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Comprehensive screening and identification of fatty acid esters of hydroxy fatty acids in plant tissues by chemical isotope labeling-assisted liquid chromatography-mass spectrometry Quan-Fei Zhu, Jing-Wen Yan, Tian-Yi Zhang, Hua-Ming Xiao, and Yu-Qi Feng Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.8b02839 • Publication Date (Web): 27 Jul 2018 Downloaded from http://pubs.acs.org on July 28, 2018
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Analytical Chemistry
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Comprehensive screening and identification of fatty acid esters of
2
hydroxy fatty acids in plant tissues by chemical isotope
3
labeling-assisted liquid chromatography-mass spectrometry
4 5
Quan-Fei Zhu,† Jing-Wen Yan,† Tian-Yi Zhang, Hua-Ming Xiao, Yu-Qi Feng *
6 7
Key Laboratory of Analytical Chemistry for Biology and Medicine (Ministry of
8
Education), Department of Chemistry, Wuhan University, Wuhan 430072, P.R. China
9
† These authors contributed equally to this work.
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*To whom correspondence should be addressed. Tel.: +86-27-68755595; fax:
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+86-27-68755595. E-mail address:
[email protected].
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Abstract Fatty acid esters of hydroxy fatty acids (FAHFAs) are a new class of lipid
17
mediators
with
promising
anti-diabetic
and
anti-inflammatory
18
Comprehensive screening and identification of FAHFAs in biological samples would
19
be beneficial to the discovery of new FAHFAs and enable greater understanding of
20
their biological functions. Here, we report the comprehensive screening of FAHFAs in
21
rice and Arabidopsis thaliana by chemical isotope labeling-assisted liquid
22
chromatography-mass spectrometry (CIL-LC-MS). Multiple reaction monitoring
23
(MRM) was used for screening of FAHFAs. With the proposed method, we detected
24
49 potential FAHFA families, including 262 regioisomers, in tissues of rice and
25
Arabidopsis thaliana, which greatly extends our knowledge of known FAHFAs. In
26
addition, we proposed a strategy to identify FAHFA regioisomers based on their
27
retention on a reversed-phase LC column. Using the proposed identification strategy,
28
we identified 71 regioisomers from 11 FAHFA families based on commercial
29
standards and characteristic chromatographic retention behaviors. The screening
30
technique could allow for the discovery of new FAHFAs in biological samples. The
31
new FAHFAs identified in this work will contribute to the in-depth study of the
32
functions of FAHFAs.
33
Keywords: FAHFA, chemical isotope labeling, mass spectrometry, chromatographic
34
retention behavior, plant
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properties.
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Analytical Chemistry
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Introduction
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Fatty acid esters of hydroxy fatty acids (FAHFAs) are a new class of endogenous
39
lipids with important physiological functions1. It has been reported that FAHFAs can
40
improve glucose uptake from the blood, enhance insulin secretion and relieve
41
obesity-associated inflammation in mammals. Therefore, theses natural lipids are
42
expected to be used for diabetes therapy1,2. The molecular structure of FAHFA is a
43
combination of two fatty acyl chains through an ester bond. In recent years,
44
lipidomics has been used to identify a total of 18 FAHFA families consisting of 5 FAs
45
(PA, PO, OA, SA, and DHA) and 6 HFAs (HPA, HPO, HOA, HSA, HLA, and HDHA)
46
in different combinations (Figure S1)1,3. The full names of all the fatty acids can be
47
found in Table S1. Furthermore, each FAHFA family consists of different ester
48
regioisomers, which are distributed differently in specific tissues in vivo1. For
49
example, 13/12-, 11-, 10-, 9-, and 5-PAHSA are present in wild-type mice serum at
50
0.4-2.5 nmol/L. In white adipose tissue, 9-PAHSA is the most abundant isomer at 100
51
pmol/g; followed by 13/12-, 11-, 10-PAHSA (20%-30% of 9-PAHSA); and 8-, 7-,
52
5-PAHSA (2-3 pmol/g)1.
53
FAHFAs can be synthesized endogenously and obtained exogenously from
54
foods1. Yore et al. demonstrated that FAHFA can be synthesized in vivo with HFA as a
55
precursor1. In addition, several PAHSA regioisomers were detected in mouse feed,
56
apple and broccoli, suggesting that FAHFAs may exist naturally in other plants, and
57
that mammals could obtained FAHFA through dietary intake1. However, current
58
studies on FAHFAs mainly focus on mammals1,4-6, and little knowledge is available 3
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on the existence of FAHFAs in plants. Previous studies have shown that FAs and
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HFAs are abundant in plants7-9, and they may act as precursors for the synthesis of
61
FAHFAs in plants. In addition, the FAs and HFAs in plants tissues are different from
62
those in mammals. Therefore, screening of FAHFAs in plants could lead to the
63
discovery of some new FAHFA families or members.
64
Mass spectrometry (MS) is the most powerful analytical platform for
65
lipidomics10-12. In previous studies, full scan13,14, precursor ion scanning15 and neutral
66
loss scanning16 modes of MS were used for non-targeted lipidomics analysis to
67
discover and identify novel lipids. However, there are several difficulties in screening
68
and identifying FAHFAs in plants by traditional lipidomics methods: (1) the
69
ionization efficiency of FAHFAs under negative ion mode is poor in electrospray
70
ionization (ESI), and the aforementioned scanning modes lack sufficient detection
71
sensitivity for low-abundance FAHFAs (approximately 0.2–15 nmol/L in serum and
72
10–2500 pmol/g in mice tissues) in vivo1; (2) few FAHFA standards are commercially
73
available, and relevant information on FAHFAs is not recorded in databases; and (3) it
74
is very difficult to obtain MSn spectra of multiple regioisomers that elucidate the ester
75
bond location due to their low abundances17. Therefore, the discovery and
76
identification of new FAHFAs remain challenging.
77
Our previous study demonstrated the introduction of an appropriate functional
78
group on the FAHFA structure could improve its detection sensitivity and
79
chromatographic separation18. Based on this, we established a new strategy using
80
chemical isotope labeling-assisted liquid chromatography (CIL-LC-MS) for 4
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Analytical Chemistry
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comprehensive screening and identification of FAHFAs in rice and Arabidopsis
82
thaliana.
83
2-dimethylaminoethylamine (DMED) and d4-DMED, were used to selectively and
84
efficiently react with the carboxyl group of FAHFAs (Figure S2). The
85
DMED/d4-DMED-labeled FAHFAs can generate two characteristic neutral losses
86
using collision-induced dissociation (CID). We designed the potential FAHFA
87
precursor ions by screening the HFAs (precursors of FAHFAs) with carbon-chain
88
lengths from C6 to C24 and then combining with the essential FAs reported in plants.
89
According to the characteristic neutral loss of DMED/d4-DMED-labeled FAHFAs in
90
CID, the corresponding product ions can be inferred. In this respect, non-targeted
91
screening of potential FAHFAs in plants can be performed with high sensitivity and
92
selectivity in multiple-reaction monitoring mode (MRM). Subsequently, we
93
investigated the LC retention behavior of DMED-labeled FAHFAs on a
94
reversed-phase column and found that the retention of FAHFA regioisomers was
95
related to the ester bond position and the number of carbon atoms in the structure.
96
Using the spectral data of identified FAHFAs (retention factors, ester position and
97
carbon atom number), we constructed a three-dimensional (3-D) prediction model to
98
putatively identify new FAHFA regioisomers. We found 49 FAHFA families (262
99
regioisomers) in rice and Arabidopsis thaliana, and 11 FAHFA families (71
100
regioisomers) were accurately identified. The established method is a promising
101
analytical platform for the discovery and identification of new FAHFA compounds in
102
plant tissues.
In
this
strategy,
a
pair
of
isotope-labeling
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Experimental section
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Chemicals and reagents
106
All of the FAHFA standards, including 13-PAHSA, 12-PAHSA, 10-PAHSA,
107
9-PAHSA, 5-PAHSA, 13-OAHSA, 12-OAHSA, 10-OAHSA, 9-OAHSA, 5-OAHSA,
108
13-SAHSA, 12-SAHSA, 10-SAHSA, 9-SAHSA, 5-SAHSA, 13-POHSA, 12-POHSA,
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10-POHSA, 9-POHSA, 5-POHSA, and 9-PAHPA were purchased from Cayman
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Chemical.
111
10-HDAHSA and 7-PDAHSA were synthesized by XuKang Medical Science and
112
Technology Co., Ltd. (Xiangtan, Hunan, China). 1H–NMR spectrum and MS spectra
113
were shown in Figure S3. 2-dimethylaminoethlamine (DMED) was supplied by J&K
114
Chemical (Beijing, China). The isotope reagent, d4-DMED was synthesized according
115
to our previously described method19.
(Arbor,
Michigan,
USA).
9-MAHSA,
9-PDAHSA,
9-PAHMA,
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Chromatographic grade acetonitrile (ACN), acetone, isopropanol (IPA),
117
chloroform, methanol (MeOH) and ethyl acetate (EtOAc) were purchased from Tedia
118
Co. Inc. (Fairfield, OH, USA). Formic acid, ammonium hydroxide (NH3·H2O),
119
2-chloro-1-methylpyridinium iodide (CMPI), and triethylamine (TEA) were of
120
analytical grade and obtained from Sinopharm Chemical Reagent Co., Ltd (Shanghai,
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China). The water used throughout the study was purified on a Milli-Q apparatus
122
(Millipore, Bedford, MA). Strong anion exchange solid phase extraction cartridges
123
(SAX SPE-cartridges, 3 mL, 200 mg) were supplied by Weltech Co. (Wuhan, China).
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Stock solutions of all FAHFAs were prepared in EtOAc at a concentration of 200 6
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µg/mL for each and stored at -20°C. CMPI, TEA, DMED, and d4-DMED were
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prepared in HPLC-grade ACN at 20 µmol/mL.
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Plant materials
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Rice (Oryza sativa ssp. indica cv. Zhenshan 97B) and Arabidopsis thaliana
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(Columbia ecotype) were obtained from State Key Laboratory of Rice Biology at the
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China National Rice Research Institute and grown in an artificial environmental
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chamber greenhouse at 30°C under 16 h light/8 h dark photoperiods. 10 days old rice
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leaves and 7 weeks old Arabidopsis thaliana were harvested, weighed, immediately
133
frozen in liquid nitrogen, and stored at −80°C.
134
Sample preparation
135
The overall procedure for sample extraction is summarized in Figure S4. First,
136
100 mg of plant materials (fresh weight) were frozen in liquid nitrogen, ground into
137
powder with liquid nitrogen, and transferred into a 5 mL centrifuge tube. Then, Bligh
138
and Dyer lipid extraction was performed20,21. A mixture of 1 mL MeOH, 1 mL H2O
139
and 2 mL chloroform was added to the plant powder sample tube. The mixture was
140
homogenized via ultrasonication for 30 min. The mixture was centrifuged, and the
141
organic phase containing the extracted lipids was collected and dried under a N2
142
stream. Subsequently, the extract was re-dissolved with 1 mL ACN containing 0.1%
143
NH3·H2O (v/v), followed by strong anion-exchange solid phase extraction (SAX SPE)
144
enrichment (3 mL, 200 mg). The SAX SPE-cartridge was preconditioned with 3 mL
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ACN. The extract were introduced to the cartridge, and the cartridge was washed with
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3 mL acetone/H2O (1/9, v/v), followed by 3 mL acetone. Analytes were eluted with 3 7
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mL formic acid/acetone (1/99, v/v), and the eluate was evaporated to dryness at 40°C
148
under nitrogen stream.
149
According to our previous work, the purified extract was equally divided into
150
two portions and labeled with DMED and d4-DMED, respectively22. Briefly, 200 µL
151
ACN, 15 µL CMPI (20 µmol/mL) and 30 µL TEA (20 µmol/mL) were added to the
152
dried samples and mixed using a vortex mixer. The mixture was then incubated at
153
40oC for 5 min. Then, 30 µL DMED (20 µmol/mL) or d4-DMED (20 µmol/mL) was
154
added, and the mixture was incubated at 40°C for 1 h. Finally, the labeled solution
155
was dried under nitrogen gas.
156
Mass spectrometry analysis
157
The screening process was performed on a UHPLC-ESI-MS/MS system
158
consisting of a Shimadzu MS-8045 mass spectrometer (Tokyo, Japan) and a
159
Shimadzu LC-30AD HPLC system (Tokyo, Japan). The LC system was equipped
160
with two 30AD pumps, a SIL-30AC auto sampler, a CTO-20A thermostat column
161
compartment, and a DGU-20A5R degasser. Data acquisition and processing were
162
performed using LabSolutions software (version 5.53 sp2, Shimadzu, Tokyo, Japan).
163
For the screening of HFAs, LC separations were performed on an Acquity UPLC
164
BEH C18 column (2.1 × 50 mm, 1.7 µm, Waters) with a flow rate of 0.4 mL/min at
165
40°C. Formic acid in water (0.1%, v/v, solvent A) and ACN (solvent B) were
166
employed as mobile phases for the analysis of DMED-labeled HFA compounds. A
167
gradient for column equilibration of 0-2 min 5% B, 2-48 min 5% to 95% B, 48-54
168
min 95% B and 54-55 min 95% to 5% B was used. MRM analysis was performed 8
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Analytical Chemistry
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using positive ion mode. The source and ion transfer parameters were as follows: DL
170
temperature of 250°C; heat block temperature of 400°C; nebulizing gas flow of 3
171
L/min;
172
[DMED-HFA]+→[DMED-HFA - 63]+ and [d4-DMED-HFA]+→[d4-DMED-HFA -
173
67]+ or DMED- and d4-DMED-labeled HFA, respectively, were used as MRM ion
174
pairs. All precursor ions ([DMED-HFA]+ and [d4-DMED-HFA]+) for the MRM-MS
175
detection were selected according to the potential HFA structures, with carbon chain
176
lengths from C6 to C24. The acquired product ions were m/z [DMED-HFA-63]+) for
177
“light”-tagged and m/z [d4-DMED-HFA-67]+ for the “heavy”-tagged samples.
and
drying
gas
flow
of
15
L/min.
The
transitions
of
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For the screening of FAHFAs, separations were also performed on an Acquity
179
UPLC BEH C18 column (2.1 × 50 mm, 1.7 µm, Waters). Formic acid in ACN/water
180
(0.1%, 6/4, v/v, solvent A) and formic acid in IPA/ACN (0.1%, 9/1, v/v, solvent B)
181
were used as the mobile phases for the analysis of DMED-labeled FAHFA compounds.
182
A gradient for column equilibration of 0-26 min 20% to 90% B, 26-40 min 90% B,
183
and 35-37 min 90% to 20% B was used. The mobile phase flow rate was 0.4 mL/min,
184
and the column oven temperature was 40°C. For MRM screening of FA1HFA2, the
185
MRM ion pairs were selected based on the fragmentation pattern of DMED- and
186
d4-DMED-labeled FAHFA, respectively. Precursor ions were set as [DMED-FAHFA]+
187
and [d4-DMED-FAHFA]+ according to the desired m/z range, while product ions were
188
set as m/z [DMED-HFA-63]+ and m/z [d4-DMED-HFA-67]+ according to the
189
characteristic fragmentation pattern. The MRM parameters are listed in Table S2.
190
Calculation of retention factor 9
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191
For structure identification, the chromatographic retention factors (k) of FAHFA
192
candidates were calculated. The column dead time, tM, was measured using thiourea.
193
The retention time of FAHFA compounds, tR, were obtained by CIL-LC-MS analysis.
194
The calculation of retention factor is shown in Eq.1. ݇=
195 196
௧ ି௧ ௧
,
(1)
where tR is the retention time of an FAHFA compound, and tM is dead time.
197 198
Results and discussion
199
Overview of the strategy for screening and identifying FAHFAs
200
In this study, we established a chemical isotope labeling-assisted LC-MS method
201
for non-targeted screening and identification of trace-level FAHFAs in plant tissues
202
(Figure 1). To this end, Bligh and Dyer lipid extraction coupled with SAX-SPE was
203
employed to selectively extract and purify FAHFAs in rice and Arabidopsis thaliana
204
samples (For detail, see Figure S4). Then, the extract was divided into two equal
205
portions and labeled by DMED/d4-DMED reagents, respectively (For detail, see
206
Figure S2). Finally, the light and heavy labeled samples were mixed equally and
207
analyzed by LC-MS.
208
To determine possible components of FAHFAs, we first investigated the
209
distribution of HFAs in rice and Arabidopsis thaliana tissues. The precursor ion
210
information of DMED/d4-DMED-labeled HFAs, with carbon chain lengths from C6
211
to C24, was obtained; and the corresponding product ions of DMED- and
212
d4-DMED-labeled HFAs were speculated, based on the characteristic neutral loss of 10
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Analytical Chemistry
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63 and 67 Da in CID. Thus, LC-MRM-MS strategy was used for the screening of
214
HFAs in rice and Arabidopsis thaliana tissues. Subsequently, we obtained the possible
215
precursor ions of the DMED/d4-DMED-labeled FAHFAs by combining the spectral
216
data of detected HFAs with that of reported essential FA species in plants, and the
217
corresponding product ions were inferred using the particular CID fragmentation
218
behavior of DMED- and d4-DMED-labeled FAHFAs. Therefore, a list of MRM
219
transitions for DMED- and d4-DMED-labeled FAHFAs could be constructed, and
220
MRM-MS detection was used for non-targeted screening of potential FAHFAs in rice
221
and Arabidopsis thaliana. The obtained peak pairs were extracted and only peak pairs
222
with similar retention times and intensities were considered FAHFA candidates.
223
Finally, the FAHFA candidates were confirmed using pure standards and comparing
224
the retention time, or putatively identified according to their retention behavior on a
225
C18 column.
226 227
Discovery of FAHFAs in plants
228
Fragmentation of DMED/d4-DMED-labeled FAHFAs
229
The fragmentation pattern of known FAHFAs provides important insight into the
230
discovery and identification of novel FAHFAs. Hence, we investigated the
231
fragmentation behavior of FAHFAs labeled with DMED and d4-DMED by tandem
232
MS analysis. Three FAHFA standards (9-PAHSA, 10-SAHSA and 9-PAHPA) were
233
used as the analytes. As shown in Figures 2A and 2B, the DMED/d4-DMED-labeled
234
9-PAHSA can produced dominant product ions at m/z 308.3 via CID. The product 11
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235
ions were formed through a neutral loss (63/67 Da) and a loss of PA fragment,
236
respectively. DMED/d4-DMED-labeled 9-SAHSA and 9-PAHPA exhibited similar
237
fragmentation patterns to those of DMED/d4-DMED-labeled 9-PAHSA (Figure
238
2C-2F). Therefore, the DMED/d4-DMED-labeled FAHFA generated characteristic
239
product ions (m/z [DMED-HFA-63]+ and m/z [d4-DMED-HFA-67]+) via CID,
240
which were formed through a neutral loss (63/67 Da) and a loss of FA fragment,
241
respectively. Using this unique fragmentation pattern, the m/z of potential FAHFAs
242
can be theoretically predicted if the FAHFA composition is known.
243
Screening analysis of hydroxy-fatty acids in plants
244
HFAs are important precursors for the synthesis of FAHFAs in vivo1,2. In order to
245
select possible precursor ions of FAHFAs, we investigated the distribution of HFAs in
246
tissues of rice and Arabidopsis thaliana.
247
We
investigated
the
MS
fragmentation
behaviors
of
DMED-
and
248
d4-DMED-labeled HFAs (3-hydroxystearic acid and 12-hydroxystearic acid). The
249
DMED/d4-DMED-labeled 3-HSA and 12-HSA generated a characteristic neutral loss
250
of 63.0/67.0 Da using CID (Figure S5) and formed the most abundant product ions at
251
m/z 308.3. With this fragmentation pattern, the m/z of the product ions of
252
DMED/d4-DMED-labeled HFAs can be easily predicted as m/z [M+H]+ 63.0/67.0, by
253
subtracting
254
DMED/d4-DMED-labeled HFA were [DMED-HFA]+/[d4-DMED-HFA]+, according
255
to the predicted structures of HFAs with carbon chain lengths from C6 to C24. The
256
corresponding product ions, m/z [DMED-HFA-63]+ and [d4-DMED-HFA-67]+ for
the
neutral
loss.
Therefore,
the
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precursor
ions
of
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257
DMED- and d4-DMED-labeled compounds, respectively, were selected for MRM-MS
258
analysis.
259
Using this method, we determined the HFAs in tissues of rice and Arabidopsis
260
thaliana. The extracted ion chromatograms for DMED- and d4-DMED-labeled HFAs
261
are shown in Figure S6 in the Supporting Information. DMED- and d4-DMED-labeled
262
samples were combined 1:1 (v/v) and analyzed by LC-MS in MRM mode. The
263
extracted peak-pairs were selected as candidates of HFAs based on the following
264
criteria: they have a fixed mass difference of 4.0 Da (i.e., M d4-DMED-labeled-M
265
DMED-labeled = 4.0 Da), approximately identical retention times and peak heights.
266
In total, 15 HFA families, including 86 regioisomers, were determined in the tissues
267
of rice and Arabidopsis thaliana (Table S3). These HFAs were used as a reference for
268
the precursor ions of potential FAHFAs in rice and Arabidopsis thaliana. Among the
269
discovered HFAs, 15 HFA families (86 regioisomers) were detected in rice, and 12
270
HFA families (49 regioisomers) were detected in Arabidopsis thaliana (Table S3).
271
Screening of FAHFAs in plants
272
Taking the correlation of DMED/d4-DMED-labeled FAHFA structures and
273
MS/MS fragmentation into account, MRM was used for non-targeted screening of
274
FAHFAs in rice and Arabidopsis thaliana tissues. The precursor ions of
275
DMED/d4-DMED-labeled
276
[d4-DMED-FAHFA]+, according to the possible combinations of detected HFAs and
277
reported essential FAs. The corresponding product ions were [DMED-HFA-63]+ and
278
[d4-DMED-HFA-67]+, according to the characteristic fragmentation pattern (Table
FAHFAs
were
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[DMED-FAHFA]+
and
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279
S2). Along this line, a list of potential FAHFAs was constructed, and a comprehensive
280
LC-MS-based non-targeted workflow was established to discover potential FAHFAs
281
in rice and Arabidopsis thaliana extracts.
282
An equal amount of rice or Arabidopsis thaliana sample was labeled with
283
DMED and d4-DMED, respectively. Then, the light and heavy labeled samples were
284
mixed and analyzed by LC-MS. A pair of DMED- and d4-DMED-labeled compounds
285
with similar retention times and intensities was assigned as a potential FAHFA. The
286
overlaid extracted ion chromatograms of FAHFAs are shown in Figure 3. For example,
287
the peak pairs of PAHPAs with similar intensities and retention times were the same
288
in the extracted ion chromatograms at m/z of 581.5→280.2 and m/z of 585.5→280.2
289
from the DMED- and d4-DMED-labeled samples, respectively (Figure 3), suggesting
290
these candidate compounds are potential PAHPA regioisomers.
291
A total of 49 FAHFA families (262 regioisomers) were identified, of which 48
292
FAHFA families (229 regioisomers) were detected in rice and 37 FAHFA families
293
(173 regioisomers) were detected in Arabidopsis thaliana. This indicates that
294
FAHFAs are abundant in tissues of rice and Arabidopsis thaliana. The distribution of
295
these discovered FAHFAs in rice and Arabidopsis thaliana are shown in Figure 4, and
296
the detail information is provided in Table S4. Among the detected 49 FAHFA
297
families, 41 families of FAHFAs were discovered in this study, and this finding
298
greatly extends our knowledge of FAHFAs. It should be noted that the FAHFAs in
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rice (48 families, 229 regioisomers) are more abundant than those in Arabidopsis
300
thaliana (37 families, 173 regioisomers), which is consistent with the distribution of 14
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detected HFAs in rice and Arabidopsis thaliana.
302 303
Identification of FAHFAs in plants
304
Confirmation of FAHFAs using pure standards
305
The detected FAHFAs were first confirmed using commercially available
306
standards. A total of 21 FAHFA regioisomers, including 5-, 9-, 10-, 12-, 13-PAHSAs,
307
5-, 9-, 10-, 12-, 13-SAHSAs, 9-, 10-, 12-, 13-OAHSAs, 9-, 12-POHSAs, 9-PAHPAs,
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9-MAHSA, 9-PDAHSA, 9-PAHMA, and 10-HDAHSA could be confirmed based on
309
the retention time and fragmentation patterns. The comparison of the extracted ion
310
chromatograms of the standard compounds and detected FAHFAs is shown in Figure
311
S7. However, few standard FAHFAs are available commercially, which restricts the
312
analysis of all FAHFAs detected in this study. Moreover, since FAHFAs are a newly
313
discovered class of lipid molecules, relevant information on FAHFAs is not recorded
314
in databases. Therefore, by analyzing the tandem MS spectra of DMED-labeled
315
FAHFAs, the composition of new FAHFAs (FA and HFA) can be confirmed, but the
316
determination of the ester position of the regioisomers in low abundance remains
317
challenging.
318
Putative annotation of FAHFAs using chromatographic retention
319
We investigated the retention behavior of different ester regioisomers of one
320
family on a C18 column and found out that the position of the ester group on the fatty
321
acyl chain was closely related to the retention of the regioisomers on the C18 column.
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Indeed, as exemplified by the elution profile of PAHSAs and OAHSAs, the retention 15
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time increased when the ester group was positioned closer to the carboxylic acid
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moiety (Figure S8). As shown, the correlation between the retention factor (log10k)
325
and the ester position of different regioisomers in the PAHSA and OAHSA family is
326
significant, and the determination coefficient (R2) values are greater than 0.99 (Figure
327
S8). These results suggest that the ester position of each regioisomer from the same
328
FAHFA family can be determined by its retention behavior on the C18 column.
329
We investigated the retention behavior of different families of FAHFAs with
330
identical ester position on a C18 column. We found that the retention time, when FA
331
or HFA is given, is a function of the length of the carbon chain. For example, the
332
retention time of 9-MAHSA, 9-PDAHSA, 9-PAHSA and 9-SAHSA (compounds with
333
the same precursor, 9-HSA) on the C18 column increased linearly with their FA
334
carbon number (Figure S9). The result demonstrates that the retention behavior of
335
FAHFAs obeys the well-known carbon number rule23,24 and, thus, would be helpful in
336
identifying FAHFAs.
337
Taking the relationship of retention time and ester position into account, we
338
constructed the prediction curves for the determination of the ester positions of
339
unknown regioisomers from PAHSA, SAHSA and OAHSA families. The log10k
340
values of the regioisomers were calculated according to Eq. 1, and regression curves
341
for different FAHFAs were constructed by plotting log10k versus the ester position
342
from known regioisomers (Figure 5). For example, good linearity between log10k and
343
ester position for PAHSA regioisomers (5-, 9-, 10-, 12- and 13-position, Figure 5A
344
black squares) was achieved. Using the linear regression equation, the ester positions 16
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of unknown PAHSA regioisomers could be predicted by their log10k values (Figure
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5A, red circles). Therefore, the ester positions of unidentified PAHSA regioisomers
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(3-, 4-, 6-, 7-, 8-, 11-, 14- and 15-position, red circles) could also be determined. In
348
this way, the regioisomers of SAHSA and OAHSA families were identified (Figure
349
5B and 5C, red circles).
350
The ester position rule is suitable for the identification of unknown regioisomers
351
within a given FAHFA family. However, identifying unknown regioisomers by this
352
rule is impossible without pure standards for calibration. To overcome this limitation,
353
we constructed prediction curves based on the carbon number rule. For example, the
354
relationship of log10k and FA carbon number is shown in Figure 6A. Then, prediction
355
curves were generated from the linear regression of identified FAHSAs with identical
356
ester positions. Each line represents a defined ester position, and the data points that
357
correlate with the lines represent the regioisomers at the corresponding ester position.
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For example, the data points that correlate with the line of the 5-position can be
359
defined as 5-FAHSAs, and thus 5-MAHSA, 5-PDAHSA and 5-HDAHSA can be
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identified (Figure 6A, red line). Along this line, the 9-, 10-, 12-, and 13- ester position
361
of unknown regioisomers from MAHSA, PDAHSA, HDAHSA and AAHSA families
362
were putatively identified in the same way (Figure 6A). Similarly, the retention of
363
PAHFA families on a C18 column also conforms to the carbon number rule. Therefore,
364
a new PAHFA regioisomer, 9-PAHAA, was identified (Figure 6B).
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Construction of prediction model for identification
366
Using the carbon number rule, we identified FAHFA regioisomers that share the 17
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same ester position with the standards. However, the difficulty in identifying those
368
isomers with ester positions different from the standards remained. Therefore, we
369
utilized the above-identified FAHSAs as standards to construct a three-dimensional
370
(3-D) prediction model for identifying the ester position of unknown regioisomers
371
from different families of FAHSA. The 3-D scatter plots were constructed with three
372
factors: log10k, ester position and FA carbon number of the identified FAHSAs (Figure
373
7, blue dots). Fortunately, the 3-D scatter plots were fitted with a binary linear
374
regression equation: y=-0.0096x1 +0.026x2 +1.34, where y denotes log10k, x1
375
denotes the position of the ester, and x2 denotes the FA carbon number of FAHFAs.
376
The coefficient of determination (R2) of the fitting equation was 0.9912, and the
377
standard deviation was 0.0052, indicating that a good correlation (Figure 7, pink plane)
378
between the three factors exits. Therefore, the fitting equation (prediction model) can
379
be utilized to accurately identify the ester position of unknown regioisomers from
380
different families of FAHSA.
381
Accounting for the measured log10k value and FA carbon number in the fitting
382
equation, the ester position of unidentified FAHSAs was obtained. For example, the
383
ester position of an unknown MAHSA (log10k = 1.56; MA carbon number = 14) was
384
estimated to be 15.17, using the fitting equation. Thus the unknown MAHSA was
385
identified as 15-MAHSA. Using this method, 19 other regioisomers from MAHSA,
386
PDAHSA, HDAHSA and AAHSA families, were putatively identified as 4-, 8-, 11-,
387
14-, 15-MAHSA, 4-, 6-, 7-, 8-, 11-, 14-, 15-PDAHSA, 4-, 6-, 8-, 11-HDAHSA and 4-,
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11-, 15-AAHSA (Figure 7, red dots). 18
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To verify the reliability of the prediction model, we synthesized 7-PDAHSA
390
(purity > 95%, see Figure S3-E), a new FAHFA identified according to above
391
established prediction model. By comparing the extracted ion chromatogram of
392
DMED-labeled PDAHSAs from rice with pure 7-PDAHSA, the structure was
393
confirmed (Figure S10). Additionally, the prediction model could be used to predict
394
regioisomers of different FAHFA families that share an identical HFA or FA. However,
395
due to the limited availability of standards, the current prediction model is only
396
suitable for the identification of saturated FAHSA regioisomers. To construct
397
prediction models for the identification of more FAHFAs, we plan to obtain more
398
FAHFA standards that could be chemically or biologically synthesized.
399
Of the detected 49 FAHFA families (262 regioisomers), 11 FAHFA families (71
400
regioisomers, Table S5) were using pure standards for 8 families (21 regioisomers,
401
Table S5) and chromatographic retention behaviors for 7 families (50 regioisomers,
402
Table S5). Moreover, an additional 38 FAHFA families (191 regioisomers, Table S5)
403
were found, but their ester positions could not be annotated in the current study.
404
To verify the applicability of the prediction model, we screened and identified
405
FAHSA regioisomers in wheat seeds. As shown in Figure S11, a total of 12
406
regioisomers from the PAHSA family were detected in wheat seeds, and the x1 values
407
of these PAHSA regioisomers with different ester positions, were calculated using the
408
binary linear regression equation (y=-0.0096x1+0.026x2+1.34). Thus, the ester
409
positions of the screened PAHSA regioisomers in wheat seeds were determined. The
410
results demonstrate that the established 3-D prediction model can be used to directly 19
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identify regioisomers from FAHSA families in a variety of biological samples.
412 413
Conclusion
414
In this study, we report a comprehensive screening of FAHFAs using
415
CIL-LC-MS in MRM mode. This approach dramatically improved the detection
416
sensitivity and selectivity of FAHFAs by selecting paired-peaks with defined mass
417
differences for MRM scanning mode. In addition, we proposed a novel strategy for
418
identifying the ester position of FAHFA regioisomers based on the characteristic
419
chromatographic retention rules on a C18 column. This strategy overcomes the
420
difficulties in identifying regioisomers when commercial standards are not available
421
or when the compounds are not reported in databases. Using this method, we detected
422
49 FAHFA families, including 262 regioisomers in rice and Arabidopsis thaliana,
423
among which 71 regioisomers from 11 FAHFA families were further confirmed based
424
on commercial standards and chromatographic retention behaviors. This method
425
provides a promising tool for the discovery and identification of new FAHFAs in
426
biological samples.
427 428
ASSOCIATED CONTENT
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Supporting information
430 431
Supporting Information Available: Table S1 – S5; Figure S1 – S10. This material is available free of charge via the Internet at http://pubs.acs.org.
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Notes The authors declare no competing financial interest.
435 436
Acknowledgements
437
The work is supported by the National Key R&D Program of China
438
(2017YFC0906800), the National Natural Science Foundation of China (21475098,
439
21635006, 31670373).
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Reference
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(1) Yore, M. M.; Syed, I.; Moraes-Vieira, P. M.; Zhang, T. J.; Herman, M. A.; Homan, E. A.; Patel, R. T.;
447 448 449 450 451 452 453 454 455 456 457 458 459 460 461 462 463 464 465 466 467 468 469 470 471
(3) Kuda, O.; Brezinova, M.; Rombaldova, M.; Slavikova, B.; Posta, M.; Beier, P.; Janovska, P.;
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Lee, J.; Chen, S. L.; Peroni, O. D.; Dhaneshwar, A. S.; Hammarstedt, A.; Smith, U.; McGraw, T. E.; Saghatelian, A.; Kahn, B. B. Cell 2014, 159, 318-332. (2) Muoio, D. M.; Newgard, C. B. Nature 2014, 516, 49-50. Veleba, J.; Kopecky, J. Jr.; Kudova, E.; Pelikanova, T.; Kopecky, J. Diabetes 2016, 65, 2580-2590. (4) Brezinova, M.; Kuda, O.; Hansikova, J.; Rombaldova, M.; Balas, L.; Bardova, K.; Durand, T.; Rossmeisl, M.; Cerna, M.; Stranak, Z.; Kopecky, J. Biochimica et Biophysica Acta (BBA) - Molecular and Cell Biology of Lipids 2018, 1863, 126-131. (5) Nelson, A. T.; Kolar, M. J.; Chu, Q.; Syed, I.; Kahn, B. B.; Saghatelian, A.; Siegel, D. Journal of the American Chemical Society 2017, 139, 4943-4947. (6) Kolar, M. J.; Nelson, A. T.; Chang, T.; Ertunc, M. E.; Christy, M. P.; Ohlsson, L.; Harrod, M.; Kahn, B. B.; Siegel, D.; Saghatelian, A. Anal Chem 2018, 90, 5358-5365. (7) Lu, C.; Fulda, M.; Wallis, J. G.; Browse, J. The Plant Journal 2006, 45, 847-856. (8) Farmer, E. E.; Weber, H.; Vollenweider, S. Planta 1998, 206, 167-174. (9) Lu, C.; Fulda, M.; Wallis, J. G.; Browse, J. Plant Journal 2006, 45, 847-856. (10) Han, X.; Gross, R. W. Expert Review of Proteomics 2005, 2, 253-264. (11) Rainville, P. D.; Stumpf, C. L.; Shockcor, J. P.; Plumb, R. S.; Nicholson, J. K. Journal of Proteome Research 2007, 6, 552-558. (12) Chen, D.; Yan, X.; Xu, J.; Su, X.; Li, L. Metabolomics 2013, 9, 949-959. (13) Bird, S. S.; Marur, V. R.; Sniatynski, M. J.; Greenberg, H. K.; Kristal, B. S. Analytical Chemistry 2011, 83, 6648-6657. (14) Huan, T.; Li, L. Analytical Chemistry 2015, 87, 7011-7016. (15) Ejsing, C. S.; Duchoslav, E.; Sampaio, J.; Simons, K.; Bonner, R.; Thiele, C.; Ekroos, K.; Shevchenko, A. Analytical Chemistry 2006, 78, 6202-6214. (16) Houjou, T.; Yamatani, K.; Nakanishi, H.; Imagawa, M.; Shimizu, T.; Taguchi, R. Rapid Communications in Mass Spectrometry 2004, 18, 3123-3130. (17) Ma, Y.; Kind, T.; Vaniya, A.; Gennity, I.; Fahrmann, J. F.; Fiehn, O. J. Cheminformatics 2015, 7, 53. DOI: 10.1186/s13321-015-0104-4
(18) Zhu, Q.-F.; Yan, J.-W.; Gao, Y.; Zhang, J.-W.; Yuan, B.-F.; Feng, Y.-Q. Journal of Chromatography B 2017, 1061, 34-40. (19) Hao, Y. H.; Zhang, Z.; Wang, L.; Liu, C.; Lei, A. W.; Yuan, B. F.; Feng, Y. Q. Talanta 2015, 144, 341-348. (20) Bligh, E. G.; Dyer, W. J. Canadian Journal of Biochemistry & Physiology 1959, 37, 911-917. (21) Zhang, T. J.; Chen, S. L.; Syed, I.; Stahlman, M.; Kolar, M. J.; Homan, E. A.; Chu, Q.; Smith, U.; Boren, J.; Kahn, B. B.; Saghatelian, A. Nat. Protoc. 2016, 11, 747-763. (22) Zhu, Q. F.; Zhang, Z.; Liu, P.; Zheng, S. J.; Peng, K.; Deng, Q. Y.; Zheng, F.; Yuan, B. F.; Feng, Y. Q. Journal of Chromatography A 2016, 1460, 100-109. (23) Meulebroek, L. V.; Paepe, E. D.; Vercruysse, V.; Pomian, B.; Bos, S.; Lapauw, B.; Vanhaecke, L. Analytical Chemistry 2017, 89, 12502-12510. (24) Yu, D.; Zhou, L.; Xuan, Q.; Wang, L.; Zhao, X.; Lu, X.; Xu, G. Anal Chem 2018, 90, 5712-5718.
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Figure legends
486
Figure 1. Overview of the procedure for the screening and identification of FAHFAs
487
in rice and Arabidopsis thaliana by CIL-LC-MS.
488 489
Figure 2. Fragmentation of DMED/d4-DMED-labeled products by MS analysis. (A)
490
DMED-labeled 9-PAHSA; (B) d4-DMED-labeled 9-PAHSA; (C) DMED-labeled
491
9-SAHSA; (D) d4-DMED-labeled 9-SAHSA; (E) DMED-labeled 9-PAHPA; (F)
492
d4-DMED-labeled 9-PAHPA. Highlighted in red are the dominant product ions;
493
highlighted in blue are the theoretical m/z.
494 495
Figure 3. Extracted ion chromatograms of FAHFAs labeled with DMED and
496
d4-DMED and analyzed by LC-MS using MRM mode.
497 498
Figure 4. Fingerprint chromatograms of discovered FAHFAs in plant tissues. In total,
499
(A) 48 FAHFA families (229 regioisomers, plots) were found in rice and (B) 37
500
FAHFA families (173 regioisomers, plots) were found in Arabidopsis thaliana.
501 502
Figure 5. Identification of PAHSA, SAHSA and OAHSA regioisomers by the ester
503
position rule. Regression curve of the measured log10k (k, retention factor) versus the
504
ester position of (A) PAHSAs, (B) SAHSAs and (C) OAHSAs by LC-MRM-MS
505
analysis. Black squares represent commercial standards, and red circles represent
506
predicted structures.
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Figure 6. Identification of FAHFA regioisomers by the carbon number rule. (A)
509
Prediction of FAHSA species via the carbon chain length of FA. Black circles for
510
FAHSA standards, gray circles for unknown FAHSAs, red line for 5-position, blue
511
line for 9-position, green line for 10-position, orange line for 12-position and purple
512
line for 13-position. (B) Prediction of PAHFA species via the carbon chain length of
513
HFA. Black circles for 9-PAHMA, 9-PAHPA and 9-PAHSA standards, gray circles for
514
remainder PAHMAs and PAHAAs, red line for 9-position.
515 516
Figure 7. The prediction model, based on the log10k, ester position and carbon
517
number of FA, for saturated FAHSAs. Blue dots represent the confirmed compounds;
518
Red dots represent the predicted compounds.
519
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Figure 1
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Figure 2
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Figure 3
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Figure 4
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Figure 6
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Figure 7
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