Subscriber access provided by UNIVERSITY OF TOLEDO LIBRARIES
Agricultural and Environmental Chemistry
Flower-like Mg(OH)2 Cross Nano-sheets for Controlling Cry1Ac Protein Loss: Evaluates Its Insecticidal activity and Biosecurity Wenhua Rao, Yating Zhan, Saili Chen, Zhangyan Xu, Tengzhou Huang, Xianxian Hong, Yilin Zheng, Xiaohong Pan, and Xiong Guan J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b00575 • Publication Date (Web): 27 Mar 2018 Downloaded from http://pubs.acs.org on March 30, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 34
Journal of Agricultural and Food Chemistry
1
Flower-like Mg(OH)2 Cross Nano-Sheets for Controlling
2
Cry1Ac Protein Loss: Evaluates Its Insecticidal Activity
3
and Biosecurity
4
Wenhua Rao,† Yating Zhan,† Saili Chen,† Zhangyan Xu,† Tengzhou Huang,†
5
Xianxian Hong,† Yilin Zheng,† Xiaohong Pan,*,† and Xiong Guan*,†
6
†
7
of Plant Protection & Key Lab of Biopesticide and Chemical Biology, Ministry of
8
Education, Fujian Agriculture and Forestry University, Fuzhou, Fujian 350002, People’s
9
Republic of China
State Key Laboratory of Ecological Pest Control for Fujian and Taiwan Crops, College
10
Corresponding Authors
11
*Tel. & Fax: +086-591-83789258. E-mail:
[email protected] (Xiaohong Pan).
12
*Tel. & Fax: +086-591-83789258. E-mail:
[email protected] (Xiong Guan).
13 14 15 16 17 18 19
1 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
20
ABSTRACT: Bacillus thuringiensis (Bt) can produce Cry proteins during the sporulation
21
phase, and Cry protein is effective against lepidopteran, coleopteran, dipteran insects and
22
nematodes. However, Cry protein tends to be discharged into soil and non-target plants
23
through rainwater runoff, leading to reduced effective period toward target insects. In the
24
present study, nano-Mg(OH)2 (MHNPs) were synthesized to control the loss of Cry1Ac
25
protein and deliver protein to Helicoverpa armigera (Lepidoptera: Noctuidae). The
26
results showed that Cry1Ac protein could be loaded onto MHNPs through electrostatic
27
adsorption, and both MHNPs and Cry protein were stable during the adsorption process.
28
Meanwhile, the Cry1Ac-loaded MHNPs (designated as Cry1Ac-MHNPs) could retain on
29
the surface of cotton leaves, resulting in enhanced adhesion amount of Cry1Ac protein by
30
59.50% and increased pest mortality by 75.00%. Additionally, MHNPs could be slowly
31
decomposed by acid medium and MHNPs showed no obvious influence on the cotton, Bt,
32
Escherichia coli and H. armigera. Therefore, MHNPs could serve as an efficient
33
nanocarrier for delivery of Cry1Ac protein and be used as a potential adjuvant for
34
biopesticide in agricultural applications.
35
KEYWORDS: Bacillus thuringiensis, Cry1Ac protein, nano-Mg(OH)2, Helicoverpa
36
armigera, loss control, insecticidal activity, biosafety
37 38 39
2 ACS Paragon Plus Environment
Page 2 of 34
Page 3 of 34
Journal of Agricultural and Food Chemistry
40
1. INTRODUCTION
41
Pesticides have been extensively applied in agricultural production. However, about 90%
42
pesticide goes to soil through rainwater runoff, resulting in reduced effective period to
43
target insects and adverse effects on non-target organism.1,2 As one type of biopesticides,
44
Bacillus thuringiensis (Bt) is widely used for biological control of pest worldwide, it
45
produces Cry protein during the sporulation phase,3,4 and Cry protein is effective against
46
lepidopteran, coleopteran, dipteran insects and nematodes.5-7 Similar to the chemical
47
pesticides, Cry protein may be lost because of rainwater and other environmental factors,
48
leading to reduced efficacy and economy loss. Therefore, controlling of biopesticide loss
49
would be a promising countermeasure to ensure adequate effect.
50
Nanomaterials can enhance stability of drug and promote drug utilization rate as well
51
as control pesticide loss since they possess high surface area, strong adsorption capacity
52
and electrical properties.8-13 Additionally, Cry protein can be easily loaded onto
53
nanomaterials, and the bioactivity of Cry protein is not affected by the nanomaterials.14-19
54
However, some nanomaterials are expensive and even show potential risks to human
55
health and ecosystem, resulting in restricted practical application of nanomaterials in
56
agriculture.20-22 Therefore, selection of suitable materials would be a key process to
57
prevent loss of biopesticides.
58
As a low cost material, nano-Mg(OH)2 (MHNPs) have already been widely applied as
59
a green adsorbent and antibacterial agent.23-25 However, only few studies have used
3 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
60
MHNPs to prevent loss of biopesticides. Additionally, the safety of nanoproducts in
61
agriculture and the potential of adverse ecosystem responses from nanoparticles are not
62
clearly understood. Therefore, in the present study, we aimed to (i) assess the adsorption
63
process between Cry1Ac protein and MHNPs as well as the stability of MHNPs, (ii)
64
evaluate the retention ability of Cry1Ac-MHNP complex on the surface of cotton leaf and
65
the bioactivity of Cry1Ac-MHNPs to Helicoverpa armigera (H. armigera), and (iii)
66
investigate the biosafety of MHNPs to cotton, Bt, E. coli and H. armigera. Our results
67
provided a promising method to control the loss of biopesticides in agricultural
68
applications.
69
2. MATERIALS AND METHODS
70
2.1. Materials. Light magnesium oxide with a purity of 99% was provided by
71
Sinopharm Chemical Reagent Company (Shanghai, China). Pageruler pre-stained protein
72
ladder was purchased from Thermo Scientific Company (USA). MES was obtained from
73
Shanghai Macklin Biochemical Company (Shanghai, China). Tryptone and yeast extract
74
were supplied from Oxid Company (England). Cotton (Ji228) was provided by Hebei
75
Jinfa Seed Company (Hebei, China). Other chemicals were of analytical grade and
76
purchased from Sinopharm Chemical Reagent Company (Shanghai, China).
77
2.2. Insect Culture. The H. armigera larvae were reared in an environmentally
78
controlled laboratory (T = 27 ± 1 °C, RH = 60 ± 5%, L:D = 16:8) at Fujian Agriculture
79
and Forestry University, China.
4 ACS Paragon Plus Environment
Page 4 of 34
Page 5 of 34
Journal of Agricultural and Food Chemistry
80
2.3. Preparation of Cry1Ac Protein. Bt (HD-73) was preserved in the Key
81
Laboratory of Biopesticide and Chemical Biology, Fujian Agriculture and Forestry
82
University, China. The preparation of Cry1Ac protein was conducted according to a
83
previously described method26 with minor modifications. Briefly, Bt was inoculated on
84
solid half strength Luria-Bertani (LB) medium and cultured at 30 °C for 48 h. After
85
washing with 1 M sodium chloride (NaCl) and double distilled water (ddH2O) twice, the
86
crystals and spores were resuspended in solubilization buffer (50 mM Na2CO3, 50 mM
87
EDTA, 5% β-mercaptoethanol, pH 9.5) for at least 4 h, and centrifuged at 16737 g for 20
88
min at 4 °C. The supernatant was then harvested, and the pH was adjusted with 4 M
89
HAc-NaAc (pH 4.5) to 4.5. The supernatant was kept on ice for 1 h, and the proteins
90
were collected by centrifugation at 16737 g for 20 min at 1 °C. The obtained proteins
91
were dissolved in 50 mM Na2CO3 (pH 9.5) and stored at -80 °C prior to further test.
92
2.4. Synthesis of MHNPs. MHNPs were synthesized according to the previous
93
studies with minor modifications.23,27,28 Briefly, 3.5 g light magnesium oxide was slowly
94
added to ddH2O with continuous stirring in a water bath at 80 °C for 1 h. The mixture
95
was centrifuged at 12298 g in Eppendorf centrifuge for 5 min and washed with ddH2O
96
twice for further characterization.
97
2.5. Loading of Cry1Ac Protein onto MHNPs. To investigate optimal loading of
98
Cry1Ac protein to MHNPs, 1 mL Cry1Ac protein (1.52 mg/mL) in 50 mM Na2CO3 was
99
loaded onto MHNPs [Cry1Ac-MHNPs (w:w)] at various ratios (1:3.28, 1:6.56, 1:9.84,
5 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
100
1:13.12 and 1:19.68), and then the mixture was incubated in 2-mL centrifuge tube at
101
room temperature with a agitation in Standard rotary mixing instrument (Scilogex Co.,
102
USA) for 50 min [50 min was enough for adsorption according to the adsorption kinetic
103
analysis (Figure S2)]. The suspension was collected and centrifuged at 16737 g for 10
104
min at 4 °C. The adsorption rate was determined based on the protein concentration in the
105
supernatant using bovine serum albumin (BSA) as standard protein (Bradford assay).29
106
Additionally, to assess the stability of Cry1Ac protein during the loading process, the
107
residual Cry1Ac protein in the supernatant was analyzed by SDS-PAGE.
108
2.6. Characterization. The Braumer-Emmet-Teller (BET) surface area of MHNPs
109
was determined with a Micromeritics’ ASAP 2000 (Micromeritics Co., USA). Cry1Ac
110
protein, MHNPs and Cry1Ac-MHNPs were dried at ultra-low temperature in vacuum
111
desiccator (Beijing Songyuanhuaxing Technology Develop Co., China). Zeta potential
112
and size distribution were determined by Malvern’s Zetasizer Nano ZS90 (Malvern Co.,
113
England).28 MHNPs and Cry1Ac-MHNPs were characterized on a JSM-6700F scanning
114
electron microscope (SEM) (JEOL Co., Japan) equipped with an Oxford-INCA
115
energy-dispersive X-ray spectroscopy (EDS). The crystal structure and interaction
116
analyses of MHNPs and Cry1Ac-MHNPs were performed on Tecnai G2 F20 S-TWIN
117
(200 kV) (TEM) (FEI Co., USA) and PANalytical X’ Pert PRO diffractometer (XRD)
118
(PANalytical Co., Netherlands). The thermal gravimetric analysis (TGA) of MHNPs was
119
recorded by the simultaneous thermal analyzer STA449C (Netzsch Co., Germany) in
6 ACS Paragon Plus Environment
Page 6 of 34
Page 7 of 34
Journal of Agricultural and Food Chemistry
120
argon atmosphere within the temperature range of 25−800 °C and a heating rate of
121
10 °C/min. FT-IR measurement was conducted within the range of 500–4000 cm−1 using
122
Nicolet IS10 (Thermo Scientific Co., USA).
123
2.7. Investigation of Adhesion Performance of Cry1Ac-MHNPs on Cotton
124
Leaf. Briefly, 1 mL Cry1Ac protein (1.98 mg/mL) and 0.03 g MHNPs were mixed by
125
Standard rotary mixing instrument for 50 min at room temperature [Cry1Ac-MHNPs
126
(w:w) at 1:15.15, this ratio was between 1:19.68 and 1:13.12, thus the spraying
127
Cry1Ac-MHNP complex might release small amount of Cry1Ac protein immediately for
128
pest control]. Cotton leaves were divided into two groups with same leaf size and stage.
129
Cotton leaves in the first group were placed on the petri dish with 30° on the ground at
130
room temperature, and the mixture (Cry1Ac-MHNPs) was evenly sprayed onto the leaf
131
surface. After air-drying, 3 mL ddH2O was evenly sprayed onto the leaf surface to
132
simulate the rainwater. Subsequently, the leaves were air-dried and immersed into 3 mL
133
50 mM dissolved medium (Na2CO3, pH 9.5) and shaken at room temperature for 10 min.
134
The pH of suspensions was adjust to 4.5 with 4 M HAc-NaAc (pH 4.5), and the
135
suspensions were kept on ice for 1 h and then centrifuged at 16737 g for 20 min at 4 °C.
136
MHNPs could be resolved by 4 M HAc-NaAc medium (pH 4.5), and the Cry1Ac protein
137
could be precipitated at pH 4.5.26 The precipitation was collected and washed with ddH2O
138
for three times. Finally, 3 mL dissolved medium (50 mM Na2CO3, pH 9.5) was added to
139
dissolve the protein, and protein concentration was quantified using BSA as described
7 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
140
above.
141
After spraying with ddH2O, MHNPs, Cry1Ac protein and Cry1Ac-MHNPs
142
respectively, another group of leaves was treated with ddH2O runoff treatments and
143
air-dried as described above. Subsequently, the leaves were punched into wafer (d = 6
144
mm), stored at -80 °C in ultra-low temperature freezer (Thermo Scientific Co., USA) for
145
12 h, and then dried in vacuum desiccator overnight for further test. The leaves were
146
characterized by SEM.
147
2.8. Pest Bioassays. Bioassays were conducted according to a previously described
148
protocol by Liao30 with minor modifications. Briefly, artificial diet was added into
149
24-well tissue culture plates, and then 50 µL toxin (Cry1Ac protein concentrations were
150
3.12, 6.25, 12.5, 25, 50 and 100 µg/mL) or control [ddH2O, MHNPs (0.03 g/mL)] were
151
evenly transferred onto the surface of the diet and allowed to dry before addition of the
152
larvae. Subsequently, one second-instar H. armigera was added to each well (n = 24 per
153
treatment). Finally, after incubation in the environmentally controlled room (T = 27 ±
154
1 °C, RH = 60 ± 5%, L:D = 16:8) for 7 days, larval mortality was scored by gentle
155
probing. All the treatments were carried out in triplicate.
156
To further investigate the adhesion performance, leaves were divided into four groups
157
and treated with different water runoff treatments according to the Section 2.7. Next, the
158
leaves were punched into wafer (d = 6 mm) and randomly divided into three groups, with
159
six replications in each group. Leaves were then added into 12-well tissue culture plates,
8 ACS Paragon Plus Environment
Page 8 of 34
Page 9 of 34
Journal of Agricultural and Food Chemistry
160
and one larva was added to each well (n = 6 per treatment). Larval mortality was scored
161
by gentle probing.
162
2.9. Acid Hydrolysis of MHNPs. To simulate the acid hydrolysis of MHNPs in the
163
field, MHNPs and Cry1Ac-MHNPs (the loading ratio was 1:15.15) were mixed in 2-mL
164
centrifuge tube containing 1 mL 30 mM MES medium (pH 5.6) at room temperature with
165
mild agitation. The supernatant was replaced with fresh medium everyday. The weight of
166
MHNPs was recorded. The control group was set as ddH2O (pH 6.8).
167
2.10. Biosafety Evaluation of MHNPs. 2.10.1. Biosafety evaluation on cotton.
168
Biosafety evaluation of MHNPs on cotton (plant) was conducted with seed germination
169
assays.31,32 Briefly, an 11-cm filter paper (Whatman) was placed in a 150-mm plastic petri
170
dish. Then 5 mL of test solution was added onto the filter paper. Test solutions were
171
ddH2O, NaOH (pH 10.6), 12.5-500 mg/L Mg2+ (MgSO4·7H2O) or 12.5-500 mg/L
172
MHNPs. A total of 12 cotton seeds were placed on the filter paper. After growing for 8
173
days, roots and shoots of germinated seeds were measured using digital calipers, and the
174
germination rate was recorded. Additionally, to evaluate the influence of the MHNPs to
175
the cotton leaf, one milliliter 0.03 g/mL MHNPs or ddH2O were sprayed evenly in the
176
surface of the cotton leaf (n = 6 per treatment). After 15 days, the total chlorophyll and
177
carotenoid of the leaves were extracted according to a previously described method.33
178
The total chlorophyll and carotenoid of the leaves in different treatments were measured
179
by UV–Vis absorptiometry (UV-1600, Japan). All tests were carried out in triplicate.
9 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
180
2.10.2. Biosafety evaluation on Bt and E. coli. Bt (HD73) (Gram-positive
181
bacterium) was added into the LB containing 12.5-500 mg/L Mg2+ (MgSO4·7H2O),
182
12.5-500 mg/L MHNPs, ddH2O or NaOH (pH 10.6) and cultured at 30 °C for 24 h. The
183
OD600 of the resulting solution was recorded by UV–Vis absorptiometry (UV-1600, Japan)
184
to reflect the growth of Bt. Additionally, biosafety evaluation on E. coli (Gram-negative
185
bacterium) was also conducted at 37 °C. All tests were carried out in triplicate.
186
2.10.3. Biosafety evaluation on pest. Biosafety evaluation on pest was conducted
187
according to the Section 2.8. Second-instar H. armigera was selected for the test. All tests
188
were carried out in triplicate.
189
2.11. Statistical Analysis. All results were expressed as means ± standard deviation
190
(SD). Data were arranged with Microsoft Excel 2016 and analyzed with SPSS 18.0 in
191
independent t-test and Probit algorithm. A p value of < 0.05 was considered as
192
statistically significant.
193
3. RESULTS AND DISCUSSION
194
3.1. Synthesis and Morphology Investigation. MHNPs were synthesized in
195
order to fabricate a carrier for Cry1Ac protein. SEM images demonstrated that MHNPs
196
had the flower-like self-supported structure consisting of cross nano-sheets (Figure S1a),
197
which was similar to the reported morphology of MHNPs.23,34 The morphology of
198
Cry1Ac-MHNPs had no obvious changes (Figure S1b). Additionally, the EDS revealed
199
that the compound contained C, N, P and S elements (Figure S3), confirming that Cry1Ac
10 ACS Paragon Plus Environment
Page 10 of 34
Page 11 of 34
Journal of Agricultural and Food Chemistry
200
protein was loaded onto MHNPs. Besides, we also found that the morphology of MHNPs
201
was not changed according to the TEM images (Figure S1c and d), indicating the
202
structural stability of MHNPs. Moreover, the physical size and distribution of particle
203
size were determined, and a (Z average) particle dimension of 712 nm (MHNPs) and 825
204
nm (Cry1Ac-MHNPs) was observed, indicating that MHNPs and Cry1Ac-MHNPs had a
205
little agglomeration in water (Figure S4).
206
3.2. Stable Property and Interaction Analysis. We performed XRD, TGA, zeta
207
potential measurements and FT-IR analyses in order to investigate stability of MHNPs as
208
well as the interactions between MHNPs and Cry1Ac protein. XRD patterns of MHNPs
209
showed that no obvious new peak or peak shift was found before and after loading of
210
Cry1Ac protein (Figure 1a), indicating that no obvious chemical reaction occurred
211
between Cry1Ac protein and MHNPs and the adsorption process might be induced by
212
physical modification. The physical adsorption process might be beneficial to the stability
213
of Cry1Ac protein, suggesting that MHNPs did not affect the biological activity of
214
Cry1Ac protein. Additionally, the size of MHNPs at the (101) direction was 18.53 nm
215
according to the Scherrer equation, close to the reported value for MHNPs (15.60 nm),23
216
indicating that MHNPs in some dimensions were at nano level and they could be
217
embedded into the groove of the leaf surface.
218
The TGA measurement showed that the weight loss of MHNPs at 300 °C might be
219
attributed to the H2O loss from MHNPs. Moreover, the weight loss of MHNPs within the
11 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
220
temperature range of 300−450 °C might be attributed to the decomposition of Mg(OH)2
221
and subsequent transformation into MgO (Figure 1b).35 The TGA pattern of MHNPs
222
demonstrated that MHNPs could be a perfect nanocarrier for delivery of Cry1Ac protein.
223
The zeta potential measurement was also performed to investigate the interface binding
224
between MHNPs and Cry1Ac protein. The results showed that Cry1Ac protein carried
225
negatively charges, while MHNPs exhibited a positively charged surface, and
226
Cry1Ac-MHNPs exhibited a negatively charged surface (Figure 1c). This result indicated
227
that the binding between MHNPs and Cry1Ac protein could be driven by the electrostatic
228
interactions.
229
Besides, FTIR measurement was employed to further investigate the interaction
230
between MHNPs and Cry1Ac protein. Figure 1d shows that the intense peaks at 3699.8
231
cm−1 and 448.9 cm−1 were the characteristic peaks of Mg–O.36 A new peak at about
232
1647.2 cm−1 might belong to the –NH2 groups in Cry1Ac-MHNPs, indicating that the Cry
233
protein was adsorbed onto MHNPs. Additionally, the intensity of the hydroxyl group
234
(-OH) absorption peak (3448 cm−1) was significantly increased. These results showed that
235
the protein was adsorbed onto MHNPs. BET measurement showed that MHNPs
236
possessed a high surface area at a value of 100.1 m²/g, confirming that MHNPs had large
237
capacity to absorb Cry1Ac protein.
238
3.3. Loading of Cry1Ac Protein onto MHNPs. To construct the Cry1Ac-MHNP
239
complexes and investigate the optimal and complete loading process of Cry1Ac protein
12 ACS Paragon Plus Environment
Page 12 of 34
Page 13 of 34
Journal of Agricultural and Food Chemistry
240
onto MHNPs, Cry1Ac protein was loaded onto MHNPs at different loading ratios. The
241
Cry1Ac protein was extracted from Bt (HD73), and the SDS-PAGE revealed a molecular
242
mass of 130 kDa for Cry1Ac protein (Figure 2a, lane 1).26 The Cry1Ac protein was
243
completely loaded at a Cry1Ac/MHNP mass ratio of 1:19.68 (w:w, mg) (Figure 2a, lane
244
6), and the adsorption process did not affect the size of Cry1Ac protein, which was
245
consistent with previous study.37 Moreover, the concentration measurement of the
246
Cry1Ac protein in the supernatant at this mass ratio showed that 97.16% Cry1Ac protein
247
was loaded onto MHNPs (Figure 2b), suggesting that MHNPs had high adhesive strength
248
toward Cry1Ac protein.
249
3.4. Binding Performance between Cry1Ac-MHNPs and Cotton Leaf.
250
According to the adsorption results between Cry1Ac protein and MHNPs, we
251
investigated the adhesion performance between Cry1Ac-MHNPs and cotton leaf. There
252
were lots of micro/nano-grooves on the surface of cotton leaf, resulting in a rough surface
253
and a high adhesion ability for MHNPs (Figure 3a). When Cry1Ac protein was loaded,
254
there was no obvious change in leaf surface (Figure 3c). When MHNPs and
255
Cry1Ac-MHNPs were sprayed onto the leaf surface, lots of micro/nano-sheets were
256
embedded into the groove of the leaf surface (Figure 3b). Therefore, after ddH2O runoff
257
treatments, there were still a large amount of MHNPs distributed on the leaf surface
258
(Figure 3d). This result confirmed the strong adhesion ability of MHNPs on the leaf
259
surface.
13 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
260
To further certify the adsorption performance between Cry1Ac-MHNPs and leaf, the
261
Cry1Ac protein on the leaf surface was extracted, and the concentration measurement
262
confirmed the anti-washing ability of MHNPs (Figure 3e). The retained protein amount
263
was increased along with the mass of MHNPs, and retained protein biomass in groups of
264
15, 20 and 30 mg was significantly higher compared with Cry1Ac protein along group (p
265
< 0.01). The significant increase of the adhesion in Cry1Ac protein biomass was mainly
266
attributed to the high adsorption and retaining capacities of MHNPs on the surface of
267
cotton leaf.
268
3.5. Acid Hydrolysis of MHNPs. To investigate the residual period of
269
Cry1Ac-MHNPs, 30 mM MES medium (pH 5.6) was added to MHNPs and
270
Cry1Ac-MHNPs to simulate the acid hydrolysis of MHNPs in the nature environment.
271
The weight of MHNPs was not changed obviously when MHNPs were mixed with
272
ddH2O. However, the weight of MHNPs was slowly decreased, and finally an equilibrium
273
was established when MHNPs were rinsed with the MES medium for 27 times.
274
Additionally, the residual period of Cry1Ac-MHNPs was same as MHNPs (Figure S5a).
275
This result indicated that loading of Cry1Ac protein onto MHNPs did not affect the acid
276
hydrolysis process of MHNPs. Meanwhile, the dry weight of final samples confirmed
277
that MHNPs could be slowly resolved by acid medium, while they remained stable in the
278
neutral environment (Figure S5b). The result demonstrated that Cry1Ac-MHNPs had a
279
balance between long persistence and biodegradability, which was beneficial for the
14 ACS Paragon Plus Environment
Page 14 of 34
Page 15 of 34
280
Journal of Agricultural and Food Chemistry
economy and environment.
281
3.6. Pest Bioassay. Bioassays were conducted on the artificial diet. Table S1 shows
282
that Cry1Ac protein adsorbed and non-adsorbed MHNPs had comparable LC50 values
283
[LC50 (Cry1Ac) = 0.67 (0.57–0.79) µg/cm2 and LC50 (Cry1Ac-MHNPs) = 0.71 (0.60–0.86) µg/
284
cm2]. The larvae showed abnormal size reduction after the treatment with Cry1Ac protein,
285
and the size of larvae was negatively correlated with the concentration of Cry1Ac protein
286
(Figure S6). However, there was no obvious difference in size before and after the
287
treatment of MHNPs, suggesting that MHNPs did not affect the toxicity of Cry1Ac
288
protein. This finding was consistent with a previous report that silica particles do not
289
change the biological activity of Cry1Ab.15
290
In addition, cotton leaves with different treatments were prepared to feed H. armigera
291
larvae. At the end of 72 h, the larval mortality after treatment of Cry1Ac-MHNPs was
292
significantly higher compared with other treatments (p < 0.001) (Figure 4a). Figure 4b
293
reveals that the larvae treated with Cry1Ac-MHNPs-leaf showed abnormal size reduction
294
compared with others. This finding might be attributed to the high adhesion ability of
295
Cry1Ac-MHNPs on the cotton leaves. These results further confirmed the high adsorption
296
and retaining capacities of MHNPs on the leaf, indicating that MHNPs could be used as a
297
potential adjuvant for biopesticide in agricultural applications.
298
3.7. Biosafety of MHNPs. In order to assess the biosafety of MHNPs, we
299
investigated the effects of different concentrations of Mg2+ and MHNPs on cotton, Bt, E.
15 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
300
coli and H. armigera. With increasing the concentration of Mg2+ and MHNPs from 12.5
301
to 500 mg/mL, the cotton seed germination and the shoot length and the root length had
302
no significant difference with the treatment of ddH2O (p > 0.05) (Figure 5 a and b).
303
Additionally, with spraying the MHNPs on the surface of cotton leave, the total
304
chlorophyll and carotenoid had no significant difference with the treatment of ddH2O (p >
305
0.05) (Figure S7). Meanwhile, the OD600 value of Bt and E. coli after adding with Mg2+
306
and MHNPs (12.5-500 mg/mL) exhibited no significant difference with the control group
307
(p > 0.05), suggesting the MHNPs did not affect the growth of Bt and E. coli (Figure 5c).
308
Additionally, the mortality of H. armigera with treatments of Mg2+ and MHNPs
309
(12.5-500 mg/mL) had no significant difference with ddH2O group (p > 0.05) (Figure 5
310
d). The results above suggesting that MHNPs could be used as a safe adjuvant for
311
preparation of Bt formulation.
312
Supporting Information
313
Additional figures and table depicting the data in SEM and TEM images of MHNPs and
314
Cry1Ac-MHNPs, adsorption kinetic analysis, EDS patern of Cry1Ac-MHNPs, size
315
distribution of MHNPs and Cry1Ac-MHNPs particles, acid hydrolysis of MHNPs,
316
mortality and the digital photographs of second instar larvae of H. armigera treated with
317
Cry1Ac protein and Cry1Ac-MHNPs on the artificial diet and the amount of the
318
chlorophyll and carotenoid of the cotton leave before and after treating with MHNPs.
319
This material is available free of charge via the Internet at http://pubs.acs.org.
16 ACS Paragon Plus Environment
Page 16 of 34
Page 17 of 34
Journal of Agricultural and Food Chemistry
320
Funding
321
This work was supported by the National Natural Science Foundation of China
322
(31601686), Natural Science Foundation of Fujian Province, China (2016J01112),
323
Science Fund for Distinguished Young Scholars of Fujian Agriculture and Forestry
324
University (Grant xjq201719), and the Special Fund for Scientific and Technological
325
Innovation of Fujian Agriculture and Forestry University (Grants CXZX2017214,
326
KF2015063-065).
327
Notes
328
The authors declare no competing financial interest.
329 330
REFERENCES
331
(1) Walvekar, V. A.; Bajaj, S.; Singh, D. K.; Sharma, S. Ecotoxicological assessment of
332
pesticides and their combination on rhizospheric microbial community structure and
333
function of Vigna radiata. Environ. Sci. Pollutr. 2017, 24, 17175-17186.
334
(2) Ravier, I.; Haouisee, E.; Clement, M.; Seux, R.; Briand, O. Field experiments for
335
the evaluation of pesticide spray-drift on arable crops. Pest Manage. Sci. 2005, 61,
336
728-736.
337
(3) Chen, J. W.; Aimanova, K. G.; Fernandez, L. E.; Bravo, A.; Soberon, M.; Gill, S. S.
338
Aedes aegypti cadherin serves as a putative receptor of the Cry11Aa toxin from Bacillus
339
thuringiensis subsp israelensis. Biophys. J. 2009, 424, 191-200.
17 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
340
(4) Lu, K. Y.; Gu, Y. Q.; Liu, X. P.; Lin, Y.; Yu, X. Q. Possible insecticidal mechanisms
341
mediated by immune-response-related Cry-binding proteins in the midgut juice of
342
Plutella xylostella and Spodoptera exigua. J. Agric. Food Chem. 2017, 65, 2048-2055.
343
(5) Arenas, I.; Bravo, A.; Soberon, M.; Gomez, I. Role of alkaline phosphatase from
344
Manduca sexta in the mechanism of action of Bacillus thuringiensis Cry1Ab toxin. J.
345
Biol. Chem. 2010, 285, 12497-12503.
346 347
(6) Bravo, A.; Gill, S. S.; Soberon, M. Mode of action of Bacillus thuringiensis Cry and Cyt toxins and their potential for insect control. Toxicon 2007, 49, 423-435.
348
(7) Melo, A. L.; Soccol, V. T.; Soccol, C. R. Bacillus thuringiensis: mechanism of
349
action, resistance, and new applications: a review. Crit. Rev. Biotechnol. 2016, 36,
350
317-326.
351
(8) Cai, D. Q.; Wang, L. H.; Zhang, G. L.; Zhang, X.; Wu, Z. Y. Controlling pesticide
352
loss by natural porous micro/nano composites: straw ash-based biochar and biosilica.
353
ACS Appl. Mater. Inter. 2013, 5, 9212-9216.
354 355
(9) Nair, R.; Varghese, S. H.; Nair, B. G.; Maekawa, T.; Yoshida, Y.; Kumar, D. S. Nanoparticulate material delivery to plants. Plant Sci. 2010, 179, 154-163.
356
(10) Sharma, S.; Singh, S.; Ganguli, A. K.; Shanmugam, V. Anti-drift nano-stickers
357
made of graphene oxide for targeted pesticide delivery and crop pest control. Carbon
358
2017, 115, 781-790.
18 ACS Paragon Plus Environment
Page 18 of 34
Page 19 of 34
359 360
Journal of Agricultural and Food Chemistry
(11) Xiang, Y. B.; Wang, M.; Sun, X.; Cai, D. Q.; Wu, Z. Y. Controlling pesticide loss through nanonetworks. ACS Sustainable Chem. Eng. 2014, 2, 918-924.
361
(12) Xiang, Y. B.; Wang, N.; Song, J. M.; Cai, D. Q.; Wu, Z. Y. Micro-nanopores
362
fabricated by high-energy electron beam irradiation: suitable structure for controlling
363
pesticide loss. J. Agric. Food Chem. 2013, 61, 5215-5219.
364
(13) von der Lühe, M.; Weidner, A.; Dutz, S.; Schacher, F. H. Reversible electrostatic
365
adsorption of polyelectrolytes and bovine serum albumin onto polyzwitterion-coated
366
magnetic multicore nanoparticles: implications for sensing and drug delivery. ACS Appl.
367
Nano Mater. 2017, 1, 232-244.
368
(14) Helassa, N.; Quiquampoix, H.; Noinville, S.; Szponarski, W.; Staunton, S.
369
Adsorption and desorption of monomeric Bt (Bacillus thuringiensis) Cry1Aa toxin on
370
montmorillonite and kaolinite. Soil Biol. Biochem. 2009, 41, 498-504.
371
(15) Madliger, M.; Gasser, C. A.; Schwarzenbach, R. P.; Sander, M. Adsorption of
372
transgenic insecticidal Cry1Ab protein to silica particles. Effects on transport and
373
bioactivity. Environ. Sci. Techno. 2011, 45, 4377-4384.
374
(16) Placido, A.; de Oliveira Farias, E. A.; Marani, M. M.; Vasconcelos, A. G.; Mafud,
375
A. C.; Mascarenhas, Y. P.; Eiras, C.; Leite, J. R.; Delerue-Matos, C. Layer-by-layer films
376
containing peptides of the Cry1Ab16 toxin from Bacillus thuringiensis for potential
377
biotechnological applications. Mater. Sci. Eng., C 2016, 61, 832-841.
19 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
378
(17) Wu, C. C.; Hu, Y.; Miller, M.; Aroian, R. V.; Sailor, M. J. Protection and delivery
379
of anthelmintic protein Cry5B to nematodes using mesoporous silicon particles. ACS
380
nano 2015, 9, 6158-6167.
381
(18) Yu, W. H.; Li, N.; Tong, D. S.; Zhou, C. H.; Lin, C. X.; Xu, C. Y. Adsorption of
382
proteins and nucleic acids on clay minerals and their interactions: a review. Appl. Clay
383
Sci. 2013, 80-81, 443-452.
384
(19) Zhou, X. Y.; Huang, Q. Y.; Chen, S. W.; Yu, Z. N. Adsorption of the insecticidal
385
protein of Bacillus thuringiensis on montmorillonite, kaolinite, silica, goethite and red
386
soil. Appl. Clay Sci. 2005, 30, 87-93.
387
(20) Brumfiel, G. Nanotechnology: a little knowledge. Nature 2003, 424, 246-248.
388
(21) Dreher, K. L. Health and environmental impact of nanotechnology: toxicological
389
assessment of manufactured nanoparticles. Toxicol. Sci. 2004, 77, 3-5.
390
(22) Geoff, B. Nanotechnology: a little knowledge. Nature 2003, 424, 246-248.
391
(23) Cao, Q.; Huang, F.; Zhuang, Z. Y.; Lin, Z. A study of the potential application of
392
nano-Mg(OH)2 in adsorbing low concentrations of uranyl tricarbonate from water.
393
Nanoscale 2012, 4, 2423-2430.
394
(24) Dong, C. X.; Cairney, J.; Sun, Q. H.; Maddan, O. L.; He, G. H.; Deng, Y. L.
395
Investigation of Mg(OH)2 nanoparticles as an antibacterial agent. J. Nanopart. Res. 2010,
396
12, 2101-2109.
20 ACS Paragon Plus Environment
Page 20 of 34
Page 21 of 34
Journal of Agricultural and Food Chemistry
397
(25) Li, C. R.; Zhuang, Z. Y.; Huang, F.; Wu, Z. C.; Hong, Y. P.; Lin, Z. Recycling rare
398
earth elements from industrial wastewater with flowerlike nano-Mg(OH)2. ACS Appl.
399
Mater. Inter. 2013, 5, 9719-9725.
400
(26) Zhou, Z. S.; Yang, S. J.; Shu, C. L.; Song, F. P.; Zhou, X. P.; Zhang, J. Comparison
401
and optimization of the method for Cry1Ac protoxin preparation in HD73 strain. J.
402
Integr. Agr. 2015, 14, 1598-1603.
403
(27) Chen, Z.; Zhuang, Z. Y.; Cao, Q.; Pan, X. H.; Guan, X.; Lin, Z.
404
Adsorption-induced crystallization of U-rich nanocrystals on nano-Mg(OH)2 and the
405
aqueous uranyl enrichment. ACS Appl. Mater. Inter. 2014, 6, 1301-1305.
406
(28) Pan, X. H.; Wang, Y. H.; Chen, Z.; Pan, D. M.; Cheng, Y. J.; Liu, Z. J.; Lin, Z.;
407
Guan, X. Investigation of antibacterial activity and related mechanism of a series of
408
nano-Mg(OH)2. ACS Appl. Mater. Inter. 2013, 5, 1137-1142.
409 410 411
(29) Lowry, O. H.; Rosebrough, N. J.; Farr, A. L.; Randall, R. J. Protein measurement with the folin phenol reagent. J. Biol. Chem. 1951, 193, 265-275. (30) Liao, C. Y.; Heckel, D. G.; Akhurst, R. Toxicity of Bacillus thuringiensis
412
insecticidal
413
(Lepidoptera). J. Invertebr. Pathol. 2002, 80, 55-63.
414 415
proteins
for
Helicoverpa
armigera
and
Helicoverpa
punctigera
(31) Gorka, D. E.; Liu, J. Effect of direct contact on the phytotoxicity of silver nanomaterials. Environ. Sci. Techno. 2016, 50, 10370-10376.
21 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
416
(32) Xiang, Y. B.; Zhang, G. L.; Chi, Y.; Cai, D. Q.; Wu, Z. Y. Fabrication of a
417
controllable nanopesticide system with magnetic collectability. Chem. Eng. J. 2017, 328,
418
320-330.
419 420
(33) Su, S.; Zhou, Y.; Qin, J. G.; Yao, W.; Ma, Z. Optimization of the method for chlorophyll extraction in aquatic plants. J. Freshwater Ecol. 2010, 25, 531-538.
421
(34) Cao, H. Q.; Zheng, H.; Yin, J. F.; Lu, Y. X.; Wu, S. S.; Wu, X. M.; Li, B. J.
422
Mg(OH)2 complex nanostructures with superhydrophobicity and flame retardant effects.
423
J. Phys. Chem. C 2010, 114, 17362-17368.
424
(35) Yousefi, S.; Ghasemi, B.; Tajally, M.; Asghari, A. Optical properties of MgO and
425
Mg(OH)2 nanostructures synthesized by a chemical precipitation method using impure
426
brine. J. Alloys Compd. 2017, 711, 521-529.
427
(36) Wang, S. Y.; He, W. Z.; Liu, C.; Li, G. M.; Zhang, F. E. Characterizations and
428
preparation of Mg(OH)2 nanocrystals through ultrasonic-hydrothermal route. Res. Chem.
429
Intermed. 2016, 42, 4135-4145.
430
(37) Pan, X. H.; Xu, Z. Y.; Li, L.; Shao, E. S.; Chen, S. L.; Huang, T. Z.; Chen, Z.; Rao,
431
W. H.; Huang, T. P.; Zhang, L. L.; Wu, S. Q.; Guan, X. Adsorption of insecticidal crystal
432
protein Cry11Aa onto nano-Mg(OH)2: Effects on bioactivity and anti-ultraviolet ability.
433
J. Agric. Food Chem. 2017, 65, 9428-9434.
434 435
22 ACS Paragon Plus Environment
Page 22 of 34
Page 23 of 34
Journal of Agricultural and Food Chemistry
436 437
Figure 1. (a) XRD pattern, (b) TGA, (c) zeta potential measurements and (d) FTIR of the
438
samples.
439 440
23 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
441 442
Figure 2. (a) SDS-PAGE analysis of the adsorption between Cry1Ac protein and MHNPs
443
[M: Marker; 1: Cry1Ac protein; 2–6: Cry1Ac-MHNPs (w:w)] at various ratios of 1:3.23,
444
1:6.56, 1:9.84, 1:13.12 and 1:19.68. (b) Adsorption rate between Cry1Ac protein and
445
MHNPs.
446 447
24 ACS Paragon Plus Environment
Page 24 of 34
Page 25 of 34
Journal of Agricultural and Food Chemistry
448 449
Figure 3. (a–d) SEM images of cotton leaves treated with ddH2O, MHNPs, Cry1Ac
450
protein or Cry1Ac-MHNPs, respectively. (e) Adhesion performance of Cry1Ac protein
451
after loading onto different mass of MHNPs. Compared with the control group, statistical
452
significance is shown with **p < 0.01.
453 454 455 456 457 458 459
25 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
460 461
Figure 4. (a) Mortality of the pest after feeding leaves with different treatments for 72 h.
462
Compared with the Cry1Ac-MHNP group, statistical significance is shown with ***p