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Agricultural and Environmental Chemistry
The mode of action of adjuvants – Relevance of physicochemical properties for effects on the foliar application, cuticular permeability and greenhouse performance of Pinoxaden Katja Arand, Elisabeth Asmus, Christian Popp, Daniel Schneider, and Markus Riederer J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.8b01102 • Publication Date (Web): 22 May 2018 Downloaded from http://pubs.acs.org on May 22, 2018
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Journal of Agricultural and Food Chemistry
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The mode of action of adjuvants – Relevance of physicochemical properties for
2
effects on the foliar application, cuticular permeability and greenhouse
3
performance of Pinoxaden
4 5 6
Katja Aranda§, Elisabeth Asmusa§#, Christian Poppb, Daniel Schneiderb and Markus
7
Riederera*
8 9
a
University of Würzburg, Julius von Sachs Institute of Biosciences, Julius-von-Sachs-
10
Platz 3, Würzburg, D-97082, Germany
11
b
12
Münchwilen, CH-4333, Switzerland
Syngenta
Crop
Protection,
Global
Formulation
Technology,
Breitenloh
5,
13 14 15
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ABSTRACT
17
We comprehensively studied the complexity of mode of action of adjuvants by
18
uncoupling the parameters contributing to the spray process during foliar application
19
of agrochemicals. The ethoxylated sorbitan esters Tween 20 and Tween 80 improved
20
the efficiency of Pinoxaden (PXD) in controlling grass-weed species in greenhouse
21
experiments by aiding retention, having humectant properties, maintaining the
22
bioavailability and increasing the cuticular penetration of PXD. The non-ethoxylated
23
sorbitan esters Span 20 and Span 80 showed minimal effects on retention, droplet
24
hydration or cuticular penetration, resulting in reduced PXD effects in the
25
greenhouse. Tris(2-ethylhexyl)phosphate (TEHP) does not contribute much to
26
retention and spreading but strongly enhances the diffusion of PXD across isolated
27
P. laurocerasus cuticular membranes. As TEHP was most efficient in controlling the
28
growth of grass-weed species, we propose, that the direct effect of penetration aids
29
on cuticular permeation plays a key role in the efficiency of foliar applied
30
agrochemicals.
31 32 33 34 35 36 37 38
KEYWORDS: Non-ionic surfactants, Polysorbates, Cuticular Penetration, Foliar
39
Application, Mode of Action
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INTRODUCTION
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Foliar spray application of agrochemicals is standard practice to protect crop plants
43
against various pests and diseases and to control weeds. The spray process is very
44
complex, and several factors such as droplet formation, droplet retention, the wetting
45
and spreading process on the leaf surface but also spray deposit formation and
46
hydration followed by the permeation of the active ingredient (AI) through the plant
47
cuticle are closely connected.1,2 The cuticular membrane is an extracellular
48
biopolymer layer, mostly composed of hydroxyl modified and esterified fatty acids.
49
The cutin matrix is impregnated with very long chain aliphatics with several functional
50
modifications and/or cyclic triterpenoids, the so-called cuticular waxes.3 Foliar-applied
51
AIs have to permeate the lipophilic layer by the physical process of diffusion4 to reach
52
the underlying plant tissue.5 In many species, very complex three-dimensional wax
53
crystalloids structures on the surface of the cuticle strongly contribute to the
54
hydrophobic surface properties and make them extremely difficult to wet.6 Thus,
55
spray retention would be dramatically reduced. As the plant cuticle is physically and
56
chemically designed to protect the plant against water loss and other biotic and
57
abiotic environmental factors,7 the overall effect of spray droplets are generally
58
challenged by this barrier. Therefore, adjuvants are used to optimize the
59
physicochemical characteristics of the spray liquid to improve the biological
60
performance of the AI. This can be achieved through spray liquid modifying
61
properties8-11 like pH adjustment, foaming activity, retention,1 wetting and spreading
62
behavior12 or humectancy.13-15 Penetration aids impact the bioavailability of the AI in
63
the spray deposit16,17 or modify the cuticular transport properties.13,18-24 Considering
64
the various processes during spray application, it is evident that adjuvants can either
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impact individual or several steps of the application procedure. Thus, one adjuvant
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can have multifunctional properties, which make the elucidation of the mode of action
67
of adjuvants very complex. Therefore, the aim of this work was to investigate the
68
individual
69
physicochemical and structural properties of the adjuvant solutions, their effect on
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cuticular penetration of the AI Pinoxaden and its efficacy on weeds. Besides the
71
commercially
72
ethylhexyl)phosphate (TEHP) two commonly used polysorbates (Tween 20 and
73
Tween 80) were selected. The corresponding non-ethoxylated sorbitan esters Span
74
20 and Span 80 were also included in this study because they share the basic
75
structure with the Tweens but without polyethoxylation. From this point of view, this
76
study will systematically contribute to a fundamental understanding of the distinct
77
mode of actions of adjuvants in foliar applied formulations.
functions
used
of
adjuvants
built-in
from
adjuvant
different
for
perspectives,
Pinoxaden
products
including
tris(2-
78
79
MATERIALS AND METHODS
80
Active ingredients
81
The post-emergence graminicide Pinoxaden (PXD) (8-(2,6-Diethyl-p-tolyl)-1,2,4,5-
82
tetrahydro-7-oxo-7H-pyrazolo[1,2-d][1,4,5]oxadiazepin-9-yl-2,2-dimethylpropionat)
83
(log KO/W 3.2) was used in form of the commercial non-adjuvanted EC100 formulation
84
Axial 100 EC (100 g l-1 PXD, Syngenta Crop Protection AG, Switzerland) containing
85
the safener cloquintocet-mexyl.
86 87
Adjuvants
88
The non-ionic surfactants sorbitan monolaurate (Span® 20, CAS: 1338-39-2) and
89
sorbitan monooleate (Span® 80, CAS: 1338-43-8) and their polyethoxylated 4 ACS Paragon Plus Environment
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derivatives polyoxyethylene sorbitan monolaurate (Tween® 20, CAS: 9005-64-5) and
91
polyoxyethylene sorbitan monooleate (Tween® 80, CAS: 9005-65-6) (Figure 1) were
92
obtained from Croda (Nettetal, Germany).
93
The lipophilic adjuvant tris(2-ethylhexyl)phosphate (TEHP) is known to have
94
substantial accelerating effects on the uptake of PXD25 and was therefore used as a
95
positive control in cuticular penetration and greenhouse experiments. TEHP was
96
emulsified with polyvinyl alcohol (TEHP EW400; 400 g l-1) (Syngenta Crop Protection
97
AG, Switzerland) which has no accelerating effects on cuticular penetration itself.
98
Isodecyl alcohol ethoxylate (Trend 90; 900 g l-1) (DuPont de Nemours, La Défense
99
Cedex, France) was used as a positive control adjuvant in retention experiments,
100
because of its pronounced surface tension lowering properties.
101
If not stated otherwise, all samples were used as aqueous solutions or emulsions
102
with an adjuvant concentration of 0.1% (w/v) which is in the typical range for the use
103
of agricultural formulation products.
104
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Plant material
106
For the retention experiments and the contact angle measurements, greenhouse-
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grown winter wheat plants (Triticum aestivum cv. Arina), grown under 14-h light
108
period with 18/17 °C day/night temperature and 70% relative humidity (RH), were
109
used in growth state BBCH 12 (2-leaf-stadium).
110
For greenhouse experiments winter wheat (Triticum aestivum cv. Horatio) and the
111
five grass-weed species wild oat (Avena fatua), Italian rye-grass (Lolium multiflorum),
112
green foxtail (Setaria viridis), awned canary-grass (Phalaris paradoxa) and black
113
grass (Alopecurus myosuroides) were used in growth state BBCH 12 (2-leaf-
114
stadium). Plants were sown together in bio troughs in soil and grown in a greenhouse
115
with a 16h light period and 20/17 °C day/night temperature at around 65% RH.
116 117
Cuticular membranes
118
Cuticular membranes (CM) were obtained from the upper, astomatous surfaces of
119
fully expanded leaves of Prunus laurocerasus cv. Herbergii plants growing in the
120
Botanical Garden of the University of Würzburg. Enzymatic isolation was carried out
121
as described previously.26
122 123
Static surface tension
124
The static surface tension (SST) of aqueous surfactant solutions was determined
125
with the drop shape analyzer DSA100S (Krüss GmbH, Hamburg, Germany) using
126
the pendant drop method.
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Dynamic surface tension
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The dynamic surface tension (DST) of surfactant solutions was measured using the
130
bubble pressure tensiometer BP100 (Krüss GmbH, Hamburg, Germany).
131 132
Retention and leaf coverage
133
The retention tests were carried out in a spray cabin equipped with a variable speed
134
track sprayer at the Global Formulation Technology Centre, Syngenta (Münchwilen,
135
Switzerland). Ten Plants were cut at the bottom and fixed vertically and well-spaced
136
in the spray cabin to prevent spraying shadows. Surfactant solutions were blended
137
with Helios SC 500 (Novartis, Basel, Switzerland) to obtain a concentration of 0.1%
138
of the fluorescent ingredient Tinopal OB CO (2,5-thiophenediylbis(5-tert-butyl-1,3-
139
benzoxazole) and sprayed 50 cm above the plants with a Teejet XR11003VP flat fan
140
nozzle with 2 bars and 8 km h-1. After a 10 min drying period, leaf surfaces were fixed
141
on a red colored surface, illuminated with UV light and photographed on both sides.
142
From the respective pseudo color images, the leaf surface area, as well as the leaf
143
coverage (%), was determined with the software FluorSoft v0.1 (Syngenta Crop
144
Protection, Switzerland). The plants were washed with 8 ml of acetonitrile for 30 s.
145
The solution was filtered into UV glass tubes, and the concentration of Tinopal was
146
measured with the Fluorimeter 96 (Novartis, Basel, Switzerland) with two technical
147
replicates. The excitation light was 375 nm, and the emission light was 435 nm.
148
Retention was calculated as ng Tinopal per leaf surface area.
149 150
Contact angle measurement
151
Contact angle (CA) measurements were performed with the optical contact angle
152
measuring device OCA 15 plus (DataPhysics Instruments GmbH, Filderstadt,
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Germany) including a drop shape analysis (DSA) software. The second leaf of wheat
154
plants was fixed with double-sided adhesive tape on glass slides. A 3 µl droplet of
155
water or the surfactant solutions, each containing 0.1% (w/v) of the strawberry-red
156
azo dye Sanolin Ponceau 4RC 82 (Clariant, Muttenz, Switzerland), was placed on
157
the adaxial leaf surface. Droplet spreading was recorded with 1 fps during 1 minute,
158
and the contact angles were measured at frame 1, 30 and 60. After drying, the
159
droplet spread area of the red colored residue was determined using a microscope
160
(Leica DMR, Leica Microsystems Wetzlar GmbH, Wetzlar, Germany) with the
161
software AxioVision Rel. 4.8 (Carl Zeiss Microscopy GmbH, Jena, Germany).
162
Measurements of at least 10 replicates were carried out for each treatment.
163 164
Simulation of foliar penetration experiments
165
The experimental set-up ‘simulation of foliar uptake/penetration’ (SOFU/SOFP)27 was
166
used to investigate the cuticular penetration of PXD. Cuticular membranes were
167
mounted on chambers made of stainless steel, with the physiological outer side
168
facing towards the atmosphere. A 5 µl droplet of a mixture of Axial 100 EC in water (2
169
g l-1 PXD) without or with adjuvant (4 g l-1) was applied to the outer surface. After
170
droplet drying, the chambers were inverted, and 1 ml of deionized water was added
171
as receiver solution. The chambers were placed in closed plastic cups over a
172
glycerol-water mixture (79.7:20.3, w/w) at 25°C to achieve 50% RH.28 At
173
approximately 24 h time intervals, 10 µl aliquots were sampled from the receiver
174
solution and PXD concentrations were quantified by UPLC-MS according to Asmus
175
et al. (2016).29 Plotting the amount of penetrated PXD as a function of time, the
176
resulting slope of the linear section represents the flow rate in µg s-1.
177
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Greenhouse experiments
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Greenhouse experiments were conducted with five different concentrations of
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Axial EC100 with application rates of 1.875, 3.75, 7.5, 15 and 30 g PXD ha-1 either in
181
water as a negative control, with 0.1% surfactants or with 0.2% TEHP as a positive
182
control. All treatment combinations were sprayed on a selection of six different
183
monocot species in a spray cabin with a Teejet XR11002VP flat fan nozzle at 2 bars
184
and 3.3 km h-1 that resulted in an actual spray quantity of 200 l ha-1 at the plant
185
intercept point. Three replicates were made. The experiment was fully randomized.
186
Plants were further grown in a greenhouse as described previously. The assessment
187
was conducted 14 days after application (DAA). Expected symptoms of plants
188
treated with an ACCase inhibiting herbicide are yellowish chloroses at the new
189
growing meristems. The herbicide damage in percent including also the loss of
190
biomass due to inhibited growth and tillering was estimated visually in comparison to
191
non-treated plants.
192 193
RESULTS
194
Surface tension
195
The dynamic surface tension (DST) was measured between 10 ms and 30 s surface
196
age and can be interpreted as a function of time. The static surface tension (SST)
197
was investigated independently at the equilibrium state. The DST and SST of water
198
were constant at around 72 mN m-1 (Figure 1). All adjuvant solutions, except Trend
199
90, showed high initial DST values of about 65 to 72 mN m- 1 but did decrease the
200
surface tension during 30 s with different kinetics (Figure 1). The DST for Span 80
201
stayed consistently high at 72 mN m-1 up to 20 s and then decreased rapidly to a low
202
SST value of 29.3 mN m-1. The DST for Span 20 moderately decreased over time 9 ACS Paragon Plus Environment
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starting from 200 ms and resulted in a final SST value of 48 mN m-1. At young
204
surface ages, the DST for TEHP followed the same kinetic as for Span 20, but from
205
about 1 s, the DST decreased much faster until an SST of 32 mN m-1 was reached.
206
The DST of Tween 20 and Tween 80 decreased linearly with time to ultimately reach
207
SST values of 46 mN m-1 (Tween 80) and 38 mN m-1 (Tween 20). The initial value for
208
Trend 90 was comparably low at about 47 mN m-1, and SST was reached at
209
27.8 mN m-1.
210 211
Contact angle and spread area
212
The initial contact angle of water droplets on the adaxial surface of wheat leaves was
213
about 152° and did not change within 60 s after droplet application (Table 1). The
214
dried-down droplet residue covered an area of about 0.6 mm². With all surfactants,
215
the initial contact angles were about 10° to 20° lower than for water. For Tween 20
216
and Tween 80, contact angles remained constant over the first 60 s resulting in a
217
spread area of about 2 mm² (Table 1). A slight decrease of the CA was observed for
218
both Spans but was more distinct for Span 20 (Table 1). After drying, the residue of
219
Span 20 covered a surface area of about 60 mm², while the coverage of the Span 80
220
residue was nearly tenfold smaller (~6 mm²) (Figure S1).
221 222
Retention and leaf coverage
223
In spray experiments, the maximum retention was obtained with Trend 90 (0.95 ng
224
mm-²) which also caused the highest leaf coverage (~14 %) followed by both Tweens
225
which showed less retention (Tween 20: 0.8 ng mm², Tween 80: 0.6 ng mm²) and
226
achieved a leaf coverage of about 5.3% (Table 1). The retention for both Spans was
227
similar to water (~0.2 ng mm²), but the resulting leaf coverage was about 2 to 4 times
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higher compared to water (~1 %) (Table 1). The retention and leaf coverage values
229
for TEHP were in the medium range (Table 1).
230 231
Simulation of foliar penetration experiments
232
The diffusion of PXD across isolated P. laurocerasus cuticles was studied from a
233
rehydrated deposit containing 10 µg PXD at 50% RH. Without additional adjuvants,
234
the flux rate of PXD was about 0.1×10- 6 µg s-1 (Figure 2). With Span 20 or Span 80,
235
the PXD flow was comparable to the non-adjuvanted control (Figure 2). By adding
236
Tween 20 or Tween 80, the PXD flow was significantly enhanced to 4.7×10- 6 µg s-1
237
or 2.9×10- 6 µg s-1, respectively (Figure 2). With TEHP, the cuticular penetration of
238
PXD (24×10- 6 µg s-1) was increased significantly by more than two orders of
239
magnitude (Figure 2).
240 241
Greenhouse experiments
242
After spraying, typical ACCase symptoms25,30 were visible at the meristematic
243
younger tissue. New leaf tissue turned slowly yellow (chlorotic), or brown leaf spots
244
became visible (necrotic) (Figure 3). The assessment of the grass-weed species
245
Phalaris paradoxa was not conducted, because of the contamination with a
246
considerable amount of a rogue species. Differences were observed due to adjuvant
247
treatment, PXD concentration level or between the plant species (Figure 3, Figure
248
4). No damage on Triticum aestivum was detected (Figure 3) due to the presence of
249
the crop safener cloquintocet-mexyl. Comparing the weed plant species, most
250
damages for all treatments were found for Setaria viridis (SETVI) (Figure 4 A). With
251
increasing PXD concentration, weed damage increased for all plant species and all
252
adjuvant treatments. The overall ranking of adjuvants relating to weed damage was
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almost similar for all plant species. The negative control (no adjuvant) resulted in
254
minimum damage. Span 20 and Span 80 showed only small differences between
255
them but still more damage than the non-adjuvanted control (Figure 4). Tween 20
256
and Tween 80 resulted in higher damage rates than the Spans used in this study.
257
The maximum weed damage was always observed for TEHP whereby 80% damage
258
rates were already reached with medium PXD concentrations of 7.5 g PXD ha-1
259
(Figure 4).
260 261
DISCUSSION
262
Surface active action
263
The retention process of a droplet on the target plant surface is a crucial prerequisite
264
for successful spray application of plant protection agents1,12,31 especially for
265
superhydrophobic plant surfaces which are difficult to wet.32,33 During foliar spray
266
application, droplets are in flight for only about 50-250 ms1,31 and an effective
267
reduction of the surface tension during this critical time frame favors successful
268
droplet adhesion upon impact on the leaf surface.12,34,35 Surface tension
269
measurements showed that all surfactants could effectively reduce the surface
270
tension over time, but in most cases, SST was not even reached after 30 s surface
271
age (Figure 1). The surface tension at a surface age of about 100 ms (94 ms, value
272
depends on the measurement procedure of maximum bubble pressure method) was
273
used to test whether the selected surfactants aid droplet retention on wheat leaves in
274
track sprayer experiments through a reduction in surface activity.
275
For all adjuvants tested except for Trend 90, droplet retention has increased with
276
decreasing surface tension at 94 ms surface age (Figure 5) and amongst them best
277
retention was achieved with Tween 20. This correlation was also previously shown 12 ACS Paragon Plus Environment
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for several other surfactants on maize plants1 which are also very difficult to wet.
279
Nevertheless, at 94 ms surface age, Span 20, Span 80 and TEHP showed a surface
280
tension close to water (Figure 1) and thus, retention on wheat leaves was not
281
significantly improved with these adjuvants (Figure 5).
282
Trend 90 was shown to have potent surface tension lowering properties within the
283
relevant time frame of the spray droplets being in flight (Figure 1). For this reason, it
284
is used as a retention aid, too. However, in our experiments, the retention of Trend
285
90 was comparable to Tween 20 and was lower than would be expected from the
286
correlation obtained with all other adjuvants. One reason might be the risk of droplet
287
shattering36 that tended to increase with decreasing surface tension, especially for
288
large, fast-moving droplets.37 In our track sprayer experiments with well-spaced
289
plants, they would be easily lost to the ground. Under field conditions with much
290
higher leaf area index, small decelerated satellite droplets produced upon the first
291
impact would eventually adhere to neighboring leaves on secondary impact due to
292
their low surface tension. This would improve overall retention.
293
The retention process involves short-term dynamics1,31 and therefore can be
294
correlated to the surface tension at very young surface ages. In contrast to that, the
295
spreading process, which is initiated after successful retention, is less time-bound
296
and can also be affected by adjuvants which reduce the surface tension at surface
297
ages far beyond 250 ms. The wetting or spreading properties of the spray droplets
298
can be characterized by the contact angle between the leaf surface and the droplet.38
299
A very high contact angle for water, as measured for greenhouse-grown wheat
300
leaves
301
surface.33,39 The water droplet forms a sphere on top of the wax crystalloids33
302
resulting in a minimal physical contact area between the droplet and the leaf surface
(151°, Table
1)
indicating
a
superhydrophobic,
very
difficult-to-wet
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303
(Figure S1). For both Tweens and Spans and also TEHP, the initial contact angles
304
were reduced by about 13°-22° only during the first minute upon droplet application
305
(Table 1), but after complete drying, enormous differences in the spread area were
306
detected (Table 1, Figure S1). The contact angle for Span 20 droplets decreased
307
steadily during the first 60 s (and even further until dry-down, not measured) and the
308
final spread area was a hundredfold bigger compared to a pure water droplet residue
309
(Table 1). In contrast to that, the initial contact angle for Tween 20 was lowest within
310
the sorbitan esters tested and only surpassed by Trend 90. This is also reflected in
311
the highest retention effects of Tween 20 (except for Trend 90) within spray
312
experiments (Table 1, Figure 5). Further spreading during the first minute was not
313
detected and the resulting spread area (1.9 mm2) was only about 3-times higher than
314
for pure water. Under controlled laboratory conditions with comparatively high droplet
315
volumes, Span 20 is a very potent spreading agent on extremely hard-to-wet
316
surfaces, while Tween 20 rather acts as a retention aid. In spray experiments, the
317
leaf coverage for Span 20 was similar to Tween 20 (about 5%) even though retention
318
was lower for Span 20. Since the spray droplets are very tiny, they will have been
319
evaporated before the spreading behavior of Span 20 comes into significant effect.
320
Additionally, the total droplet deposition on the leaf surface would not be sufficient
321
with Span 20 due to its poor retention properties.
322
Trend 90 showed by far the lowest initial contact angle, which also decreased over
323
time, resulting in a ca. 30-fold enhanced spread area compared to water. The
324
combination of good retention and spreading properties led to the highest leaf
325
coverage in track spray experiments (Table 1). Nevertheless, the physical value of
326
surface tension alone cannot explain why Span 20 produces a much bigger spread
327
area than Trend 90 when applied as a single droplet. Possible influences of
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interfacial properties40-42 or the size, velocity, and viscosity of the droplets34 were not
329
elucidated in this study.
330 331
Simulation of foliar penetration experiments
332
After droplet adhesion and spreading on the leaf surface, AI uptake into the leaf is
333
initiated. Thereby, cuticular waxes act as a potential barrier to the permeation of
334
organic and inorganic solutes.43,44 The rate of AI permeation is considerably
335
determined by their solubility characteristics related to the physicochemical
336
properties of the cuticle, which are indicated by the octanol/water (KO/W) or
337
cuticle/water (KC/W) partition coefficient.5 The permeation of hydrophilic solutes (log
338
KO/W < 1) takes place via hydrated sites in the cuticle and is therefore influenced by
339
the actual hydration status of the cuticle.45 Cuticular permeation of nonpolar, lipophilic
340
solutes (log KO/W > 1) is favored by factors impairing the resistance of cuticular
341
waxes, e.g. by reducing their crystallinity.43 Thereby; low EO surfactants are known
342
to readily penetrate the cuticle enhancing the lipophilic pathway20,46,47 whereas higher
343
EO surfactants rather increase the permeability for hydrophilic solutes.14,19,48
344
In cuticular penetration experiments with P. laurocerasus, the addition of TEHP
345
significantly enhanced the flow of PXD. Muehlebach et al.25 stated that TEHP might
346
act in the spray deposit by “overcoming active ingredient chemical stability or
347
crystallization issues” thus, maintaining the driving force. On the other hand, it is very
348
likely that the lipophilic adjuvant enters the cuticle and change the structure or the
349
composition of the cuticular pathway,19 thus increasing the mobility of PXD.
350
With Span 20 and Span 80, the PXD diffusion across isolated P. laurocerasus
351
cuticles at 50% RH was not affected significantly, indicating that Spans neither
352
improve the bioavailability of PXD in the spray deposit nor increase its mobility in the 15 ACS Paragon Plus Environment
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rate limiting barrier of the cuticle. In contrast, Tween 20 and Tween 80 enhanced the
354
PXD flow by factors of about 40 and 25, respectively. Tweens are highly diverse and
355
complex mixtures of different molecules varying in the degree of ethoxylation and
356
also in the fatty acid chain length distribution.49,50 Therefore, the potential of the low
357
EO fraction to act within the cuticle20,46,47 might also be a contributing factor for
358
mobilization of PXD. Conversely, it was stated that Tween 20 is known to have poor
359
foliar uptake properties and the activation action is due to humectant properties.47
360
Recently, Asmus et al.15 published a comprehensive data set about the humectant
361
activity (nws) of several surfactants at different humidities, showing that the humectant
362
activity increases with increasing ethoxylation. For the sorbitan esters used in our
363
study, the PXD diffusion across P. laurocerasus cuticles at 50% RH rises with
364
increasing humectant activity and respectively with increasing EO content. These
365
results indicate the enhanced uptake of PXD with Tweens in contrast to Spans is
366
also promoted by their humectant property, preventing the AI from crystal
367
precipitation and thus improving the bioavailability.14
368 369
Greenhouse experiments
370
PXD is a graminicide for the control of wide-spread annual grass-weed species in
371
mainly wheat, and barley.25,51 Since the cuticular membrane of grass species cannot
372
be isolated for further uptake experiments, cuticular membranes of the model plant P.
373
laurocerasus were used to elucidate the underlying mechanisms concerning cuticular
374
penetration. By using a plant species without epicuticular wax crystalloids, we also
375
minimized the effect of wetting and spreading, and the contact area with the droplet
376
was comparable for all adjuvants. To take a step forward, greenhouse experiments
377
were performed with target grass-weeds, to determine whether our findings from 16 ACS Paragon Plus Environment
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378
model systems can be applied to living plants. To minimize retention effects, we used
379
an 02 flat fan nozzle producing a narrow droplet spectrum, so the droplets generated
380
adhere to the leaf surface more easily. Furthermore, plants were grown tightly
381
together resulting in a much bigger leaf area index compared to the retention
382
experiment, where single plants were used. Droplets which bounce off at first impact
383
will be captured at an adjacent leaf instead. PXD is usually applied at application
384
rates of 15-60 g AI ha-1, depending on the target weed species.30,51 To detect
385
differences in the adjuvant response of PXD, we used PXD rates far below the
386
recommended field rate.
387
The mode of action of PXD is the inhibition of the fatty acid biosynthesis which
388
impacts the formation of biomembranes (HRAC-class A).30 The physiological
389
symptoms like plant leaf chlorosis at the growing meristems followed by browning
390
become visible in the grass-weed species within 1-3 weeks after treatment.25 At the
391
time of assessment (14 DAT) considerable differences in the absolute plant damage,
392
depending on plant species, adjuvants and PXD rates were observed (Figure 4). To
393
quantify the adjuvant effects, we calculated the slope of the initial linear part of the
394
dose-response relationship (Figure 4) for each adjuvant. This slope can be used as
395
a proxy to determine the effect of the adjuvant on the biological performance of PXD.
396
Even though the different weed species showed different absolute responses, the
397
same ranking of adjuvants was observed across the species tested (TEHP >> Tween
398
20 > Tween 80 > Span 20 = Span 80 > no adjuvant). The leaf damage values for all
399
species were averaged to compare them with the results gained from laboratory
400
experiments. By plotting the slope against the PXD flow across isolated P.
401
laurocerasus cuticles, a positive relationship was observed between the penetration
402
enhancing effect of all adjuvants and their impact on weed control efficiency of PXD
17 ACS Paragon Plus Environment
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403
in the greenhouse (Figure 6). This indicates that cuticular penetration is one of the
404
major bottlenecks for the weed control efficiency of PXD.
405
In summary, we comprehensively studied the complexity of mode of action of several
406
adjuvants from the sorbitan ester family and TEHP, by uncoupling the many
407
parameters which contribute to the spray process in the field such as droplet
408
retention, spreading, the formation of the spray deposit and also penetration of the AI
409
through the plant cuticle.
410
We showed that the ethoxylated sorbitan esters Tween 20 and Tween 80 have
411
multifunctional adjuvant qualities. They aid retention, have promoting humectant
412
properties, maintaining the bioavailability of PXD in the surface residue and finally
413
increase the cuticular penetration of PXD. The combination of these factors improves
414
the efficacy of PXD in controlling the growth of grass-weed species in the
415
greenhouse compared to non-adjuvanted treatments. In contrast, the non-
416
ethoxylated sorbitan esters Span 20 and Span 80 are rather inefficient since they
417
show minimal effects on retention, droplet hydration or cuticular penetration, resulting
418
in reduced PXD effects in greenhouse experiments. In all grass-weed species, the
419
formulation containing TEHP was most efficient for the use with PXD across the
420
range of rates tested. As it was shown in the surface tension measurements and
421
spray experiments, TEHP does not contribute much to retention and spreading, but it
422
enhanced the diffusion of PXD across isolated cuticular membranes of P.
423
laurocerasus five times compared to the best performing sorbitan ester Tween 20.
424
These findings indicate that the direct effect of penetration aids on PXD plays a
425
critical role and cuticular uptake is a significant bottleneck. In fact, SOFP experiments
426
with isolated cuticles are a well-suited system to screen for potent permeation
427
enhancing adjuvants for AIs such as PXD in a small scale. Nevertheless, in practice,
18 ACS Paragon Plus Environment
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Journal of Agricultural and Food Chemistry
428
also retention and spreading play a significant role since spray droplets behave
429
differently and the leaf area index at the time of application differs. Therefore,
430
additional studies are required to close the gap between laboratory experiments,
431
greenhouse studies with controlled environmental conditions and the real situation in
432
the field.
433 434 435
ABBREVIATIONS USED
436
AI
Active ingredient
437
ALOMY
Alopecurus myosuroides
438
AVEFA
Avena fatua
439
CA
Contact angle
440
CM
Cuticular membrane
441
DAA
Days after application
442
DST
Dynamic surface tension
443
EC
Emulsion concentrate
444
EW
Emulsion oil-in-water
445
EO
Ethylene oxide
446
LOLMU
Lolium multiflorum
447
PXD
Pinoxaden
448
RH
Relative humidity
449
SETVI
Setaria viridis
450
SOFP
Simulation of foliar penetration
451
SST
Static surface tension
452
TEHP
Tris(2-ethylhexyl)phosphate 19 ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
453
TRZAW
Page 20 of 40
Triticum aestivum
454 455
Author Information
456
*Corresponding author
457
e-mail:
[email protected], phone + 49 931 31 86200
458
§
459
Katja Arand and Elisabeth Asmus contributed equally to this work
Author Contribution
460 461
#
462
Bayer AG, Research & Development / Crop Science, Building H872, 65926 Frankfurt
463
am Main, Germany
Present address
464 465
Funding
466
This work was partially supported by a grant from Syngenta Crop Protection AG.
467
Notes
468
The authors declare no competing financial interest.
469 470
ACKNOWLEDGEMENTS
471
The authors deeply express their thanks to René Jaun, Markus Krischke, Andreas
472
Krommrei and James Murdock for their valuable technical assistance.
473 474
SUPPORTING INFORMATION DESCRIPTION
475
Supplementary data associated with this article can be found online. This file
476
includes a comparison of freshly settled droplets (3 µl volume) containing the
477
respective adjuvant and the strawberry-red azo dye Sanolin Ponceau and the droplet
20 ACS Paragon Plus Environment
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Journal of Agricultural and Food Chemistry
478
residue after water evaporation on adaxial Triticum aestivum cv. Arina leaves (Figure
479
S1). This material is available free of charge via the Internet at http://pubs.acs.org
480
21 ACS Paragon Plus Environment
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481
Page 22 of 40
FIGURE CAPTIONS
482 483
Figure 1. Dynamic surface tension as a function of surface age (ms) and static
484
surface tension (mN m-1). The surface age ranges from 10 ms to 30000 ms. Static
485
surface tension values (mN m- 1) indicate the equilibrium-state of surface tensions.
486 487
Figure 2. Box-plots of flow rates of cuticular permeation (F) of PXD in the presence
488
of varying surfactants at 50% RH. Continuous horizontal lines within the boxes
489
represent the median and dotted lines the mean. Whiskers indicate the 5th to 95th
490
percentiles and dots the minimum and maximum values observed. Box-plots
491
indicated with * are significantly different from the non-adjuvanted control (Kruskal-
492
Wallis Test with Dunn’s Test, p < 0.001).
493 494
Figure 3. Photographs of plant troughs 14 days after application. Plants sprayed with
495
non-adjuvanted Axial EC 100 containing 15 g PXD ha-1 water or the respective
496
adjuvant. Plants from left to right: Triticum aestivum, Avena fatua, Lolium multiflorum,
497
Setaria viridis, Phalaris paradoxa and Alopecurus myosuroides. On Triticum
498
aestivum (left) no damages could be observed. The most significant damage was
499
visible for Setaria viridis (fourth from left).
500 501 502
Figure 4.
503
Dose-response curves of mean grass-weed control by PXD with different adjuvant
504
treatments on (A) Setaria viridis (SETVI), (B) Avena fatua (AVEFA), (C) Lolium
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505
multiflorum (LOLMU) and (D) Alopecurus myosuroides (ALOMY). In some cases,
506
error bars (SD) are smaller than the symbols (mean).
507 508
Figure 5. Relationship between the retention (ng Tinopal OB per mm2 leaf area) on
509
Triticum aestivum cv. Arina leaves and the dynamic surface tension (DST) at 94 ms
510
surface age of selected adjuvants. Dots indicate mean values and error bars
511
represent the standard deviation, n=10.
512 513
Figure 6.
514
Correlation between the slope of the initial linear part of the dose response
515
relationship (Figure 4) and the mean cuticular flow rates (F) of PXD with different
516
adjuvants at 50% RH (Figure 2). Mean values of the slope were calculated across all
517
grass-weed species. Error bars represent the standard deviation. Dots for Span 20
518
and Span 80 overlap each other. The non-adjuvanted control is excluded from the
519
regression line (dashed line, R² = 0.99).
520
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521
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Table 1. Contact angles (°) at three respective times and spread area (mm2) after the evaporation of water on the upper side of Triticum aestivum cv. Arina leaves of selected adjuvants. Retention (ng Tinopal OB per mm2 leaf area) and leaf coverage (%) of selected adjuvant solutions on both sides of Triticum aestivum cv. Arina leaves. Mean (SD) n=10.
Tradename
Water Span 20 Span 80 Tween 20 Tween 80 TEHP EW400 Trend 90
Spread area (mm2)
Contact angle (°)
initial 151.9 (4.9) 136.9 (6.3) 138.2 (5.8) 129.7 (4.7) 137.1 (5.1) 132.9 (3.3) 56.4 (5.7)
30 s 151.8 (5.9) 128.6 (10.6) 136.7 (6.9) 129.2 (4.3) 136.0 (5.5) 132.4 (3.4) 30.4 (6.8)
60 s 151.2 (5.6) 124.5 (10.2) 135.8 (7.0) 129.0 (4.2) 136.0 (5.7) 131.7 (3.4) 24.5 (6.3)
0.6 (0.4) 63.2 (23.9) 6.8 (1.3) 1.9 (0.5) 1.8 (0.2) 2.9 (0.7) 17.2 (2.0)
Retention (ng Tinopal OB per mm2 leaf area) 0.20 (0.15) 0.28 (0.08) 0.18 (0.03) 0.82 (0.25) 0.57 (0.14) 0.40 (0.12) 0.95 (0.22)
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Leaf coverage (%) 0.96 (1.04) 4.49 (1.05) 2.23 (0.74) 5.31 (2.19 5.34 (1.52) 2.97 (0.74) 13.70 (4.27)
Page 33 of 40
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Figure 1 static surface tension (mN m-1) 72.3
surface tension (mN m-1)
70
29.3
60
48.0
50
46.0
40
38.0 32.0
Water Tween 20 Tween 80 Span 20 Span 80 Trend 90 TEHP EW400
30
20
101
27.8
102
103
104
surface age (ms)
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Figure 2
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Figure 3
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Figure 4
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Figure 5
1.0
2
retention (ng Tinopal OB per mm leaf area)
1.2
0.8
0.6
Water Tween 20 Tween 80 Span 20 Span 80 Trend 90 TEHP EW400
0.4
0.2
0.0 30
40
50
60
70
80
DST at 94 ms surface age
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Figure 6
30
slopedose response
25
20
15
10 No Adjuvant Tween 20 Tween 80 Span 20 Span 80 TEHP
5
0 0
5
10
15 6
20
25
30
-1
FPXD * 10 (µg s )
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Journal of Agricultural and Food Chemistry
GRAPHICS FOR TABLE OF CONTENTS
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
85x48mm (150 x 150 DPI)
ACS Paragon Plus Environment
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