
[18] Garrison, A. W.; Avants, J. K.; Jones, W. J. Microbial transformation of
474
triadimefon to triadimenol in soils: selective production rates of triadimenol
475
stereoisomers affect exposure and risk. Environ. Sci. Technol. 2011, 45,
476
2186-2193.
477
[19] Shen, Z.; Zhang, P.; Xu, X.; Wang, X.; Zhou, Z.; Liu, D. Gender-related
478
differences in stereoselective degradation of flutriafol in rabbits. J. Agric. Food
479
Chem. 2011, 59, 10071-10077. 22
ACS Paragon Plus Environment
Page 22 of 35
Page 23 of 35
Journal of Agricultural and Food Chemistry
480
[20] Sun, X.; Wang, J.; Feng, D.; Ma, Z.; Li, H. PdCYP51B, a new putative sterol
481
14α-demethylase gene of Penicillium digitatum involved in resistance to imazalil
482
and other fungicides inhibiting ergosterol synthesis. Appl. Microbiol. Biotechnol.
483
2011, 91, 1107-1119.
484
[21] Ouyang, Q.; Tao, N.; Jing, G. Transcriptional profiling analysis of penicillium
485
digitatum, the causal agent of citrus green mold, unravels an inhibited ergosterol
486
biosynthesis pathway in response to citral. BMC Genomics. 2016, 17, 599.
487 488
[22] Nes, W. D. Biosynthesis of cholesterol and other sterols. Chem. Rev. 2011, 111, 6423-6451.
489
[23] Alcazar-Fuoli, L.; Mellado, E.; Garcia-Effron, G.; Lopez, J. F.; Grimalt, J. O.;
490
Cuenca-Estrella, J. M.; Rodriguez-Tudela, J. L. Ergosterol biosynthesis pathway
491
in Aspergillus fumigatus. Steroids. 2008, 73, 339-347.
492
[24] Duan, Y.; Ge, C.; Liu, S.; Chen, C.; Zhou, M. Effect of phenylpyrrole fungicide
493
fludioxonil on morphological and physiological characteristics of Sclerotinia
494
sclerotiorum. Pestic. Biochem. Phys. 2013, 106, 61-67.
495
[25] Zhang, Q.; Gao, B.; Tian, M.; Shi, H.; Hua, X.; Wang, M. Enantioseparation and
496
determination of triticonazole enantiomers in fruits, vegetables, and soil using
497
efficient extraction and clean-up methods. J. Chromatogr. B. 2016, 1009,
498
130-137.
499
[26] Podust, L.M.; Poulos, T. L.; Waterman, M. R. Crystal structure of cytochrome
500
P450 14α-sterol demethylase (CYP51) from mycobacterium tuberculosis in
501
complex with azole inhibitors. P. Natl. Acad. Sci. 2001, 98, 3068-3073. 23
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 24 of 35
502
[27] Tian, M.; Zhang, Q.; Hua, X.; Tang, B.; Gao, B.; Wang, M. Systemic
503
stereoselectivity study of flufiprole: Stereoselective bioactivity, acute toxicity
504
and environmental fate. J. Hazard. Mater. 2016, 320, 487-494.
505
[28] Zhang, J.; Begum, A.; Brännström, K.; Grundström, C.; Iakovleva, I.; Olofsson,
506
A.; Sauer-Eriksson, A. E.; Andersson, P. L. A structure-based virtual screening
507
protocol for in silico identification of potential thyroid disrupting chemicals
508
targeting transthyretin. Environ. Sci. Technol. 2016, 50, 11984-11993.
509
[29] Burden, R.S.; Carter, G. A.; Clark, T.; Cooke, D.T.; Croker, S. J.; Deas, A. H. B.;
510
Hedden, P.; James, C. S.; Lenton, J. R. Comparative activity of the enantiomers
511
of triadimenol and paclobutrazol as inhibitors of fungal growth and plant sterol
512
and gibberellin biosynthesis. Pest Manag. Sci. 2010, 21, 253-267.
513
[30] Trzaskos, J. M.; Fischer, R. T.; Favata, M. F. Mechanistic studies of lanosterol
514
c-32
demethylation.
conditions
which
promote
oxysterol
intermediate
515
accumulation during the demethylation process. J. Biol. Chem. 1986, 26,
516
16937-16942.
517
[31] Zhai, G.; Hu, D.; Lehmler, H. J.; Schnoor, J. L. Enantioselective
518
biotransformation of chiral PCBs in whole poplar plants. Environ. Sci. Technol.
519
2011, 45, 2308-2316.
520
[32] Khalaf, H.; Larsson, A.; Berg, H.; Mccrindle, R.; Arsenault, G.; Olsson, P. E.
521
Diastereomers
of
the
brominated
flame
retardant
522
dibromoethyl)cyclohexane induce androgen receptor activation in the HepG2
523
hepatocellular carcinoma cell line and the LNCaP prostate cancer cell line. 24
ACS Paragon Plus Environment
1,2-dibromo-4-(1,2
Page 25 of 35
524
Journal of Agricultural and Food Chemistry
Environ. Health Perspect. 2009, 117, 1853-1859.
525
[33] Zhao, M.; Zhang, Y.; Zhuang, S.; Zhang, Q.; Lu, C.; Liu, W. Disruption of the
526
hormonal network and the enantioselectivity of bifenthrin in trophoblast:
527
Maternal-fetal health risk of chiral pesticides. Environ. Sci. Technol. 2014, 48,
528
8109-8116.
529
[34] He, X.; Dong, X.; Zou, D.; Yu, Y.; Fang, Q.; Zhang, Q.; Zhao, M.
530
Enantioselective effects of o,p′-DDT on cell invasion and adhesion of breast
531
cancer cells: chirality in cancer development. Environ. Sci. Technol. 2015, 49,
532
10028-10037.
533
[35] Shelley, J. C.; Cholleti, A.; Frye, L. L.; Greenwood, J. R.; Timlin, M. R.;
534
Uchimaya, M. Epik: A software program for pKa prediction and protonation state
535
generation for drug-like molecules. J. Comput. Aided. Mol. Des. 2017, 21,
536
681-691.
537
[36] Friesner, R. A.; Banks, J. L.; Murphy, R. B.; Halgren, T. A.; Klicic, J. J.; Mainz,
538
D. T.; Repasky, M. P.; Knoll, E. H.; Shelley, M.; Perry, J. K.; Shaw, D. E.;
539
Francis, P.; Shenkin, P. S. Glide: A New Approach for Rapid, Accurate Docking
540
and Scoring. 1. Method and Assessment of Docking Accuracy. J. Med. Chem.
541
2004, 47, 1739-1749.
542
[37] Iakovleva, I.; Brännström, K.; Nilsson, L.; Gharibyan, A. L.; Begum, A.; Anan, I.;
543
Walfridsson, M.; mSauer-Eriksson, A. E.; Olofsson, A. Enthalpic forces correlate
544
with the selectivity of transthyretin-stabilizing ligands in human plasma. J. Med.
545
Chem. 2015, 58, 6507-6515. 25
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
546
[38] Alhamadsheh, M. M.; Connelly, S.; Cho, A.; Reixach, N.; Powers, E. T.; Pan,
547
D.W.; Wilson, I. A.; Kelly, J. W.; Graef, I. A. Potent kinetic stabilizers that
548
prevent transthyretin-mediated cardiomyocyte proteotoxicity. Sci. Transl. Med.
549
2011, 3, 81.
550
[39] Huang, H.; Zhang, S.; Lv, J.; Wen, B.; Wang, S.; Wu, T. Experimental and
551
theoretical evidence for diastereomer- and enantiomer-specific accumulation and
552
biotransformation of HBCD in maize roots. Environ. Sci. Technol. 2016, 50,
553
12205-12213.
554
26
ACS Paragon Plus Environment
Page 26 of 35
Page 27 of 35
Journal of Agricultural and Food Chemistry
555
Figure Legends
556
Figure 1. The enantioselective inhibition of ergosterol biosynthesis by chiral
557
triticonazole enantiomers.
558
Figure 2. The relationship between the R/S ratio value of enantioselective bioactivity
559
and the enantioselective inhibition of ergosterol.
560
Figure 3. The two-dimensional and three-dimensional enantiomer-specific binding
561
modes for triticonazole enantiomers bound to CYP51b.
562
Figure 4. Time development of EF values for the triticonazole enantiomers in
563
vegetables.
564
27
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 28 of 35
Table 1. EC50 values of chiral triticonazole enantiomers for nine plant pathogens. R-triticonazole
Species
Rac-triticonazole
S-triticonazole
R/Sd
EC50a (mg kg-1)
R2b
Pc
EC50 (mg kg-1)
R2
P
EC50 (mg kg-1)
R2
P
Rhizoctonia solani
0.0060±0.0005
0.9497
0.0173
0.0091±0.0007
0.9516
0.0019
0.2619±0.0057
0.9873
0.0027
43.65
Fusarium verticillioide
0.0335±0.0019
0.9574
0.0105
0.1153±0.0039
0.9830
0.0026
2.7769±0.0431
0.9870
0.0018
82.89
Botrytis cinerea (strawberry) Rhizoctonia cereali
0.1190±0.0036
0.9456
0.0048
0.4307±0.0121
0.9421
0.0058
1.3825±0.0578
0.9917
0.0057
11.62
0.1632±0.0043
0.9710
0.0231
0.3485±0.0193
0.9755
0.0134
1.9580±0.0713
0.9967
0.0151
12.00
Botrytis cinerea (tomato) Alternaria solani
0.2771±0.0203
0.9916
0.0071
0.7431±0.0363
0.9847
0.0047
4.2013±0.2151
0.9448
0.0071
15.16
0.3084±0.0176
0.9847
0.0238
0.7934±0.0219
0.9887
0.0313
4.8694±0.2637
0.9921
0.0054
15.79
Gibberella zeae
0.4066±0.0183
0.9896
0.0137
0.8034±0.0605
0.9757
0.0171
6.0840±0.4179
0.9938
0.0079
14.96
Sclerotinia sclerotiorum
0.5236±0.0471
0.9900
0.0091
0.9070±0.0786
0.9910
0.0121
11.2996±1.0021
0.9704
0.0191
21.58
Pyricularia grisea
1.7661±0.0893
0.9798
0.0275
2.1607±0.1563
0.9679
0.0029
5.4854±0.4873
0.9966
0.0023
3.11
a the effective concentration that results in a 50% reduction in population growth compared to the control. b represents the correlation coefficient. c represents the probability (associated with the t-test). d the EC50 value of R-triticonazole to S-triticonazole ratio.
28
ACS Paragon Plus Environment
Page 29 of 35
Journal of Agricultural and Food Chemistry
Table 2. Inhibited cell membrane permeability (%) in plant pathogens by chiral triticonazole enantiomers.
Gibberella
Rhizoctonia
Botrytis cinerea
Rhizoctonia
Alternaria
Botrytis cinerea
Fusarium
Sclerotinia
Pyricularia
zeae
cereali
(strawberry)
solani
solani
(tomato)
verticillioide
sclerotiorum
grisea
(R)-triticonazole
30.30
24.98
45.40
37.60
52.16
76.42
21.72
73.20
69.85
(Rac)-triticonazole
26.95
21.42
42.19
33.25
48.78
73.41
17.68
69.51
63.61
(S)-triticonazole
24.15
20.07
40.38
32.25
43.89
70.32
16.95
65.54
59.73
Untreated control
21.59
15.85
37.73
31.45
41.81
67.82
15.97
63.34
57.90
Chiral enanatiomers
29
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Figure 1. The enantioselective inhibition of ergosterol biosynthesis by chiral triticonazole enantiomers in nine plant pathogens.
30
ACS Paragon Plus Environment
Page 30 of 35
Page 31 of 35
Journal of Agricultural and Food Chemistry
Figure 2. The relationship between the R/S ratio value of enantioselective bioactivity and the enantioselective inhibition of ergosterol.
31
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Figure 3. The two-dimensional dimensional and three-dimensional enantiomer-specific specific binding modes for pure triticonazole enantiomers bound to CYP51b in five plant pathogens verticilllioide C Botrytis cinerea,, D Sclerotinia (A Gibberella zeae, B Fusarium verticilllioide, sclerotiorum, E Pyricularia grisea) grisea with high sequence similarity.
32
ACS Paragon Plus Environment
Page 32 of 35
Page 33 of 35
Journal of Agricultural and Food Chemistry
Figure 4. Time development of EF values for the triticonazole enantiomers in spinach (A) , cucumber (B), (B) Chinese cabbage (C) and tomato (D).
33
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
TOC Graphic:
34
ACS Paragon Plus Environment
Page 34 of 35
Page 35 of 35
Journal of Agricultural and Food Chemistry
509x285mm (150 x 150 DPI)
ACS Paragon Plus Environment