Subscriber access provided by University of Otago Library
Article
Genotyping of toxic pufferfish based on specific PCRRFLP products as determined by liquid chromatography/ quadrupole-Orbitrap hybrid mass spectrometry Hajime Miyaguchi, Tadashi Yamamuro, Hikoto Ohta, Hiroaki Nakahara, and Shinichi Suzuki J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.5b03703 • Publication Date (Web): 02 Oct 2015 Downloaded from http://pubs.acs.org on October 2, 2015
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Journal of Agricultural and Food Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 33
Journal of Agricultural and Food Chemistry
Research Article Genotyping of toxic pufferfish based on specific PCR-RFLP products as determined by liquid chromatography/quadrupole-Orbitrap hybrid mass spectrometry Hajime Miyaguchi*, Tadashi Yamamuro, Hikoto Ohta, Hiroaki Nakahara and Shinichi Suzuki National Research Institute of Police Science, 6-3-1 Kashiwanoha, Kashiwa, Chiba 277-0882, Japan *Corresponding Author. Tel.: +81471358001; Fax: +81471339189; E-mail:
[email protected].
1
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
1
ABSTRACT: A method for the discrimination of toxic pufferfish was established
2
based on liquid chromatography/electrospray mass spectrometric analysis of the
3
enzymatically digested amplicons derived from mitochondrial 16S rRNA gene. A
4
MonoBis C18 narrow-bore silica monolith column (Kyoto Monotech) and a Q
5
Exactive mass spectrometer (Thermo Fisher) were employed for separation and
6
detection, respectively. Monoisotopic masses of the oligonucleotides were
7
calculated using Protein Deconvolution 3.0 software (Thermo Fisher). Although
8
a lock mass standard was not used, excellent accuracy (mass error, 0.83 ppm
9
on average) and precision (relative standard deviation, 0.49 ppm on average)
10
were achieved and a mass accuracy of less than 2.8 ppm was maintained for at
11
least 180 hours without additional calibration. The present method was applied
12
to 29 pufferfish samples and results were consistent with Sanger sequencing.
13 14
KEYWORDS: Pufferfish, Fugu, Polymerase chain reaction, Restriction fragment
15
length polymorphism, Electrospray ionization mass spectrometry
16
2
ACS Paragon Plus Environment
Page 2 of 33
Page 3 of 33
Journal of Agricultural and Food Chemistry
17
INTRODUCTION
18
According to an official bulletin by the Japanese government, 21 species of
19
pufferfish are categorized as edible; however, not all parts (organs/tissues) are
20
edible. The edible parts that are free of tetrodotoxin vary by species. Other
21
pufferfish are prohibited for sale because of the presence of toxins throughout
22
the whole body (e.g., Lagocephalus lunaris1) or because there is a lack of
23
toxicity data for a particular species. Therefore, species-based labeling of
24
pufferfish is officially required in the Japanese market; mislabeling, which could
25
lead to serious food poisoning, is a criminal offence.
26
Differentiation and discrimination of pufferfish is not just a challenge in Japan. In
27
the United States, the distribution of pufferfish is prohibited except for limited
28
importation from Japan of edible parts of Takifugu rubripes. However, a
29
tetrodotoxin poisoning occurred in Chicago in 2007 because of an illegal
30
importation of frozen pufferfish (Lagocephalus family) from China that had been
31
mislabeled as monkfish.2
32
Discrimination of pufferfish species is carried out in the Japanese market
33
morphologically, however, inedible L. lunaris is at risk of misidentification as
34
edible L. wheeleri, owing to the species having similar morphologies.1 Moreover,
35
morphological examination of pufferfish is virtually impossible in the case of
36
filleted or minced fish. A tetrodotoxin poisoning outbreak due to consumption of
37
dried fillets of L. lunaris occurred in Minneapolis in 2014.3 A discrimination
38
capability is also needed in the context of food fraud investigations because
39
Takifugu rubripes is far more expensive than other kinds of pufferfish. 3
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
40
For DNA-based differentiation of pufferfish species, the genes of cytochrome b,
41
12S rRNA, 16S rRNA and cytochrome c oxidase I in mitochondrial DNA have
42
been analyzed by Sanger sequencing, PCR-restriction fragment length
43
polymorphism (RFLP) analysis and real-time PCR analysis.2,4–8 While Sanger
44
sequencing is accurate and well-established, PCR-RFLP and real-time PCR
45
analysis are simple and rapid for analyzing DNA polymorphism. However,
46
because detection of DNA in the latter two methods is usually carried out by
47
non-sequence-based techniques which typically involve using a DNA-binding
48
fluorescent dye, the reliability of discrimination is inferior to that of Sanger
49
sequencing.
50
Mass spectrometry (MS) is one of the most reliable technologies for identifying
51
and characterizing biomolecules. Although matrix-assisted laser
52
desorption/ionization–time-of-flight MS is frequently used for the analysis of
53
proteins and short oligonucleotides (less than ~25 nucleotides (nt)), it is not
54
applicable to long oligonucleotides owing to the subsequent fragmentation,
55
adduct formation and low ionization efficiency.9–11 Instead, electrospray
56
ionization (ESI) can produce many charge states of multiply charged ions
57
([M-nH]n-) from biomacromolecules and, therefore, the mass of the analyte can
58
exceed the upper limit of the scan range of the spectrometer. This requires
59
transformation of a charge state series into the corresponding mass via
60
deconvolution. In the context of ESI-MS, whereas dissociation of a DNA duplex,
61
purification and desalting are required for direct measurement to overcome
62
ionization issues such as ion suppression and adduct formation,12–17 liquid 4
ACS Paragon Plus Environment
Page 4 of 33
Page 5 of 33
Journal of Agricultural and Food Chemistry
63
chromatography (LC) provides an on-line separation of the analytes from
64
coexisting substances instead of laborious sample purification and desalting.18,19
65
Whereas LC/ESI-MS has been used for amplicon-based genotyping including
66
differentiation of pathogen species, single nucleotide polymorphism and short
67
tandem repeat,9,12,15,20–24 discrimination of species other than pathogens by
68
LC/ESI-MS has not been reported.
69
In this study, LC/ESI-MS is applied for the first time for PCR-RFLP analysis of
70
fish samples to permit rapid and accurate discrimination of toxic pufferfish
71
species.
72 73
MATERIALS AND METHODS
74
Chemicals and materials
75
1,1,1,3,3,3-Hexafluoro-2-propanol and triethylamine were “eluent additive for
76
LC-MS” grade and supplied by Sigma–Aldrich (St. Louis, MO, USA). Synthetic
77
DNA templates (86–115 nt, sequences are shown in Table 1) were purchased
78
from Eurofins Genomics (Tokyo, Japan).
79 80
Preparation of digested amplicons
81
The procedure of sample preparation is summarized in Figure 1. PCR reactions
82
were performed on a 25 µL reaction scale and consisted of 0.625 U of Pfu-X
83
DNA polymerase (Jena Bioscience, Jena, Germany), 0.2 mM of each dNTP
84
(Jena Bioscience), 1× detergent free Phusion HF buffer (New England Biolabs,
85
Ipswich, MA, USA), either 12.5 ng of an extracted fish DNA or 0.5 pmol of the 5
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
86
synthetic DNA template and 0.4 µM of each primer. Two forward primers
87
(5′-CCATGTGGAATGAAAACACC-3′ for Takifugu and
88
5′-AAAAACAAGAGCCACAGCTCTAA-3′ for Lagocephalus) and one reverse
89
primer (5′-CCCTAGGGTAACTCGGTTCG-3′) were designed with the help of
90
Primer3Plus software (http://www.bioinformatics.nl/primer3plus/) and
91
synthesized by Fasmac (Atsugi, Japan). These primers were used to amplify
92
114–115-bp and 86-bp amplicons of the mitochondrial 16S ribosomal RNA gene
93
of Takifugu species and Lagocephalus species, respectively (Figure 1).25,26
94
Thermocycling was performed in a T100 thermal cycler (Bio-Rad, Hercules, CA,
95
USA) under the following conditions: 95 °C, 2 min, then 30 cycles at 95 °C, 30 s,
96
56 °C, 30 s, 72 °C, 30 s, 72 °C, 7 min and 12 °C hold. After PCR, 2 µL of the 10×
97
universal buffer M (Takara Bio, Otsu, Japan, containing 100 mM Tris-HCl (pH
98
7.5), 100 mM MgCl2, 10 mM dithiothreitol and 500 mM NaCl) and 1 µL of each
99
FastDigest restriction enzyme (Dra I and Msp I, Thermo Fisher Scientific) were
100
added to the tube and incubated for 30 min at 37 °C, followed by additional
101
incubation for 5 min at 72 °C. A portion of the reaction solution was analyzed by
102
polyacrylamide gel electrophoresis (PAGE) using the staining dye Gel Green
103
(Biotium, Hayward, CA, USA), if necessary. The remaining solution was filtered
104
with a Nanosep MF centrifugal device containing a Bio-inert membrane (0.45 µm,
105
Pall Corporation, Port Washington, NY, USA) before LC/ESI-MS analysis. The
106
filtrates were stored at −20 °C until analysis.
107 108
LC/ESI-MS analysis 6
ACS Paragon Plus Environment
Page 6 of 33
Page 7 of 33
Journal of Agricultural and Food Chemistry
109
The LC/ESI-MS was performed using an Ultimate 3000 liquid chromatograph
110
and a Q Exactive quadrupole–Orbitrap hybrid mass spectrometer (Thermo
111
Fisher Scientific). A reverse-phase silica monolith column (MonoBis C18, Kyoto
112
Monotech, Kyoto, Japan; 2.0×50 mm, mesopore size 30 nm, product number
113
2050H30ODS) was used for the separation at 20 °C with a MonoBis C18 guard
114
column (Kyoto Monotech). The mobile phase, delivered at a flow rate of 0.4
115
mL/min, was 400 mM 1,1,1,3,3,3-hexafluoro-2-propanol, 15 mM triethylamine
116
(pH 7.9) (A)–methanol (B).27 The proportion of B in the mobile phase was
117
changed over a linear gradient as follows: 0–0.5 min, 5%; 0.5–1 min, 5–30%; 1–
118
3.5 min, 30–40%; 3.5–5 min, 40–98%; 5–6 min, 98%; 6–6.05 min, 98–5% and
119
6.05–8 min, 5%. The sample injection volume was 1.0 µL except for the tests of
120
the stability of mass accuracy and the temperature of the column (0.5 µL each).
121
The post-column flow was connected to the mass spectrometer for 3.5–6 min
122
after sample injection. A heated ESI probe (HESI-II, Thermo Fisher) was used in
123
negative ion mode and with the following parameters: spray voltage, 2.5 kV;
124
vaporizer temperature, 350 °C; sheath gas, 50 arbitrary units (a.u.); auxiliary gas,
125
15 a.u. The parameters for the desolvation at the entrance of the mass
126
spectrometer were as follows: Capillary temperature, 350 °C; sweep gas
127
pressure, 1 a.u.; S-lens radiofrequency level, 100. High resolution mass analysis
128
was performed using the following parameters: scan range, m/z 700–3500;
129
nominal resolution (at m/z 200), 140,000; auto gain control target, 1×106;
130
microscans, 3; maximum ion time, 50 ms; in-source collision induced
131
dissociation, 15 eV. The C-trap pressure, which can be adjusted with the valve 7
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
132
inside the chassis, was reduced to 0.2 MPa to improve the sensitivity for long
133
oligonucleotides. A lock mass was not assigned. Mass calibration was
134
performed daily using sodium trifluoroacetate clusters (n = 5–24, m/z
135
792.85908–3376.38045).28 The calibration solution was 0.5 mg/mL sodium
136
trifluoroacetate (pH 3.5) in water–acetonitrile (1:1, v/v) and was infused into the
137
mass spectrometer at the flow rate of 10 µL/min. The in-source collision-induced
138
dissociation voltage was set to 60 eV to develop the cluster ions at higher mass
139
range.
140
Peak detection and deconvolution from the raw data using Xtract algorithm29,30
141
were carried out automatically with the Protein Deconvolution version 3.0
142
software (Thermo Fisher). The parameters were as follows: fit factor 90%,
143
charge range 3–50.
144 145 146
Analysis of pufferfish and other fish species
147
Twenty-nine pufferfish samples (1 boiled skin of T. rubripes, 3 raw livers and 1
148
ovary of Takifugu porphyreus, 1 raw muscle tissue of Takifugu vermicularis, 2
149
fresh whole bodies of Takifugu pardalis, 1 dried fillet of Takifugu snyderi, 19
150
fresh whole bodies of Takifugu poecilonotus and 1 dried fillet of Lagocephalus
151
wheeleri) and eight raw muscle tissues of other fish (Atlantic mackerel (Scomber
152
scombrus), Japanese horse mackerel (Trachurus japonicus), Japanese pilchard
153
(Sardinops melanostictus), Skipjack tuna (Katsuwonus pelamis), Yellowfin tuna
154
(Thunnus albacares), Japanese amberjack (Seriola quinqueradiata), Atlantic 8
ACS Paragon Plus Environment
Page 8 of 33
Page 9 of 33
Journal of Agricultural and Food Chemistry
155
salmon (Salmo salar) and Flying fish (Cypselurus pinnatibarbatus japonicus)
156
were obtained from fish wholesalers and retail markets in Japan. Total genomic
157
DNA in fish tissue (~50 mg) was extracted with a DNeasy Blood and Tissue Kit
158
(Qiagen, Hilden, Germany) in accordance with the protocol of the manufacturer.
159
In the case of whole body samples, fresh fins were collected for extraction. The
160
species of the pufferfish samples being studied were verified using the official
161
method of the Office of Import Food Safety, Inspection and Safety Division,
162
Department of Food Safety, Ministry of Health, Labour and Welfare, Japan
163
(2011), which was based on Sanger sequencing of the 16S ribosomal RNA
164
gene.6 The same method was also used to confirm the common names of other
165
fish samples with the aid of the BLAST search (DNA Data Bank of Japan).
166
Amplification and LC/ESI-MS analysis were performed as described above.
167 168
RESULTS AND DISCUSSION
169
Optimization of LC/ESI-MS conditions
170
Past studies dealing with LC/ESI-MS analysis of long oligonucleotides have
171
mostly been carried out using a poly(styrene-divinylbenzene) (PS-DVB) capillary
172
monolith column (0.2 mm i.d.) at low flow rate (2 µL/min).18–24,31 Instead, we
173
tested a narrow-bore type (2.0 mm i.d.) reverse-phase silica monolith column for
174
the separation of long oligonucleotides employing a much higher flow rate (400
175
µL/min), which enabled the use of a heated sprayer at the interface. Accordingly,
176
the DNA duplexes were denatured, regardless of column temperature, when the
9
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
177
mobile phase was sprayed into the ion source with the aid of heated nitrogen
178
(350 °C).
179
Column temperature was optimized (Figure 2). Signals for the three pairs of
180
DNA duplexes (26, 37 and 53 bp) and the primers were separated from one
181
another at 20 °C and 60 °C, whereas distorted peaks were observed at 40 °C.
182
These differences may be related to the formation of the double helix structure
183
during chromatographic separation. Oberacher et al reported that a DNA duplex
184
longer than 25–50 bp could be denatured in the analytical column at a
185
temperature between 50–80 °C.24 Accordingly, possible explanations for this
186
behavior are that the DNA duplexes maintained their rigid structure at 20 °C,
187
denatured partially at 40 °C, and denatured completely at 60 °C. Taking the
188
separation behavior and the maximum column temperature recommended by
189
the manufacturer (40 °C) into consideration, the column temperature was
190
adjusted to 20 °C. Despite the low column temperature, the maximum back
191
pressure of the system (12.5 MPa) was below the upper limit of the column (30
192
MPa) recommended by the manufacturer, owing to the inherently large channel
193
size of the silica monolith.32
194 195
Discrimination of synthetic DNA by PCR-RFLP coupled with LC/ESI-MS
196
The PCR-RFLP method was used to discriminate 11 synthetic DNA (range, 86
197
to 115 bp) samples (Table 1), which served as the positive control templates for
198
the pufferfish. The list for the target pufferfish was compatible with the published
199
method by the Japanese government based on the Sanger sequencing. The 10
ACS Paragon Plus Environment
Page 10 of 33
Page 11 of 33
Journal of Agricultural and Food Chemistry
200
exceptions to this were T. pardalis and T. snyderi and, given that the target
201
sequences for these two species are identical, T. pardalis was selected as being
202
a representative example. The result obtained by PAGE is shown in Figure 3a,
203
and that obtained by LC/ESI-MS is given in Figure 3b and Table 2. Using PAGE,
204
the band pattern could only be divided into three groups: Takifugu chrysops,
205
another species of genus Takifugu and genus Lagocephalus (Figure 3a). Each
206
band, which corresponded to the DNA duplex detected by PAGE, was also
207
detected by LC/ESI-MS as a peak (Figure 3b), and where each peak in the
208
chromatogram represented the mass spectra of the forward and reverse
209
oligonucleotides. Because the digestion with the endonucleases was performed
210
just after PCR amplification without purification, the sticky end generated by the
211
Msp I endonuclease was filled up with the remaining DNA polymerase during
212
incubation (Figure 1).12
213 214
Method validation
215
Accuracy and precision data for the LC/ESI-MS analyses are presented in Table
216
2. Although an internal mass standard was not used, excellent accuracy (mass
217
error, 0.83 ppm on average) and precision (standard deviation, 0.49 ppm on
218
average) were achieved. Although this performance reflects the inherent
219
performance of the Orbitrap analyzer, deconvolution also contributed to an
220
improved accuracy and precision. Because dozens of peaks having different
221
charge states and isotopic compositions are taken into account for the
222
calculation of a monoisotopic mass, the monoisotopic mass calculated by 11
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
223
deconvolution has a reduced observational error and must have been more
224
accurate than any molecular mass information determined from an individual
225
peak.30,33 In addition, the use of the monoisotopic mass for mass
226
characterization is preferable to that of the average mass for achieving
227
enhanced accuracy and precision.33 Because the monoisotopic mass is, for all
228
practical purposes, independent of the isotope ratio,34 the acquired data can be
229
directly compared with the theoretical monoisotopic mass calculated from the
230
molecular formula. An alternative mass spectrometry metric for a biomolecule is
231
the average mass, which is defined as the centroid of the isotopic distribution of
232
the biomolecule. However, according to a calculation by Zubarev et al, the
233
accuracy of the average mass measurement is limited to 10 ppm for
234
biomolecules larger than 10,000 Da because of natural variations of isotopic
235
abundances of the elements. Furthermore, the non-symmetric shape of the
236
isotopic distribution causes negative bias.33 Manduzio et al reported an average
237
mass deviation of 9.15 ± 7.11 ppm as a result of analyzing a 114-bp PCR
238
product despite an Orbitrap analyzer being used.12 Kullolli et al used an
239
LTQ-Orbitrap Veros for analyzing microRNA ranging from 22 to 25 nt.35 A mass
240
accuracy of 1.3 ppm on average was reported; however, these studies
241
compared the monoisotopic peaks of the multiply charged ions with the
242
corresponding theoretical ones instead of the deconvoluted monoisotopic mass
243
of the molecule. Because the monoisotopic peak disappears from a mass
244
spectrum with increasing molecular mass,33 the approach involving the
245
monoisotopic peaks is only applicable for short oligonucleotides. 12
ACS Paragon Plus Environment
Page 12 of 33
Page 13 of 33
Journal of Agricultural and Food Chemistry
246
Periodic analyses were carried out to evaluate the stability of mass accuracy.
247
Digested amplicons derived from the synthetic DNA of Takifugu chrysops were
248
analyzed every 10 h for 180 h. As a result, all the monoisotopic masses of the
249
digested PCR amplicons were successfully determined within a mass error of
250
2.8 ppm without any additional mass calibration. Consequently, a daily
251
calibration can be replaced by a weekly calibration.
252
As a result of the above findings and observations, a flow chart for the
253
discrimination of the pufferfish is proposed (Figure 4). The target pufferfish
254
always yields two or three peaks in the TIC chromatogram at a retention time of
255
4–5.5 min; otherwise the sample is not the target pufferfish. If two peaks are
256
observed in the range, a pair of the monoisotopic masses of the DNA duplex
257
corresponding to the latter peak will be compared to the theoretical values to
258
determine if any one of the species is T. chrysops, L. inermis, L. gloveri, L.
259
lunaris or L. wheeleri. The mass tolerance for the determination is 3 ppm which
260
does not cause overlap. If three peaks are observed in the range, a similar
261
matching procedure is required for the second peak in some cases as well as for
262
the third peak (Figure 4).
263 264
Mixed template
265
The synthetic DNA template of Lagocephalus lunaris was mixed with that of L.
266
wheeleri at ratios of 1:1, 1:4 and 1:19, and the mixtures were analyzed as
267
described above. As the result of the preparation, four pairs of DNA duplexes
268
would have existed in the sample solution and the success of the discrimination 13
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
269
relies on the difference of the masses between each oligonucleotide. The results
270
are shown in Figure 5. In the case when the mass difference was about 25 Da
271
(Figure 5a, single base substitution) and 7 Da (Figure 5b, triple base
272
substitution), each strand could be analyzed independently for the mixing ratio of
273
1:1; however, minor constituents could not be calculated properly. When the
274
difference was about 6 Da (Figure 5c, the complementary sequence of Figure 5b)
275
because of an overlapping of clusters of peaks, the isotopic mass could not
276
calculated even for a mixing ratio of 1:1 although this could be compensated for
277
by the results for the complementary strand. These observations are basically
278
consistent with the study of Manduzio et al who investigated the discrimination
279
ability for an equal mixture of templates with single base substitution.12 They
280
reported that a mass difference of 16 Da (A G) could be discriminated,
281
although that of 9 Da (T A) could not be discriminated for analysis of 114 bp
282
DNA. This was overcome by emphasizing the difference of the m/z values using
283
endonuclease digestion, which is consistent with the present strategy.
284
As an alternative to calculating the monoisotopic mass, the extracted ion
285
chromatograms (XICs) of the most abundant isotopic ions were examined as a
286
means to discriminate T. rubripes from T. pardalis. However, it was impossible to
287
discriminate the two species using XIC because of the overlapping of the peaks
288
(Figure 6), although they could be discriminated using a deconvolution approach
289
(Table 2). Therefore, deconvolution was the preferred approach for species
290
identification, especially when the sample was considered to be derived from a
291
single source. 14
ACS Paragon Plus Environment
Page 14 of 33
Page 15 of 33
Journal of Agricultural and Food Chemistry
292 293
Application for small samples
294
A small amount of pufferfish alone or its presence in another fish was analyzed
295
by the present methods. As a result of the analysis of a raw muscle tissue
296
homogenate of T. vermicularis (0.1 mg equivalent, n = 2), all the expected DNA
297
fragments were successfully identified with an average mass error of 1.50 ppm.
298
In addition, raw muscle tissue of T. vermicularis mixed with that of Korean black
299
scraper (Thamnaconus modestus) (2.5 wt % of T. vermicularis in 50 mg mixture)
300
could be identified with an average mass error of 1.15 ppm (n = 2). Therefore,
301
the present method is considered applicable to small sample amounts as long as
302
PCR amplification proceeds successfully.
303 304
Discrimination of pufferfish and other fish samples
305
The present method was applied to 29 pufferfish samples and 8 other fish
306
species (Figure 7). The results for discrimination based on the present criteria
307
(Figure 4) were consistent with the official method based on Sanger sequencing,
308
although the present method could not discriminate T. pardalis from T. snyderi
309
because these species contain the same amplicon sequence (data not shown).
310
Additionally, no deconvolution value was calculated from the chromatograms of
311
fish samples other than pufferfish.
312
As mentioned above, the use of LC/ESI-MS for fish genotyping has been
313
demonstrated for the first time. A remaining problem is the interpretation of data
314
obtained from a mixed template at a closer ratio as mentioned above. Using 15
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
315
multiplex PCR with another pair of pufferfish-specific or species-specific primers
316
may be an effective way for resolving analytes in a mixture.
317 318
Funding
319
This work was supported by a Grant-in-Aid for Scientific Research by the Japan
320
Society for the Promotion of Science (15K08060).
321
16
ACS Paragon Plus Environment
Page 16 of 33
Page 17 of 33
Journal of Agricultural and Food Chemistry
322
REFERENCES
323
(1)
324
Distribution of tetrodotoxin in pufferfish collected from coastal waters of
325
Sihanouk Ville, Cambodia. Shokuhin Eiseigaku Zasshi 2008, 49, 361–365.
326
(2)
327
White, K. D.; Thompson, T. M.; Wahl, M.; Pham, T. D.; Guichard, F. M.; Huh, I.;
328
Austin, C.; Dizikes, G.; Gerber, S. I., Public health response to puffer fish
329
(tetrodotoxin) poisoning from mislabeled product. J. Food Prot. 2009, 72, 810–
330
817.
331
(3)
332
M.; Centers for Disease, C.; Prevention, Tetrodotoxin poisoning outbreak from
333
imported dried puffer fish — Minneapolis, Minnesota, 2014. MMWR Morb. Mortal.
334
Wkly. Rep. 2015, 63, 1222–1225.
335
(4)
336
Hwang, D.-F., Puffer fish-based commercial fraud identification in a segment of
337
cytochrome b region by PCR–RFLP analysis. Food Chem. 2010, 121, 1305–
338
1311.
339
(5)
340
puffer fish inferred from partial sequences of cytochrome b gene and restriction
341
fragment length polymorphism analysis. J. Agric. Food Chem. 2004, 52, 4159–
342
4165.
343
(6)
344
Shiomi, K.; Watabe, S., Molecular identification of pufferfish species using PCR
Ngy, L.; Taniyama, S.; Shibano, K.; Yu, C. F.; Takatani, T.; Arakawa, O.,
Cohen, N. J.; Deeds, J. R.; Wong, E. S.; Hanner, R. H.; Yancy, H. F.;
Cole, J. B.; Heegaard, W. G.; Deeds, J. R.; McGrath, S. C.; Handy, S.
Hsieh, C.-H.; Chang, W.-T.; Chang, H. C.; Hsieh, H.-S.; Chung, Y.-L.;
Hsieh, Y. W.; Hwang, D. F., Molecular phylogenetic relationships of
Ishizaki, S.; Yokoyama, Y.; Oshiro, N.; Teruya, N.; Nagashima, Y.;
17
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 18 of 33
345
amplification and restriction analysis of a segment of the 16s rRNA gene. Comp.
346
Biochem. Physiol. Part D Genomics Proteomics 2006, 1, 139–144.
347
(7)
348
assay for the detection of pufferfish products. J. Food Prot. 2010, 73, 1698–
349
1702.
350
(8)
351
of the genus Lagocephalus: L. lunaris, L. spadiceus and L. inermis, using
352
multiplex PCR. Food Biotechnol. 2014, 28, 216–231.
353
(9)
354
Overview of recent developments in the mass spectrometry of nucleic acid and
355
constituents. In Mass spectrometry of nucleosides and nucleic acids, Banoub, J.
356
H.; Limbach, P. A., Eds. CRC Press: Boca Raton, FL, 2010; pp 1–90.
357
(10)
358
for characterization of sequence variability in genomic DNA. Anal. Bioanal.
359
Chem. 2008, 391, 135–149.
360
(11)
361
analysis
362
charge-tagging. Nucleic Acids Res. 2003, 31, e63.
363
(12)
364
mass spectrometer for the analysis of polymerase chain reaction products.
365
Rapid Commun. Mass Spectrom. 2010, 24, 3501–3509.
366
(13)
367
approaches for purifying and desalting polymerase chain reaction products prior
Jones, Y. L.; Oliver, H. F.; Deeds, J. R.; Yancy, H. F., Real-time PCR
Sangthong, P.; Ngernsiri, L.; Sangthong, D., Identification of puffer fish
Banoub, J. H.; Miller-Banoub, J.; Jahouh, F.; Joly, N.; Martin, P.,
Oberacher, H., On the use of different mass spectrometric techniques
Sauer, S.; Lehrach, H.; Reinhardt, R., MALDI mass spectrometry of
single
nucleotide
polymorphisms
by
photocleavage
and
Manduzio, H.; Ezan, E.; Fenaille, F., Evaluation of the LTQ-Orbitrap
Manduzio, H.; Martelet, A.; Ezan, E.; Fenaille, F., Comparison of
18
ACS Paragon Plus Environment
Page 19 of 33
Journal of Agricultural and Food Chemistry
368
to electrospray ionization mass spectrometry. Anal. Biochem. 2010, 398, 272–
369
274.
370
(14)
371
thermal denaturation for the production of single-stranded PCR amplicons:
372
Piperidine-induced destabilization of the DNA duplex? J. Am. Soc. Mass
373
Spectrom. 2002, 13, 232–240.
374
(15)
375
characterization of nucleic acids by electrospray ionization mass spectrometry.
376
Rapid Commun. Mass Spectrom. 2003, 17, 2699–2706.
377
(16)
378
preparation techniques for mass measurements of PCR products using
379
ESI-FT-ICR mass spectrometry. J. Am. Soc. Mass Spectrom. 2002, 13, 338–
380
344.
381
(17)
382
synthetic nucleic acids by electrospray ionization quadrupole time-of-flight mass
383
spectrometry. J. Mass Spectrom. 2005, 40, 932–945.
384
(18)
385
chromatography–mass spectrometry. Mass Spectrom. Rev. 2001, 20, 310–343.
386
(19)
387
chromatography and mass spectrometry. In Handbook of analysis of
388
oligonucleotides and related products, Bonilla, J. V.; Srivatsa, G. S., Eds. CRC
389
Press: Boca Raton, FL, 2011; pp 137–166.
390
(20)
Mangrum, J. B.; Flora, J. W.; Muddiman, D. C., Solution composition and
Null, A. P.; Benson, L. M.; Muddiman, D. C., Enzymatic strategies for the
Null, A. P.; George, L. T.; Muddiman, D. C., Evaluation of sample
Oberacher, H.; Niederstatter, H.; Parson, W., Characterization of
Huber, C. G.; Oberacher, H., Analysis of nucleic acids by on-line liquid
Pourshahian, S.; McCarthy, S. M., Analysis of oligonucleotides by liquid
Beer, B.; Erb, R.; Pitterl, F.; Niederstatter, H.; Maroñas, O.; Gesteira, A.; 19
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
391
Carracedo, A.; Piatkov, I.; Oberacher, H., CYP2D6 genotyping by liquid
392
chromatography-electrospray ionization mass spectrometry. Anal. Bioanal.
393
Chem. 2011, 400, 2361–2370.
394
(21)
395
Identification of bacteria by polymerase chain reaction followed by liquid
396
chromatography–mass spectrometry. Anal. Chem. 2005, 77, 4563–4570.
397
(22)
398
chromatography mass spectrometry: A useful tool for the detection of DNA
399
sequence variation. Angew. Chem. Int. Ed. Engl. 2001, 40, 3828–3830.
400
(23)
401
Optimized suppression of adducts in polymerase chain reaction products for
402
semi-quantitative SNP genotyping by liquid chromatography-mass spectrometry.
403
J. Am. Soc. Mass Spectrom. 2004, 15, 1897–1906.
404
(24)
405
polymerase chain reaction products by on-line liquid chromatography–mass
406
spectrometry for genotyping of polymorphic short tandem repeat loci. Anal.
407
Chem. 2001, 73, 5109–5115.
408
(25)
409
M., Toxicity and molecular identification of green toadfish Lagocephalus lunaris
410
collected from Kyushu coast, Japan. J. Toxicol. 2011, 2011, 801285.
411
(26)
412
Doi, H.; Takahashi, H.; Mabuchi, K.; Nishida, M.; Sakai, H., Explosive speciation
413
of Takifugu: Another use of fugu as a model system for evolutionary biology. Mol.
Mayr, B. M.; Kobold, U.; Moczko, M.; Nyeki, A.; Koch, T.; Huber, C. G.,
Oberacher, H.; Oefner, P. J.; Parson, W.; Huber, C. G., On-line liquid
Oberacher, H.; Parson, W.; Hölzl, G.; Oefner, P. J.; Huber, C. G.,
Oberacher, H.; Parson, W.; Muhlmann, R.; Huber, C. G., Analysis of
Nagashima, Y.; Matsumoto, T.; Kadoyama, K.; Ishizaki, S.; Terayama,
Yamanoue, Y.; Miya, M.; Matsuura, K.; Miyazawa, S.; Tsukamoto, N.;
20
ACS Paragon Plus Environment
Page 20 of 33
Page 21 of 33
Journal of Agricultural and Food Chemistry
414
Biol. Evol. 2009, 26, 623–629.
415
(27)
416
modified oligonucleotides by tandem ion-pair reversed-phase high-performance
417
liquid chromatography/electrospray ionization mass spectrometry. Rapid
418
Commun. Mass Spectrom. 2003, 17, 646–653.
419
(28)
420
as a tune/calibration compound for positive- and negative-ion electrospray
421
ionization mass spectrometry in the mass range of 100–4000 Da. J. Am. Soc.
422
Mass Spectrom. 1998, 9, 977–980.
423
(29)
424
interpretation of high resolution electrospray mass spectra of large molecules. J.
425
Am. Soc. Mass Spectrom. 2000, 11, 320–332.
426
(30)
427
monoisotopic masses and ion populations for large biomolecules from resolved
428
isotopic distributions. J. Am. Soc. Mass Spectrom. 1995, 6, 229–233.
429
(31)
430
chromatography–electrospray ionization mass spectrometry of single- and
431
double-stranded nucleic acids using monolithic capillary columns. Anal. Chem.
432
2000, 72, 4386–4393.
433
(32)
434
nucleic
435
ionization mass spectrometry. Trends Anal. Chem. 2002, 21, 166–174.
436
(33)
Fountain, K. J.; Gilar, M.; Gebler, J. C., Analysis of native and chemically
Moini, M.; Jones, B. L.; Rogers, R. M.; Jiang, L., Sodium trifluoroacetate
Horn, D. M.; Zubarev, R. A.; McLafferty, F. W., Automated reduction and
Senko, M. W.; Beu, S. C.; McLafferty, F. W., Determination of
Premstaller, A.; Oberacher, H.; Huber, C. G., High-performance liquid
Oberacher, H.; Huber, C. G., Capillary monoliths for the analysis of acids
by
high-performance
liquid
chromatography–electrospray
Zubarev, R. A.; Demirev, P. A.; Håkansson P.; Sundqvist B. U. R., 21
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
437
Approaches and limits for accurate mass characterization of large biomolecules.
438
Anal. Chem. 1995, 67, 3793–3798.
439
(34)
440
distributions in mass spectra of large molecules. Anal. Chem. 1983, 55, 353–
441
356.
442
(35)
443
microRNA analysis using high resolution mass spectrometry. J. Am. Soc. Mass
444
Spectrom. 2014, 25, 80–87.
Yergey, J.; Heller, D.; Hansen, G.; Cotter, R. J.; Fenselau, C., Isotopic
Kullolli, M.; Knouf, E.; Arampatzidou, M.; Tewari, M.; Pitteri, S. J., Intact
445
22
ACS Paragon Plus Environment
Page 22 of 33
Page 23 of 33
Journal of Agricultural and Food Chemistry
446
FIGURE CAPTIONS
447
Figure 1. Method summary. Bold indicates the nucleotides filled up with the
448
remaining DNA polymerase. p indicates a phosphate group.
449
Figure 2. Chromatograms of the PCR products of the synthetic DNA of Takifugu
450
rubripes for comparison of temperatures for the MonoBis C18 column. TIC, total
451
ion current.
452
Figure 3. Results for PCR-RFLP analysis of synthetic pufferfish DNA. a, PAGE;
453
b, LC/ESI-MS.
454
Figure 4. Flow chart for the discrimination of pufferfish. TIC, total ion current. RT,
455
retention time.
456
Figure 5. Total ion current chromatograms obtained from the mixed templates.
457
nt, nucleotides.
458
Figure 6. An example of failure of discrimination between T. rubripes and T.
459
pardalis using individual isotopic peaks. nt, nucleotides.
460
Figure 7. Total ion current chromatograms derived from actual fish samples.
461
23
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Table 1
Page 24 of 33
DNA Sequences Used for the PCR Templates.
Species
DNA sequencesa
Takifugu rubripes Takifugu porphyreus
CCATGTGGAATGAAAACACCCTTTTTAAACCCAAGAGTCACCACTCTAGGATACAGAACATCTGACCAAT-AATGATCCGGCT-AAAGCCGATTAACGAACCGAGTTACCCTAGGG
Length (nt)b 114
Refer encec (26)
Accession No. AP006045
CCATGTGGAATGAAAACACCCTTTTTAAAACCAAGAGTCACCACTCTAGGATACAGAACATCTGACCAAT-AATGATCCGGCT-AAAGCCGATTAACGAACCGAGTTACCCTAGGG
114
(26)
AP009529
Takifugu chrysops
CCATGTGGAATGAAGACACCCTCTCTAAAACCAAGAGTCACCACTCTAAGTTACAGAACATCTGACCAAT-AATGATCCGGCT-AAAGCCGATTAACGAACCGAGTTACCCTAGGG
114
(26)
AP009525
Takifugu vermicularis
CCATGTGGAATGAAAACACCCTTTTTAAAACCAAGAGTCACCACTCTAAGTTACAGAACATCTGACCAATTAATGATCCGGCT-AAAGCCGATTAACGAACCGAGTTACCCTAGGG
115
–
AB741999
Takifugu pardalis
CCATGTGGAATGAAAACACCCTTTTTAAAACCAAGAGTCACCACTCTAAGTTACAGAACATCTGACCAAT-AATGATCCGGCT-AAAGCCGATTAACGAACCGAGTTACCCTAGGG
114
(26)
AP009528
Takifugu niphobles
CCATGTGGAATGAAAACACCCTTTTTAAAACCAAGAGTCACCACTCTAAGTTACAGAACATCTGACCAAT-AATGATCCGGCTTAAAGCCGATTAACGAACCGAGTTACCCTAGGG
115
(26)
AP009526
Takifugu poecilonotus
CCATGTGGAATGAAAACACCCTTTTTAAAACCAAGAGTCACCACTCTAAGTTACAGAACATCTGACCAGT-AATGATCCGGCTT-AAGCCGATTAACGAACCGAGTTACCCTAGGG
114
(26)
AP009539 AP009538
Lagocephalus wheeleri
AAAAAC-AAGAGCCACAGCTCTAATGAGCAGAACATCTGACCTACCA--GATCCGGC--ATAGCCGATCAACGAACCGAGTTACCCTAGGG
86
(26)
Lagocephalus gloveri
AAAAAC-AAGAGCCACAGCTCTAATGAACAGAACATCTGACCTACCA--GATCCGGC--ATAGCCGATCAACGAACCGAGTTACCCTAGGG
86
–
AB742032
Lagocephalus lunaris
AAAAAC-AAGAGCCACAGCTCTAATAAACAGAACATCTGACCAGCCA--GATCCGGC--CTAGCCGATCAACGAACCGAGTTACCCTAGGG
86
(25)
Not available
Lagocephalus inermis
AAAAAC-AAGAGCCACAGCTCTAATAAACAGAACATCTGACCCACCA--GATCCGGC--ACAGCCGATCAACGAACCGAGTTACCCTAGGG
86
–
AB742030
a
Underline indicates primer-binding site and bold indicates the recognition sites of the restriction enzymes. bnt, nucleotide. c–, unpublished.
24
ACS Paragon Plus Environment
Page 25 of 33
Journal of Agricultural and Food Chemistry
Table 2
LC/ESI-MS Analysis of the Amplicons Digested with the Endonucleases.
Species
T. rubripes
T. porphyreus
T. chrysops
T. vermicularis
T. pardalis
T. niphobles
T. poecilonotus
L. wheeleri
L. gloveri
L. lunaris
L. inermis
F/Ra
F F F R R R F F F R R R F F R R F F F R R R F F F R R R F F F R R R F F F R R R F F R R F F R R F F R R F F R R
Length (nt)b
26 53 37 37 53 26 26 53 37 37 53 26 79 37 37 79 26 54 37 37 54 26 26 53 37 37 53 26 26 53 38 38 53 26 26 53 37 37 53 26 52 36 52 36 52 36 52 36 52 36 52 36 52 36 52 36
Expected molecular Monoisotopic mass, n = 5 (interday) formula Theoretical Measured value Relative value (Da) (Da, average ± standard standard deviation) deviation (ppm) C254H321O154N94P25 7925.362 7925.366 ± 0.003 0.37 C515H647O307N208P53 16296.750 16296.763 ± 0.006 0.34 11466.909 11466.920 ± 0.002 0.18 C360H452O218N147P37 C360H456O225N132P36 11341.885 11341.890 ± 0.003 0.25 C522H659O331N186P53 16468.655 16468.661 ± 0.004 0.25 8085.340 8085.352 ± 0.001 0.13 C256H322O157N98P26 C254H321O154N94P25 7925.362 7925.367 ± 0.004 0.44 C516H647O306N210P53 16320.762 16320.764 ± 0.017 1.05 C360H452O218N147P37 11466.909 11466.919 ± 0.006 0.50 C360H456O225N132P36 11341.885 11341.892 ± 0.004 0.33 C522H660O332N183P53 16443.648 16443.651 ± 0.010 0.62 C256H322O157N98P26 8085.340 8085.350 ± 0.002 0.28 C768H965O458N303P78 24173.107 24173.129 ± 0.017 0.70 C360H452O218N147P37 11466.909 11466.918 ± 0.006 0.56 C360H456O225N132P36 11341.885 11341.891 ± 0.006 0.52 C779H980O489N283P79 24566.979 24567.021 ± 0.016 0.64 C254H321O154N94P25 7925.362 7925.367 ± 0.004 0.46 C526H661O314N209P54 16599.801 16599.821 ± 0.009 0.56 11466.909 11466.922 ± 0.006 0.49 C360H452O218N147P37 C360H456O225N132P36 11341.885 11341.890 ± 0.005 0.48 C533H672O336N190P54 16780.717 16780.724 ± 0.004 0.21 C256H322O157N98P26 8085.340 8085.349 ± 0.005 0.65 7925.362 7925.367 ± 0.002 0.30 C254H321O154N94P25 C516H648O307N207P53 16295.755 16295.764 ± 0.020 1.21 C360H452O218N147P37 11466.909 11466.922 ± 0.007 0.60 11341.885 11341.889 ± 0.006 0.49 C360H456O225N132P36 C523H660O331N185P53 16467.659 16467.671 ± 0.011 0.66 8085.340 8085.350 ± 0.003 0.36 C256H322O157N98P26 C254H321O154N94P25 7925.362 7925.367 ± 0.005 0.64 C516H648O307N207P53 16295.755 16295.764 ± 0.012 0.76 C370H465O225N149P38 11770.955 11770.971 ± 0.005 0.41 11654.943 11654.951 ± 0.004 0.30 C370H468O230N137P37 16467.659 16467.666 ± 0.006 0.34 C523H660O331N185P53 C256H322O157N98P26 8085.340 8085.353 ± 0.003 0.38 C254H321O154N94P25 7925.362 7925.369 ± 0.005 0.61 16311.750 16311.730 ± 0.014 0.84 C516H648O308N207P53 C360H453O220N144P37 11457.898 11457.910 ± 0.003 0.23 C360H455O223N135P36 11350.897 11350.892 ± 0.007 0.62 16452.660 16452.664 ± 0.007 0.45 C522H659O330N186P53 C256H322O157N98P26 8085.340 8085.349 ± 0.003 0.33 15937.744 15937.761 ± 0.008 0.48 C505H632O296N209P51 11138.852 11138.844 ± 0.010 0.87 C349H439O212N143P36 C511H647O327N179P52 16131.586 16131.595 ± 0.006 0.39 C350H443O219N130P35 11053.834 11053.844 ± 0.004 0.38 C505H632O295N209P51 15921.750 15921.765 ± 0.007 0.46 C349H439O212N143P36 11138.852 11138.848 ± 0.006 0.50 C512H648O328N178P52 16146.585 16146.580 ± 0.009 0.54 C350H443O219N130P35 11053.834 11053.849 ± 0.010 0.89 C505H631O293N212P51 15930.761 15930.776 ± 0.006 0.36 C348H439O213N141P36 11114.841 11114.846 ± 0.006 0.58 C512H649O330N175P52 16137.574 16137.583 ± 0.007 0.42 C350H442O218N133P35 11078.841 11078.836 ± 0.003 0.24 C504H631O293N210P51 15890.755 15890.773 ± 0.006 0.38 C348H438O211N144P36 11123.852 11123.851 ± 0.004 0.35 C513H649O330N177P52 16177.580 16177.590 ± 0.005 0.33 C350H443O220N130P35 11069.829 11069.836 ± 0.008 0.71
a
Average mass errorc (ppm) 0.57 0.80 0.93 0.45 0.42 1.44 0.73 0.78 0.85 0.60 0.53 1.19 0.92 0.84 0.58 1.69 0.69 1.21 1.11 0.42 0.40 1.06 0.64 1.11 1.08 0.51 0.76 1.21 0.82 0.80 1.36 0.74 0.39 1.57 0.91 1.21 1.10 0.53 0.42 1.07 1.04 0.90 0.61 0.88 0.94 0.49 0.51 1.33 0.96 0.51 0.59 0.37 1.10 0.26 0.64 0.84
F, forward strand; R, reverse strand (see Figure 1). bnt, nucleotide. cMass error is defined as the absolute deviation of a measured monoisotopic mass from the theoretical one.
25
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Fish sample
DNA extraction
PCR
Enzymatic digestion
LC/ ESI-MS
Data analysis
Genus Takifugu (except for Takifugu chrysops) Forward primer for Takifugu 5ʹ 3ʹ 26 bp
Dra I digestion
Msp I digestion
TTT pAAA AAAp TTT
CCG pCGG GGCp GCC
53–54 bp
37–38 bp
3ʹ 5ʹ
Reverse primer
Takifugu chrysops Forward primer for Takifugu 5ʹ 3ʹ
Msp I digestion CCG pCGG GGCp GCC
TCTAAA AGATTT
37 bp
3ʹ 5ʹ
Reverse primer
79 bp
Genus Lagocephalus Forward primer for Lagocephalus
Msp I digestion CCG pCGG GGCp GCC
5ʹ 3ʹ 52 bp
36 bp
3ʹ 5ʹ
Reverse primer
Figure 1
26
ACS Paragon Plus Environment
Page 26 of 33
Page 27 of 33
Journal of Agricultural and Food Chemistry
Relative intensity
20 °C
60 °C
40 °C
1.04 ×107
4.53 ×106
1.08 ×107
0 1.06 ×105
0 2.43 ×104
0 7.86 ×104
26 bp
0 6.80 ×104 37 bp 0 7.43 ×104
53 bp
0 6.50 ×104
m/z = 2835.720 + 2866.976
37 bp
37 bp 0 2.52 ×104
0 8.45 ×104 53 bp
53 bp 0 6
m/z = 2641.785 + 2695.111
26 bp
26 bp 0 2.04 ×104
0 3
TIC
m/z = 1163.548 + 1175.827
0 3
6
3
6
Time / min
Figure 2
27
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Figure 3
28
ACS Paragon Plus Environment
Page 28 of 33
Page 29 of 33
Journal of Agricultural and Food Chemistry
Draw TIC chromatogram
≤1
Peak Number at RT = 4–5.5 min
3
Negative
(genus Takifugu) 2 (Takifugu chrysops or genus Lagocephalus)
Monoisotopic mass of the 3rd peak(Da)
Monoisotopic mass of the 2nd peak (Da)
16443.599–16443.697 16452.610–16452.709 16467.610–16467.709 16468.605–16468.704
T. poecilonotus T. exascurusa
16400
6
16500 16599.751–16599.851 16780.667–16780.767
16200
T. vermicularis
16131.537–16131.634 16137.525–16137.622 16146.537–16146.634 16177.531–16177.629
T. chrysops
24173.034–24173.179 24566.905–24567.053
T. porphyreus T. obscurusa
L. lunaris
L. gloveri
L. wheeleri
15890.707–15890.803 15921.702–15921.797 15930.713–15930.809 15937.697–15937.792
16000
16100
16300
6
L. inermis
15900
5 Time / min
5 Time / min
T. rubripes
4
4
16295.706–16295.804 16296.701–16296.799 16311.701–16311.799 16320.713–16320.811
Monoisotopic mass of the 2nd peak (Da)
4
11300
5 Time / min
11466.875–11466.944 11500 11600
11770.920–11770.991 11800
Figure 4
29
ACS Paragon Plus Environment
T. niphobles
11654.908–11654.978 11700
T. pardalis T. snyderi T. ocellatusa T. xanthopterusa T. stictonotusa
11341.851–11341.919 11400
6
Journal of Agricultural and Food Chemistry
a 36 nt, reverse strand [M-4H]4-, ∆ = 25.006 (Da)
L. wheeleri : L. lunaris
L. wheeleri 0.48 ppm
b 52 nt, forward strand [M-5H]5- , ∆ = 6.983 (Da) L. lunaris 0.29 ppm
L. wheeleri 0.82 ppm
L. lunaris 0.70 ppm
4:1
L. wheeleri 1.04 ppm
19:1
2760
L. wheeleri NA
L. wheeleri 2.34 ppm
L. lunaris NA
L. wheeleri 0.62 ppm
L. wheeleri 2.38 ppm
L. lunaris NA
2770
c 52 nt, reverse strand [M-5H]5- , ∆ = 5.988 (Da)
L. wheeleri 2.97 ppm
L. lunaris 0.44 ppm
1:1
L. wheeleri 0.60 ppm
L. lunaris NA
3180
3190
Figure 5
30
ACS Paragon Plus Environment
Page 30 of 33
3220
L. lunaris NA
L. lunaris NA
L. lunaris NA
3230
m/z
Page 31 of 33
Journal of Agricultural and Food Chemistry
Figure 6
31
ACS Paragon Plus Environment
Relative intensity
Journal of Agricultural and Food Chemistry
2.39×106
Negative control
0 3.60×107
T. rubripes
0 4.11×107
T. porphyreus
0 3.95×107
T. vermicularis
0 3.65×107
T. pardalis
0 1.63×107
T. snyderi
0 3.55×107
T. poecilonotus
0 3.07×107
L. wheeleri
0 6.17×106
Atlantic mackerel (Scomber scombrus)
0 4.15×106 0 4.63×106 0 2.09×106 0 1.86×106
0 2.67×106
Japanese horse mackerel (Trachurus japonicus)
Japanese pilchard (Sardinops melanostictus)
Skipjack tuna (Katsuwonus pelamis)
Yellowfin tuna (Thunnus albacares)
Japanese amberjack (Seriola quinqueradiata)
0 6.51×106
Atlantic salmon (Salmo salar)
0 2.81×106
Flying fish (Cypselurus pinnatibarbatus japonicus)
0
3.5
4.0
4.5 5.0 Time / min
5.5
6.0
Figure 7
32
ACS Paragon Plus Environment
Page 32 of 33
Page 33 of 33
Journal of Agricultural and Food Chemistry
Graphic for TOC
33
ACS Paragon Plus Environment