Subscriber access provided by UNIV OF NEWCASTLE
Article
The foliar desiccators glyphosate, carfentrazone and paraquat affect the technological and chemical properties of cowpea grains Igor da Silva Lindemann, Gustavo Heinrich Lang, Jessica Fernanda Hoffmann, Cesar Valmor Rombaldi, Mauricio de Oliveira, Moacir Cardoso Elias, and Nathan Levien Vanier J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b01912 • Publication Date (Web): 21 Jul 2017 Downloaded from http://pubs.acs.org on July 25, 2017
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
1
The foliar desiccators glyphosate, carfentrazone and paraquat affect the
2
technological and chemical properties of cowpea grains
3 4
Igor da Silva Lindemann1, Gustavo Heinrich Lang1, Jessica Fernanda Hoffmann1, Cesar
5
Valmor Rombaldi1, Maurício de Oliveira1, Moacir Cardoso Elias1, Nathan Levien
6
Vanier1*
7 8
1
9
96010-900, Pelotas, RS, Brazil
Department of Agroindustrial Science and Technology, Federal University of Pelotas,
10 11
Igor da Silva Lindemann (
[email protected])
12
Gustavo Heinrich Lang (
[email protected])
13
Jessica Fernanda Hoffmann (
[email protected])
14
Cesar Valmor Rombaldi (
[email protected])
15
Maurício de Oliveira (
[email protected])
16
Moacir Cardoso Elias (
[email protected])
17 18
* Corresponding author: Nathan Levien Vanier (
[email protected])
19
Tel/Fax: +005553981175570
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
20
Abstract
21
The effects of the use of glyphosate (GLY), glyphosate plus carfentrazone (GLY/CAR),
22
and paraquat (PAR) as plant desiccators on the technological and chemical properties of
23
cowpea grains were investigated. All studied desiccants provided lower cooking time to
24
freshly harvested cowpea. However, the coat color of PAR- and GLY/CAR-treated
25
cowpea was reddish than control treatment. Principal component analysis (PCA) from
26
liquid chromatography-mass spectrometry (LC-MS) data sets showed a clear distinction
27
among cowpea from the different treatments. Catechin-3-glucoside and epicatechin
28
significantly contributed for discriminating GLY-treated cowpea, while citric acid was
29
responsible for discriminating GLY/CAR-treated cowpea. Quercetin derivative and
30
gluconic acid were responsible for discriminating control treatment. Residual
31
glyphosate and paraquat content was higher than the maximum limits allowed by Codex
32
Alimentarius and European Union Commission. Improvements in the technological and
33
chemical properties of cowpea may not be overlapped by the risks that those desiccants
34
exhibit when exceeding the maximum limits of tolerance in food.
35
Keywords: Vigna unguiculata, coat color, cooking time, phenolics, storage of cowpea.
ACS Paragon Plus Environment
Page 2 of 33
Page 3 of 33
Journal of Agricultural and Food Chemistry
36
1. Introduction
37
Cowpea (Vigna unguiculata L.) is considered a good source of carbohydrates,
38
proteins, fibers, vitamins, as well as iron and zinc.1 Moreover, cowpea exhibits phenolic
39
compounds
40
antihypertensive properties, which are distributed mainly in the grain coat, but are also
41
present in cotyledon. Those compounds include flavonols, phenolic acids, flavan-3-ols
42
and anthocyanins.2
with
putative
antioxidant,
antimutagenic,
anti-inflammatory
and
43
Once the plants from cowpea are resistant to dry- and warm-weather conditions,
44
they are mainly cultivated in semi-arid regions all over the world.3 In Brazil, cowpea
45
was firstly cultivated in small farms located in the North and Northeast of the country;4
46
however, nowadays, cowpea has been cultivated in huge farms located in the Center-
47
East of the country, where the manual harvesting gave space to the mechanical
48
harvesting, since the harvested area in each farm may vary from few hundreds to more
49
than 3,000 hectares.
50
Cowpea naturally exhibit indeterminate growth type of plant. This means that
51
the plants may retain green leaves during grain ripening, which impairs or delays
52
mechanical harvesting.5 Thus, desiccation treatment is required in order to allow the
53
mechanical harvesting of cowpea. The strategy is largely employed in major crops,
54
especially in species and cultivars expressing stay-green phenotype.6 Between the most
55
commonly herbicides used by Brazilian farmers and in other countries are glyphosate,
56
protox inhibitors and paraquat, as well as the combination of glyphosate and protox
57
inhibitors in the same spraying treatments. It is important to note that the cited
58
herbicides have the post-harvest interval varying from 2 days (glyphosate) to 7 days
59
(paraquat). The farmers utilize these treatments in order to mechanically harvest the
60
crop with lower losses, lower fuel consumption and better production yield.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 4 of 33
61
Glyphosate acts by inhibition of the 5-enolpiruvil-shikimato-3-fosfato synthase
62
(EPSPS) enzyme, which participate in the shikimate pathway. Once this molecule is
63
applied as herbicide, the synthesis of aromatic amino acids is stopped, which, in turn,
64
impair the synthesis of proteins and some specialized metabolites.7,8 Intermediate toxic
65
compounds could be also synthesized when glyphosate is metabolized, but it is still not
66
fully understood.9
67
In
order
to
improve
glyphosate
efficiency,
some
herbicides
from
68
protoporphyrinogen oxidase (Protox) group are used in combination. Protox inhibitors
69
are powerful inhibitors of the Protox enzyme, responsible for the chlorophyll and heme
70
biosynthesis. In sum, this enzyme catalyzes the oxidation of protoporphyrinogen IX to
71
protoporphyrin IX, and it will end in the formation of singlet and triplet oxygen radicals
72
followed by cell and cell organelles disintegration.10, 11
73
Paraquat is also used to desiccate crops.6 It acts inhibiting photosystem I.
74
Paraquat produces radical oxygen species (ROS), such as hydrogen peroxide (H2O2)
75
and free hydroxyl (OH-).12 ROS rapidly interact with lipids, promoting irreversible lipid
76
peroxidation with subsequent cell organelles, proteins and nucleic acids destruction.13
77
The effects of herbicides in the desiccation of crops are well established but few
78
literature reports deal with the impact of desiccation on grain quality. According to
79
Unver et al.14 plants may exhibit different responses to biotic and abiotic stresses, which
80
severally impacts the plant bioactive compounds’ content. Komives and Schröder15
81
published a review article regarding glyphosate mechanism of action and its effects on
82
secondary metabolites of plants and stated that more studies are necessary to elucidate
83
the synthesis of specialized metabolites as a function of desiccation treatments.
84
Once the desiccation is necessary to improve the mechanical harvesting, we
85
evaluate the effects of the use of glyphosate, glyphosate plus carfentrazone, and
ACS Paragon Plus Environment
Page 5 of 33
Journal of Agricultural and Food Chemistry
86
paraquat as plant desiccators on the technological and chemical properties of cowpea
87
grains. The residual herbicide in the grains was also assessed in the present study.
88 89
2. Materials and Methods
90
2.1. Materials and sample preparation
91
Cowpea from “Bico de ouro” variety was produced in the 2015/2016 growing
92
season in the countryside of Primavera do Leste, State of Mato Grosso, Brazil. Four
93
field plots of 25 hectares each were used. In each 25-hectare plot, three areas of 10 m x
94
20 m were considered as replicates for sample analyses. Seedling and agronomical
95
practices of insects and fungal control were exactly the same in all the four field plots.
96
Moreover, soil fertility was similar between the field plots.
97
Three treatments were tested: 1) treatment A (GLY) consisted of 1824 g a.i. of
98
glyphosate (Glizmax® Prime, Monsanto do Brasil, São Paulo, Brazil) per hectare; 2)
99
treatment B (GLY/CAR) consisted of 1824 g a.i. of glyphosate + 0.032 g a.i. of
100
carfentrazone (Aurora®, FMC Corporation, Philadelphia, USA) per hectare; and 3)
101
treatment C (PAR) consisted of 552 g a.i. of paraquat (Tocha®, HuBei XianLong
102
Chemical Industry Co., China) per hectare. One field crop (25 hectare) was kept without
103
herbicide application before harvesting, being used as control. Figure 1 presents images
104
from the three different field crops taken after 24 h of desiccation and control treatment.
105
GLY, GLY/CAR and PAR were applied 70 days after seeding by using a self-
106
propelled sprayer. GLY, GLY/CAR and PAR were mechanically harvested after 4, 3
107
and 2 days of herbicide treatment, respectively, when plants exhibited total leaf
108
abscission and the grains exhibited around 13% moisture content. Untreated cowpea
109
plants from control treatment were manually harvested after 70 days and placed under
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
110
the ground. Grains were separated from these plants and submitted to drying in the field
111
until 13% moisture content be achieved.
112
Cowpea grains were cleaned, packaged into raffia bags and immediately
113
transported to Laboratório de Pós-Colheita, Industrialização e Qualidade de Grãos
114
(LABGRÃOS) from Universidade Federal de Pelotas (UFPEL), where the storage and
115
analyses were carried out. The evaluations of coat color, cooking time, total phenolics
116
and proanthocyanidins content, and individual phenolics were carried out at the harvest.
117
Coat color and cooking time was also evaluated in cowpea stored after 8 months at 25
118
°C under dark.
119 120
2.2. Coat color and cooking time of cowpea
121
Color attributes of bean samples were determined by using a Minolta
122
colorimeter (CR-410, Konica Minolta, Japan). The colorimetric parameter a* was
123
obtained and used for sample comparison. The a* value expresses red (+) or green (-),
124
being set with a white background plate which was directly obtained from the
125
apparatus.
126
In order to determine the cooking time, grains were soaked for 14 hours in
127
distilled water and then submitted to the cooking procedure at the Mattson Bean Cooker
128
(MBC), as described by Wang and Daun 16. Cooking time was defined as the time, in
129
minutes, that 50% of the cowpea grains were fully cooked, which was easily perceived
130
by plungers dropping.
131
The changes in a* value (∆a*) and cooking time (∆cooking time) of cowpea
132
during 8 months of storage were also determined. Cowpea was stored at 25 ºC in
133
polyethylene bags of 0.16 mm of film thickness and capacity for 1.5 kg of cowpea.
134
Grains were put in a new polyethylene package every 30 days in order to avoid the
ACS Paragon Plus Environment
Page 6 of 33
Page 7 of 33
Journal of Agricultural and Food Chemistry
135
absence of oxygen. ∆a* and ∆cooking time were calculated by subtracting the values
136
obtained at the 8th storage month from those at the beginning of storage.
137 138
2.3. Total phenolics and proanthocyanidins
139
2.3.1. Free phenolics extraction
140
The extraction of free phenolics was performed according to the method
141
described by Qiu, Liu, and Beta,17 with some modifications. The flour from whole
142
grains (2 g) was extracted twice with Acetone/Water solvent (70:30 v/v). For each
143
extraction, the mixture was kept on a mechanical shaker (Certomat Biotech
144
International, Germany) for 1 h at 150 rpm at room temperature. After centrifuging it
145
(5430-R, Eppendorf AG, Germany) at 1430 x g for 5 min, the supernatants obtained
146
from each extraction were combined and concentrated until dryness by using a rotary
147
evaporator at 35 °C. The dried extracts were redissolved in 20 mL of Acetone/Water
148
solvent (70:30 v/v) and used as crude extracts for total quantification of the free
149
phenolics.
150 151
2.3.2. Bound phenolics extraction
152
The bound phenolics extraction was performed according to the optimized
153
method described by Alves et al.18 with minor modifications. The residue obtained after
154
two steps of the extraction of free phenolics using Acetone/Water (70:30 v/v) was
155
washed with distilled water, filtrated, and left to dry in the hood, under dark. Initially,
156
5.0 mL of distilled water was added to the residue from the extraction of free phenolics.
157
Afterwards, the residue was hydrolyzed with 5 µL of α-amylase (50 units/µL) from
158
Bacillus licheniformis (Sigma–Aldrich, United States) at 37 °C during 15 min.
159
Enzymatic reaction was then stopped by heating the material to 90 °C during 5 min. The
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
160
material was subject to alkaline hydrolysis with 40 mL of 4 M NaOH in a shaker for 4
161
h. After digestion, the solution was adjusted to a pH of 1.5–2.0 with 6 M HCl and then
162
extracted three times with 70 mL aliquots of ethyl acetate. The combined ethyl acetate
163
fractions were evaporated until dry and reconstituted in 5 mL of Acetone/Water solvent
164
(70:30 v/v), constituting the bound phenolics extract.
165 166
2.3.3. Phenolics quantification
167
Free and bound phenolics content was determined by using the Folin–Ciocalteu
168
method, with some modifications.19 Briefly, 100 µL of the properly diluted extracts
169
were mixed with 400 µL of distilled water, 0.25 mL of 1 N Folin–Ciocalteu reagent,
170
and then 1.25 mL of 7.5 g/100 mL sodium carbonate were added. After reacting for 120
171
min, the absorbance of the mixture was measured at 725 nm (UV 17000
172
spectrophotometer, Shimadzu, Japan). The quantification was performed using a
173
calibration curve made with gallic acid dissolved in Acetone/Water solvent (70:30 v/v).
174
Results were expressed as mg of gallic acid equivalents (GAE) per 100 g of cowpea on
175
a dry weight basis.
176 177
2.4. Proanthocyanidins
178
The proanthocyanidin content was determined based on the method described by
179
Diaz et al.20 0.5 mL of the extract was pipetted (same extract used for free phenolics
180
quantitation) in glass tubes. Then, 3.0 mL of acidified butanol (butanol:HCl, 950 mL:50
181
mL) and 100 µL of ferric reagent were added. The mixture was boiled (97-100 °C) for
182
30 minutes. The absorbance was measured at 550 nm and the results were expressed in
183
mg of leucocyanidins per 100 g of dry sample.
184
ACS Paragon Plus Environment
Page 8 of 33
Page 9 of 33
Journal of Agricultural and Food Chemistry
185
2.5. LC-ESI-qTOF-MS analysis
186
The same extract used for total phenolics determination was used for LC-ESI-
187
qToF-MS analysis. Samples were filtered through a 0.45 µm nylon membrane filter
188
(Merck Millipore Corporation, Darmstadt, Hesse, Germany). The LC-ESI-qTof-MS
189
analysis was performed on a Prominence UFLC system (Shimadzu, Japan) coupled to a
190
quadrupole time-of-flight mass spectrometer (Impact HD, Bruker Daltonics, Bremen,
191
Germany). Metabolites were separated using a Bidentate C18 column (100 × 2.1 mm,
192
MicroSolv Technology Corp., Leland, NC, USA). Mobile phases were 0.1% aqueous
193
formic acid (pH 2.8; solvent A) and acetonitrile (solvent B). The gradient program was
194
set as follows: started at 5% B, increased linearly to 90% B at 15 min, and maintained
195
for 3 min at 90% B; returned to 5% B in 2 min and maintained at 5% B for an additional
196
6 min at a flow rate of 0.2 mL min−1. The injection volume was 10 µL. All samples
197
were injected in duplicate.
198
Parameters for MS analysis were set using negative ionization mode with spectra
199
acquired over a mass range from m/z 50 to 1200. The parameters were: capillary
200
voltage, +4.0 kV; drying gas temperature, 180 °C; drying gas flow, 8.0 L/min;
201
nebulizing gas pressure, 2 bar; collision RF, 150 Vpp; transfer time 70 µs, and pre-pulse
202
storage, 5 µs. Moreover, automatic MS/MS experiments were performed adjusting the
203
collision energy values as follows: m/z 100, 15 eV; m/z 500, 35 eV; m/z 1000, 50 eV,
204
and using nitrogen as collision gas.
205
The MS data were analyzed using Data Analysis 4.0 software (Bruker Daltonics,
206
Bremen, Germany). Data mining and alignment (m/z, retention time and intensity) of
207
LC-MS/MS records was performed on ProfileAnalysisTM software (version 2.0, Bruker
208
Daltonics, Bermen, Germany) and submit to principal component analysis (item 2.7).
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
209
Tentative metabolite identification of significant peaks on PCA was performed
210
by matching the accurate m/z values and MSn fragmentation patterns with data from
211
databases (METLIN, KEGG compounds, PubChem, Mass bank, Maven, FooDB, and
212
ReSpect) and reference literature with a mass accuracy window of 5 ppm. The identities
213
of citric acid and epicatechin were confirmed with external standards (Sigma-Aldrich).
214 215
2.6. Glyphosate, carfentrazone and paraquat determination
216
Residual glyphosate and paraquat content were determined in accordance to the
217
method described by the European Union Reference Laboratory for Residues of
218
Pesticides.21 Residual carfentrazone content was determined using the AOAC 2007.01
219
method of AOAC International.22 Results were expressed as mg per kilograms of dry
220
weight.
221 222
2.7. Statistical analysis
223
Analytical determinations for the samples were performed in triplicate, and
224
standard deviations were reported. A comparison of the means was ascertained with
225
Tukey’s test to a 5% level of significance using an analysis of the variance (ANOVA).
226
The LC–ESI-qTOF-MS data (aligned peak intensities, mass and retention times)
227
of four treatments was analyzed by principal component analysis (PCA) to identify
228
potential discriminate metabolites. PCA was performed using MetaboAnalyst 3.0.
229 230
3. Results and discussion
231
3.1. Color and cooking time are affected by desiccation
232
Grains harvested from plants treated with PAR exhibited the highest a* value
233
(Fig. 2). It is well-known that PAR treatment generates ROS, which improves the
ACS Paragon Plus Environment
Page 10 of 33
Page 11 of 33
Journal of Agricultural and Food Chemistry
234
activity of polyphenol oxidase (PPO) enzyme in plants.23,24 The activation of PPO may
235
increase quinone production, darkening the seed coat color.25 Cowpea harvested from
236
GLY-treated plants exhibited higher a* value than those from GLY/CAR and control
237
treatments. Although GLY acts inhibiting shikimate pathway being apparently not so
238
stressful to the plants compared to herbicides that directly generate high amount of
239
ROS, GLY may have up-regulated plant phenolics synthesis as well as their
240
polymerization, giving a reddish color to cowpea seed coat. This hypothesis remains to
241
be tested.
242
Interestingly, the highest cooking time of 15.9 minutes was determined for
243
cowpea untreated with desiccants (Fig. 2B). Lignification of the cell wall and
244
polymerization of phenolic constituents mainly from the seed coat have been described
245
as the main phenomena contributing for the increase in the cooking time of stored
246
beans.26 The softening of cowpea during cooking depends on starch gelatinization,
247
which, in turn, depends on the amount and ability of water intake through the cotyledon.
248
The lower cooking time of cowpea subjected to desiccation treatments with GLY,
249
GLY/CAR, and PAR may be a result of the destruction of membranes from organelles
250
and cells, that increased the ability of water intake through cotyledon and heat transfer
251
during cooking. This has likely favored starch gelatinization and cotyledon softening
252
when analyzing freshly harvested cowpea. Another factor that may have contributed for
253
the highest cooking time of untreated cowpea is the longer time that grains from
254
untreated plants (control treatment) took to achieve the optimum moisture content prior
255
threshing.
256 257
3.2. Total phenolics and proanthocyanidins content change as a function of desiccation
258
treatment
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
259
Free and bound phenolics were firstly quantitated by Folin-Ciocalteu method.
260
According to Zhang et al.27 phytochemicals, such as phenolics, mainly exist as
261
glycosides linked to various sugar moieties or as other complexes linked to organic
262
acids, amines, lipids, carbohydrates, and other phenols. Paiva et al.28 stated that
263
phenolic compounds are commonly present in the bound form and are typically
264
components of complex structures, such as lignins and hydrolysable tannins, and linked
265
to the cell wall structural components, such as cellulose, lignin, and proteins through
266
ester bonds. In the present study, free phenolics corresponded to around 88% of total
267
phenolics in cowpea.
268
The highest free and bound phenolics content was determined in grains
269
harvested from GLY-treated plants (Figs. 3A and 3B). GLY treatment have also
270
provided the greatest proanthocyanidins content in cowpea, as presented in Fig. 3C. To
271
our knowledge, GLY treatment up-regulated the activity of enzymes linked to phenolics
272
synthesis as a natural mechanism of specialized metabolites production. GLY is not so
273
abrupt in promoting plant senescence compared to GLY/CAR and PAR, and while the
274
plants took 1- or 2-days more to be ready for mechanical harvesting they continue to
275
produce those specialized metabolites.
276
Proanthocyanidins results (Fig. 3C) followed a similar trend to free and bound
277
phenolics results (Fig. 3A and 3B). Proanthocyanidins are also known as condensed
278
tannins and are considered polymers of flavan-3-ol units, such as catechin and
279
epicatechin, which are described as end-products of flavonoids biosynthesis.29
280
Proanthocyanidins exhibits 15- to 30-times greater antioxidant capacity than phenolic
281
acids.30 The low proanthocyanidins and free and bound phenolics of grains from control
282
treatment suggests that there was little collaboration of phenolics polymerization to the
283
initial cooking time of freshly harvested cowpea, leading to the conclusion that the
ACS Paragon Plus Environment
Page 12 of 33
Page 13 of 33
Journal of Agricultural and Food Chemistry
284
integrity of the cotyledon cells was the main contributor to the cooking time differences
285
observed between grains from control and herbicide-treated plants.
286 287
3.3. Principal component analysis
288
Principal component analysis was applied to verify the influence of herbicide
289
application on secondary metabolism of cowpea. Figure 4A and 4B shows the PCA
290
score and loading plot for components 1 and 2. These components explained 66% of
291
total variance.
292
The identities of metabolites responsible for separations were presented in Table
293
1. Catechin-3-glucoside ([M-H]- m/z 451.1258) and epicatechin ([M-H]- m/z 289.0723)
294
significantly contributed for discrimination of GLY-treated cowpea from the other
295
treatments (Fig. 4B, Table 1). Extracted ion chromatograms of catechin-3-glucoside and
296
epicatechin are presented in Fig. 5A. Both catechin and epicatechin are described as
297
end-route compounds from the flavonoid biosynthesis pathway, being found as
298
monomers, dimmers, trimmers, tetramers, as well as in more complex polymeric forms.
299
According to Zabalza et al.31, glyphosate treatment induces a non-regulated carbon
300
entrance through 3-deoxy-D-arabino-heptulosonate-7-phosphate synthase (DAHPS),
301
which is the first enzyme of the shikimate pathway, and accumulation of metabolites
302
upstream EPSPS. In sum, the findings from Zabalza et al.31 clarified that phenylalanine
303
ammonia-lyase (PAL) activity is up-regulated due to glyphosate treatment,
304
accompanied by the synthesis of flavonoid precursor and flavonoids.
305
Citric acid ([M-H]- m/z 191.0205) was responsible for discrimination of
306
GLY/CAR-treated cowpea (Fig. 5B). A previous work conducted by Wells and
307
Appleby32 provided evidence that another protox inhibitor molecule called “Lactofen”
308
associated to glyphosate potentiated the glyphosate transport throw the symplast, as
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
309
well as glyphosate penetration in plant cells. Thus, it is hypothesized that similar
310
behavior occurred in the present work, with carfentrazone favoring glyphosate
311
assessment in the grain cells, which, in turn, favored citric acid accumulation. Zhu et
312
al.33 observed an increase in the expression of five cDNAs codifying for enolases, when
313
soybean susceptible to glyphosate was treated with glyphosate. Enolase is the ninth
314
enzyme from the glycolysis pathway, acting in the conversion of 2-phosphoglycolate to
315
phosphoenolpyruvate. The authors concluded that greater amounts of intermediates of
316
the tricarboxylic acid cycle are accumulated in such situation. The statements of Zhu et
317
al.33 support our findings.
318
Quercetin derivative ([M-H]- m/z 625.1426) and gluconic acid ([M-H]- m/z
319
195.0515) were responsible for discrimination of control treatment (Figs. 5C and 5D;
320
Table 1). According to the studies performed by Ojwang et al.34, quercetin is the main
321
flavonol found in white, black, red, and brown cowpea. De Abreu et al.35 reported that
322
quercetin is a potential antioxidant of ROS. Although levels of ROS have not been
323
determined in the present study, the applied desiccants are known to increase ROS
324
levels. Thus, it is assumed that greater quercetin derivatives content was determined in
325
samples from control treatment because less ROS were formed at the absence of
326
desiccant treatment. Baxter et al.36 reported increases in gluconic acid content in
327
Arabidopsis cells when subjected to oxidative stress, justifying this behavior by the re-
328
routing of glycolytic carbon flow to the oxidative pentose phosphate pathway. The
329
authors also reported a decrease in the activity of the enzymes related to tricarboxylic
330
acid cycle. This fact supports the low citric acid content as well as the higher gluconic
331
acid content determined in samples from control treatment.
332
Intermediate gluconic acid level was determined in PAR treatment (Fig. 5C),
333
that may be a result of the re-routing of carbon flow to the oxidative pentose phosphate
ACS Paragon Plus Environment
Page 14 of 33
Page 15 of 33
Journal of Agricultural and Food Chemistry
334
pathway associated with ROS generation and an abrupt plant desiccation. In this case,
335
gluconic acid accumulation was stimulated but for a fewer time than control treatment.
336 337
3.4. Residual glyphosate, carfentrazone and paraquat content
338
Flour from uncooked GLY-, GLY/CAR- and PAR-treated cowpea was prepared
339
from grains stored during 30 months at 15 °C. Residual glyphosate content of 13 and 14
340
mg per kilogram of dry weight were determined in GLY- and GLY/CAR-treated
341
cowpea, respectively. Carfentrazone was below the limit of quantification of 0.01 mg
342
per kilogram of dry weight in cowpea from GLY/CAR-treated cowpea. Glyphosate
343
values from both treatments are higher than the maximum limit of 2 and 0.1 mg per
344
kilogram stablished by Codex Alimentarius37 and European Union38. Paraquat content
345
was 0.84 mg per kilogram of dry weight in PAR-treated cowpea. Paraquat value
346
determined in the present study is higher than the maximum limits of 0.5 and 0.02 mg
347
per kilogram of grains allowed by Codex Alimentarius37 and European Union38,
348
respectively. Effects of glyphosate exposure on human’s health have been studied for
349
years, being a controversial issue in research. Scientific evidences suggest that
350
incidence of Parkinson’s disease is associated to exposure to toxicants such as
351
paraquat.39,40
352 353
3.5. Susceptibility to changes in coat color and cooking time during storage
354
Once cowpea is subjected to desiccation, different metabolic responses occur
355
depending on the herbicide used, as seen previously in sections 3.1, 3.2, and 3.3. One
356
problem that arises is the susceptibility of the grains obtained from the different
357
desiccation treatments to the postharvest color and cooking time changes. Thus, cowpea
358
from the GLY, GLY/CAR, PAR and control treatments were stored at 25 °C during 8
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
359
months, in order to evaluate differences in coat color (∆a*) and cooking time (∆cooking
360
time). Results are presented in Figs. 6 and 7.
361
From this issue, we observed that grains from control treatment exhibited an
362
increase in coat color and cooking time during storage (Figs. 6 and 7), which are
363
phenomena involved in the appearance of hard to cook defect in stored beans.25 GLY
364
and GLY/CAR treatment increased coat color to a similar level than control treatment.
365
Interestingly, PAR treatment provided the lowest ∆a*, which may be a reflect of a
366
lower grain metabolism. Cowpea from PAR treatment exhibited just 58% of
367
germination while cowpea from other treatments exhibited between 86 and 94% of
368
germination (data not shown). In Fig. 7, some extremely darken cowpea are perceived
369
mixed to the samples at the eighth month of storage, mainly in PAR and control
370
treatments. This may be a result of the variations in metabolic responses of the grains as
371
a function of maturity; when the desiccant is applied, some grains are fully mature while
372
others are still green. This issue needs to be addressed in future studies.
373
The GLY and PAR treatments provided the lowest ∆cooking time (Fig. 6B). The
374
lower grain metabolism supported by the germination levels in PAR-treated cowpea has
375
probably maintained the cotyledon cells with a mild lignification degree. Interestingly,
376
GLY-treated cowpea was the less susceptible to increases in cooking time during 8
377
months of storage at 25 °C. This fact supports that GLY treatment impacts mainly the
378
metabolism of grain coat flavonoids than in lignification process of cell walls from
379
cowpea cotyledon.
380
To the best of our knowledge, this is the first time that the effects of the most
381
common desiccants used in Brazil on the quality of cowpea from “Bico de Ouro”
382
variety were determined. All studied desiccants provided lower cooking time compared
383
to freshly harvested cowpea. However, the coat color of PAR- and GLY/PAR-treated
ACS Paragon Plus Environment
Page 16 of 33
Page 17 of 33
Journal of Agricultural and Food Chemistry
384
cowpea was reddish than control treatment. This is not desired by farmers, traders,
385
industry nor consumers. During storage, GLY- and PAR-treated cowpea exhibited
386
better resistance to changes in coat color and cooking time than control and GLY/CAR
387
treatments. It is better because cowpea without reddish color is marketed at higher
388
values. Any possibility of improvements in the technological and chemical properties of
389
cowpea may be off-set by the risks of those desiccants exhibit when exceeding the
390
maximum limits of tolerance in food. This is why Federal inspection may be urgently
391
intensified.
392
Transcriptome, proteome and metabolome studies may help to deeply
393
understand the metabolic responses of cowpea to the different commercial desiccants.
394
Moreover, studies dealing with other types of herbicides, desiccant doses, period of
395
desiccant application and conditions will help farmers and bean industries to find
396
alternatives for a safe cowpea harvesting in large areas.
397 398
Abbreviations used
399
cDNA – complementary deoxyribonucleic acid
400
EPSPS - 5-enolpiruvil-shikimato-3-fosfato synthase
401
ESI – Electrospray ionization source
402
GLY – Glyphosate
403
GLY/CAR – Glyphosate plus carfentrazone
404
LC-MS – liquid chromatography-mass spectrometry
405
PAR – Paraquat
406
PPO – Polyphenol oxidase
407
PROTOX - protoporphyrinogen oxidase
408
qTOF – quadrupole-time of flight mass analyzer
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
409
ROS – Reactive oxygen species
410 411
Acknowledgments
412
We would like to thank Dr. Galileu Rupollo for the technical and financial support for
413
this research, as well as Conselho Nacional de Desenvolvimento Científico e
414
Tecnológico, Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES),
415
Fundacão de Amparo à Pesquisa do Estado do Rio Grande do Sul (FAPERGS),
416
Secretaria do Desenvolvimento Econômico, Ciência e Tecnologia do Estado do Rio
417
Grande do Sul (SDECT-RS), and Polo de Inovação Tecnológica em Alimentos da
418
Região Sul (Polo de Alimentos).
419 420
References
421
1. Devi, C. B.; Kushwaha, A.; Kumar, A. Sprouting characteristics and associated
422
changes in nutritional composition of cowpea (Vigna unguiculata). Food Sci. Technol.
423
2015, 52, 6821–6827.
424
2. Awika, J. M.; Duodu, K. G. Bioactive polyphenols and peptides in cowpea (Vigna
425
unguiculata) and their health promoting properties: A review. J. Fun. Food. 2016, In
426
Press. doi: 10.1016/j.jff.2016.12.002
427
3. FAO. Food & Agriculture Organization of the United Nations. Statistical database.
428
2017. http://faostat.fao.org. Accessed 25 April 2017.
429
4. Filho, F. R. F.; Ribeiro, V. Q.; Rocha, M. R.; Silva, K. E.; Nogueira, M. R.;
430
Rodrigues, E. V. Feijão-Caupi no Brasil: Produção, melhoramento genético, avanços e
431
desafios, edition 1.; Filho, F. R.F., Eds., Publisher: Teresina, Brazil – BR, 2011; 84 pp.
432
5. Iqbal, J.; Ahsan, M.; Saleem, M.; Ali, A. Appraisal of gene action for indeterminate
433
growth in mungbean (Vigna radiata L. Wilczek). Int. J. Plant Sci. 2015, 6, 1-8.
ACS Paragon Plus Environment
Page 18 of 33
Page 19 of 33
Journal of Agricultural and Food Chemistry
434
6. Soltani, N.; Blackshaw, R. E.; Gulden, R. H.; Gillard, C. L.; Shropshire, C.; Sikkema,
435
P. H. Desiccation in dry edible beans with various herbicides. Can. J. Plant. Sci. 2013,
436
93, 871–877.
437
7. Kielak, E.; Sempruch, C.; Mioduszewska, H.; Klocek, J.; Leszczyński, B.
438
Phytotoxicity of Roundup Ultra 360 SL in aquatic ecosystems: Biochemical evaluation
439
with duckweed (Lemna minor L.) as a model plant. Pestic. Biochem. Phys. 2011, 99,
440
237–243.
441
8. Reddy, K. N.; Duke, S. O. Soybean Mineral Composition and Glyphosate Use. In
442
Processing and Impact on Active Components in Food, edition 1.; Preedy, V., Eds.;
443
Publisher: San Diego, United States – USA, 2014, 369-376.
444
9. Gomes, M. P.; Le Manac’h, S. G.; Maccario, S.; Labrecque, M.; Lucotte, M.; Juneau,
445
P. Differential effects of glyphosate and aminomethylphosphonic acid (AMPA) on
446
photosynthesis and chlorophyll metabolism in willow plants. Pestic. Biochem. Phys.
447
2016, 130, 65–70
448
10. Reade, J. P. H.; Cobb, A. H. Herbicides Modes of Action and Metabolism. In Weed
449
Management Handbook, edition 9.; Robert, L., Eds.; Publisher: Cornwall, Great Britain
450
– GBR, 2002; 134-170.
451
11. Zhang, L.; Wan, J.; Yang, G. A DFT-based QSARs study of protoporphyrinogen
452
oxidase inhibitors: Phenyl triazolinones. Bioorgan. Med. Chem. 2004, 12, 6183–6191.
453
12. Fuerst E.P.; Vaughn K.C. Mechanisms of paraquat resistance. Weed Technol. 1990,
454
4, 150–156.
455
13. Aksakal, O. Assessment of paraquat genotoxicity on barley (Hordeum vulgare L.)
456
seedlings using molecular and biochemical parameters. Acta. Physiol. Plant. 2013, 35,
457
2281–2287.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
458
14. Unver, T.; Bakar, M.; Shearman, R. C.; Budak, H. Genome-wide profiling and
459
analysis of Festuca arundinacea miRNAs and transcriptomes in response to foliar
460
glyphosate application. Mol. Genet. Genomics. 2010, 283, 397–413.
461
15. Komives, T.; Schröder, P. On glyphosate. Sci. J. Eur. Eco. Society. 2016, 2, 1–8.
462
16. Wang, N.; Daun, J. K. Determination of cooking times of pulses using an automated
463
Mattson cooker apparatus. J. Agr. Food. Chem. 2005, 85, 1631-1635.
464
17. Qiu, Y.; Liu, Q.; Beta, T. Antioxidant properties of commercial wild rice and
465
analysis of soluble and insoluble phenolic acids. J. Agr. Food. Chem. 2010, 121, 140–
466
147.
467
18. Alves, G. H.; Ferreira, C. D.; Vivian, P. G.; Monks, J. L. F.; Elias, M. C., Vanier, N.
468
L.; De Oliveira, M. The revisited levels of free and bound phenolics in rice: Effects of
469
the extraction procedure. Food Chem. 2016, 208, 116–123.
470
19. Singleton, V. L.; Rossi, J. A. Jr. Colorimetry of total phenolics with
471
phosphomolybdic-phosphotungstic acid reagents. Am. J. Enol. Viticult. 1965, 16, 144–
472
158.
473
20. Díaz, A. M.; Caldas, G. V.; Blair, M. W. Concentrations of condensed tannins and
474
anthocyanins in common bean seed coats. Food Res. Int. 2010, 43, 595–601.
475
21. Anastassiades, M.; Kolberg, D. I.; Mack, D., Sigalova, I.; Roux, D.; Fügel, D. Quick
476
method for the analysis of residues of numerous highly polar pesticides in foods of plant
477
origin involving simultaneous extraction with methanol and LC-MS/MS determination.
478
2013, Version 4.
479
22. Official Methods of Analysis, AOAC Official Method 2007.01. Pesticide residues in
480
foods by acetonitrile extraction and partitioning with magnesium sulfate, AOAC
481
International, 2007.
ACS Paragon Plus Environment
Page 20 of 33
Page 21 of 33
Journal of Agricultural and Food Chemistry
482
23. Fujii, T.; Yokoyama, E.; Inoue, K.; Sakurai, H. The sites of electron donation of
483
Photosystem I to methyl viologen. Biochim. Biophys. Acta. 1990, 1015, 41–48.
484
24. Pinto, M. S. T.; Siqueira, F. P.; Oliveira, A. E. A.; Fernandes, K. V. S. A wounding-
485
induced PPO from cowpea (Vigna unguiculata) seedlings. Phytochemistry. 2008, 69,
486
2297–2302.
487
25. Marles, M. A. S.; Vandenberg, A.; Bett, K. E. Polyphenol oxidase activity and
488
differential accumulation of polyphenolics in seed coats of pinto bean (Phaseolus
489
vulgaris L.) characterize postharvest color changes. J. Agr. Food. Chem. 2008, 56,
490
7049–7056.
491
26. Nasar-Abbas, S. M.; Plummer, J. A.; Siddique, K. H. M.; White, P.; Harris, D.;
492
Dods, K. Cooking quality of faba bean after storage at high temperature and the role of
493
lignins and other phenolics in bean hardening. LWT-Food. Sci. Technol. 2008, 41,
494
1260–1267.
495
27. Zhang, M. W.; Zhang, R. F.; Zhang, F. X.; Liu, R. H. Phenolic profiles and
496
antioxidant activity of black rice bran of different commercially available varieties. J.
497
Agr. Food. Chem. 2010, 58, 7580–7587.
498
28. Paiva, F. F.; Vanier, N. L.; Berrios, J. D. J.; Pan, J.; Villanova, F. A.; Takeoka, G.;
499
Elias, M. C.; Vanier, N. L. Physicochemical and nutritional properties of pigmented rice
500
subjected to different degrees of milling. J. Food Compos. Anal. 2014, 35, 10–17.
501
29. Zuiter, A. S. Proanthocyanidin: Chemistry and Biology: From Phenolic Compounds
502
to Proanthocyanidins. In Chemistry, Molecular Sciences and Chemical Engineering,;
503
Reedijk, J., Eds.; Publisher: Waltham, United States – USA, 2014; 1-29.
504
30. Ávila, M. B.; De Lúcio, J. A. G.; Mendoza, N. V.; González, C. V.; Arciniega, M.
505
D. L.; Vargas, G. A. Geranium Species as Antioxidants. In.: Oxidative Stress and
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
506
Chronic Degenerative Diseases - A Role for Antioxidants. (J. A. Morales-González,
507
Ed.). Intech: Rijeka, Croatia. 2013, 87–112.
508
31. Zabalza, A.; Orcaray, L.; Fernández-Escalada, M.; Zulet-González, A.; Royuela, M.
509
The pattern of shikimate pathway and phenylpropanoids after inhibition by glyphosate
510
or quinate feeding in pea roots. Pestic. Biochem. phys. 2016, In Press.
511
32. Wells, B. H.; A. P. Appleby. Lactofen Increases Glyphosate-Stimulated Shikimate
512
Production in Little Mallow (Malva parviflora). Weed Sci.1992, 40, 171–173.
513
33. Zhu, J.; Patzoldt, W.; Shealy, R.; Vodkin, L.; Clough, S.; Tranel, P. Transcriptome
514
Response to Glyphosate in Sensitive and Resistant Soybean. J. Agr. Food. Chem. 2008,
515
56, 6355–6363.
516
34. Ojwang, L. O.; Dykes, L.; Awika, J. M. Ultra performance liquid chromatography-
517
tandem quadrupole mass spectrometry profiling of anthocyanins and flavonols in
518
cowpea (Vigna unguiculata) of varying genotypes. J. Agr. Food. Chem. 2012, 60,
519
3735–3744.
520
35. De Abreu, I. N.; Mazzafera, P. Effect of water and temperature stress on the content
521
of active constituents of Hypericum brasiliense Choisy. Plant. Physiol Biochem. 2005,
522
43, 241–248.
523
36. Baxter, C. J.; Redestig, H.; Schauer, N.; Repsilber, D.; Patil, K. R.; Nielsen, J.;
524
Sweetlove, L. J. The metabolic response of heterotrophic Arabidopsis cells to oxidative
525
stress. Plant. Physiol. 2007,143, 312–325.
526
37. FAO/WHO. Codex Alimentarius Comission: Procedure Manual, 39th session. Ed.
527
Rome, Italy. 2016.
528
Goldman, S. M. Environmental toxins and Parkinson's disease. Annu. Rev. Pharmacol.
529
Toxicol. 2014, 54, 141–164.
ACS Paragon Plus Environment
Page 22 of 33
Page 23 of 33
Journal of Agricultural and Food Chemistry
530
38. European Commission. Commission Regulation, (EU) No. 520/2011, amending
531
Annexes II and III to Regulation (EC) No 396/2005 of the European Parliament and of
532
the Council as regards maximum residue levels for benalaxyl, boscalid, buprofezin,
533
carbofuran,
534
metaflumizone, methoxyfenozide, paraquat, prochloraz, spirodiclofen, prothioconazole
535
and zoxamide in or on certain products, 2011.
536
39. Goldman, S. M. Environmental toxins and Parkinson's disease. Annu. Rev.
537
Pharmacol. Toxicol. 2014, 54, 141–164.
538
40. Hou, L.; Zhang, C.; Wang, K.; Liu, X.; Wang, H.; Che, Y.; Sun, F.; Zhou, X.; Zhao,
539
X.; Wang, Q. Paraquat and maneb co-exposure induces noradrenergic locus coeruleus
540
neurodegeneration
541
Toxicology. 2017, 380, 1–10.
carbosulfan,
cypermethrin,
through
NADPH
fluopicolide,
hexythiazox,
oxidase-mediated
microglial
indoxacarb,
activation.
542 543
Figure captions
544
Figure 1. Images taken after 24 hours of plant desiccation with glyphosate (A),
545
glyphosate plus carfentrazone (B) and paraquat (C), and after 24 hours of manual
546
harvesting in case of control treatment (D).
547
Figure 2. a* value (A) and cooking time (B) of cowpea harvested from plants
548
desiccated with different herbicides.
549
Figure 3. Free phenolics (A), bound phenolics (B) and proanthocyanidins (C) content
550
of cowpea grains obtained from plants desiccated with different herbicides.
551
Figure 4. Principal component analysis of score plot (A) and loading ions (B) derived
552
from LC-MS data using negative electrospray ionization of cowpea extracts.
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
553
Figure 5. Extracted ion chromatogram of catechin-3-glucoside and epicatechin (A),
554
citric acid (B), gluconic acid (C), and quercetin glucoside derivative (D) from cowpea
555
grains harvested from plants desiccated with different herbicides.
556
Figure 6. ∆a* (A) and ∆cooking time (B) of cowpea stored during 8 months at 25 °C as
557
a function of the plant desiccant applied prior harvesting.
558
Figure 7. Visual appearance of cowpea grains at the beginning and at the 4th and 8th
559
months of storage at 25 °C under dark.
560 561
Table captions
562
Table 1. Mainly compounds differentiating cowpea grains treated with different
563
herbicides derived from LC-MS data using negative electrospray ionization.
564
ACS Paragon Plus Environment
Page 24 of 33
Page 25 of 33
565 566
Journal of Agricultural and Food Chemistry
Table 1. Mainly compounds differentiating cowpea grains treated with different herbicides derived from LC-MS data using negative electrospray ionization Retention time (min)
Experimental m/z
Theoretical m/z
Error (ppm)
mSigma
Fragmentation m/z
Identification
6.86
289.0723
289.0718
-0.60
45
-
Epicatechin
Quantification (mg . 100g-1) GLY 0.92±0.0
GLY/CAR 0.66±0.0
PAR 0.89±0.1
CONTROL 1.12±0.1
1
567 568
1.69
195.0515
195.0510
-0.4
8.8
129.0216 75.0088
Gluconic acid2
2.65±0.0
2.78±0.0
3.12±0.0
3.77±0.0
9.52
625.1426
625.1410
-2.5
46.2
300.0266
1.69±0.0
1.62±0.0
1.65±0.0
1.87±0.0
1.98
191.0205
191.0197
-4.0
15.6
111.0088 85.0299
Quercetin glucoside derivative2 Citric acid1
33.79±0.1
34.22±0.0
30.95±0.1
30.19±0.2
5.72
451.1258
451.1246
-2.7
59.8
289.0722 Catechin-3- 1.95±0.0 1.58±0.0 1.64±0.0 1.65±0.0 245.0821 glucoside2 137.0239 1 Confirmed by comparison to the external standard compound; 2 Confirmed by MS/MS; mSigma = fit between measured and theoretical isotopic pattern. The smaller the mSigma value the better the isotopic fit.
569
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
570
Fig. 1
571
ACS Paragon Plus Environment
Page 26 of 33
Page 27 of 33
Journal of Agricultural and Food Chemistry
Fig. 2
7
A a
6 b
a* Value
5
c
c
4 3 2 1 0 GLY
GLY/CAR
PAR
CONTROL
18
a
B 16 14 Cooking time (min)
572
b b
b
GLY
GLY/CAR
12 10 8 6 4 2 0 PAR
CONTROL
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
573
Fig. 3
1600
A -1
Free phenolics content (mg.100 g )
1400
a
1200
b
bc
GLY/CAR
PAR
CONTROL
b
b
b
GLY/CAR
PAR
CONTROL
b
b
c
1000 800 600 400 200 0 GLY
-1
Bound phenolics content (mg.100 g )
200 180
B
a
160 140 120 100 80 60 40 20 0 GLY
C
-1
Proanthocyanidins content (mg.100 g )
400
a 300
c 200
100
Free
0
GLY
GLY/CAR
PAR
CONTROL
574
ACS Paragon Plus Environment
Page 28 of 33
Page 29 of 33
Journal of Agricultural and Food Chemistry
575
Fig. 4
576
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
577
Fig. 5
578
ACS Paragon Plus Environment
Page 30 of 33
Page 31 of 33
Journal of Agricultural and Food Chemistry
579
Fig. 6
10
A
a
a
∆Cooking time (min)
8
b 6
c 4
2
0 GLY
GLY/CAR
PAR
CONTROL
10
B a
8
ab ∆a* Value
b 6
c 4
2
0 GLY
GLY/CAR
PAR
CONTROL
580
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
581
Fig. 7
582
ACS Paragon Plus Environment
Page 32 of 33
Page 33 of 33
Journal of Agricultural and Food Chemistry
583
TOC Graphic
584
ACS Paragon Plus Environment