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The factors enhancing or constraining foliar uptake of herbicides ... coefficient values of surfactant solution droplets on leaf or .... 0*5. % SURFAC...
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Chapter 7

Effects of Surfactants on Droplet Spreading and Drying Rates in Relation to Foliar Uptake 1

J. A. Zabkiewicz, D. Coupland , and F. Ede

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Forest Research Institute, Rotorua, New Zealand

Various non-ionic organosilicone and organic surfactant solutions were compared by means o f droplet contact angle, spread area and drying time measurements. Several organosilicone surfactant solutions had leaf wetting and spreading c a p a b i l i t i e s f a r superior to the organic surfactant solutions. Surfactants were characterised further by their influence on the uptake of 14C-2-deoxyglucose i n t o bean, eucalypt and C i t r u s f o l i a g e . Obvious plant species differences e x i s t that could not be completely overcome by the surfactants tested. Similar rates of f o l i a r uptake of the deoxyglucose were found with selected organosilicone and organic surfactants. The organosilicone solution properties were such that both c u t i c u l a r penetration and stomatal flooding were possible. This may be of value i n the field with "difficult" plant species or adverse spraying conditions.

The factors enhancing or constraining f o l i a r uptake of herbicides have been investigated and reviewed many times (1-5), with much emphasis on the nature of the leaf surface and the e f f e c t s of spray additives (6-9). There has a l s o been a recognition that some spray formulation properties may be s e l f - c o n f l i e t i n g , e.g. retention and coverage (7); rapid uptake and phytotoxicity (10, 11); uptake and translocation (12). The incorporation of a suitable surfactant into a spray formulation i s generally e s s e n t i a l . However, the large number of candidate surfactants and their varied behaviour has not made their evaluation easy. Of the physical tests available, only the wetting, contact angle and spreading c o e f f i c i e n t values of surfactant solution droplets on leaf or iCurrent address: Long Ashton Research Station, Bristol, BS18 9AF, England 0097-6156/88AB71-0077$06.00/0 ° 1988 American Chemical Society

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

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a r t i f i c i a l surfaces have been deemed useful (13, 14). Pesticide uptake studies have not provided s u f f i c i e n t l y consistent data to enable useful correlations to be made between penetration rates and the various physical and chemical properties of surfactants (2, 15). However, there are clearer trends with the various plant factors which influence pesticide uptake, such as c u t i c l e thickness and leaf morphology (16-18). In the case of " d i f f i c u l t " plants, with i r r e g u l a r or pubescent surfaces or thick c u t i c l e s , the addition of suitable surfactants to spray solutions i s essential so that the droplets can contact the true leaf surface ( i . e . the epidermis) and allow penetration of the active ingredient through the c u t i c l e . Such spray formulations need to have low surface tensions, but because most solutions have surface tensions rarely below 30 mN m" , they f a i l to be f u l l y e f f e c t i v e . Such was the s i t u a t i o n with the sprays used for the control of gorse (Ulex europaeus), a thorny, woody shrub of the legume family. Extensive screening of candidate surfactants by physical methods, and uptake of C - l a b e l l e d herbicides i n t o the p l a n t , led to the choice of an organosilicone block co-polymer surfactant as the most suitable adjuvant for several commercial herbicides (19). Improved gorse control i n the f i e l d was also demonstrated but the reason for t h i s enhanced h e r b i c i d a l a c t i v i t y on addition of Silwet L-77 surfactant was not known. Gorse i s too d i f f i c u l t a plant to use for fundamental studies, therefore other species (bean, eucalypt and Citrus) were used instead. To avoid physiological interactions caused by the active ingredient e.g. contact phytotoxicity, a non-phytotoxic r a d i o l a b e l e d compound was used for the f o l i a r uptake studies. The compound chosen had to be water soluble (no further formulation needed); non-ionic (no p o s s i b i l i t y of i n t e r a c t i o n with i o n i c surfactants); metabolically stable and available at s u f f i c i e n t l y high s p e c i f i c a c t i v i t y for low concentration use. This present work describes the effects of three organosilicone surfactants on droplet contact angle, spreading and drying rates, and compares them to two organic surfactants. These aqueous solutions were also tested on leaves of several plant species to determine their influence on the uptake of an "inert" r a d i o l a b e l e d compound (2-deoxyglucose).

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Materials and Methods Plant m a t e r i a l . Bean plants ( V i c l a faba v a r . Evergreen) were grown from seed i n a 3:1 peat:pumice mixture i n a glasshouse. Eucalyptus plants (Eucalyptus botrvoldes) were grown from seed outdoors then at approx. one year of age potted i n t o 10 1 of sandy-loam s o i l . Plants were used approx. four months later when they were 1-1.4 m t a l l with 5-10 side branches. Mandarin plants (Citrus n o b l l l s v a r . Unshin, S i l v e r h i l l s t r a i n ) were obtained from a commercial nursery when they were approx. two years o l d . The scions shared a common parent source and were grafted onto a t r i f o l i a t e rootstock. A l l plants were brought into the growth room for preconditioning p r i o r to treatment. In a l l experiments the leaves used were f u l l y expanded and mature; with bean, the youngest, fully-developed bi-lobed leaves were treated. Unless specified otherwise a l l treatments were to

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

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the adaxial leaf surfaces and i n the growth room. Conditions : 8 h photoperiod; 20O/15OC day/night temperature; 70% r e l a t i v e humidity; l i g h t intensity 300-340 umol.s""! m~2.

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Surfactants. I n i t i a l l y a wide range of Union Carbide Silwet organosilicone surfactants was screened. The three chosen for further study were Silwet L-77, L-7607 and Y-6652 ( a l l s i l i c o n e polyalkyleneoxide copolymer v a r i a n t s ) . Organic surfactants used for comparison purposes were T r i t o n X-45 (Rohm and Haas; octylphenyloxyethylene product) and Agral (ICI; nonylphenyloxyethylene product, either 90% or 30% active ingredient). Contact angle. Leaf wax was obtained from leaves of field-grown plants by washing with chloroform (20 s ) . Solutions were d r i e d , f i l t e r e d and concentrated. Portions of the wax were redissolved i n chloroform (10 mg/ml) and a modified t i c applicator was used to apply 20 ;ul onto microscope glass s l i d e s to give an even coating of wax equivalent to 39 >ug/cm . Droplets (3>ul) of each test solution were applied with a microsyringe to the waxed surface of each s l i d e and the droplet's image was projected; the height and diameter were measured and the contact angle (CA) calculated (20). A l l determinations were made at 20°C and 55-65% rh with a minimum of 20 r e p l i c a t i o n s . 2

Droplet spread areas. Spread areas (SA) were measured on wax films on glass s l i d e s and on leaf surfaces using solutions containing surfactant (0.5% v/v) and Blankophore-P fluorescent dye (1% w/v; Bayer). Droplet sizes were 0.5yul; a l l treatments (maximum of 10 replicates) were carried out at 20°C and 55-65% rh under dim illumination to prevent any photo-degradation of the fluorescent i n d i c a t o r , when the droplets were dry, the spread areas were v i s u a l i s e d under uv l i g h t (360 run) and measured with an Optimax Image Analyser. Droplet drying. A Li-Cor 6000 portable photosynthesis porometer was used to measure droplet drying rates. The porometer included a Varsala humidity sensor and a chamber temperature thermistor, producing a continual readout for percentage r h , temperature and time. C i t r u s and eucalypt leaves were chosen for uniformity of growth and absence of surface blemishes. They were detached from the shoots and l e f t at 20°C,, 55-65% rh under dim illumination to e q u i l i b r a t e for 30 min. Bach leaf was used for only a single determination (6 r e p l i c a t e s ) . Droplets (4 x 0.5>ul) were applied either to wax films on microscope s l i d e s or to adaxial leaf surfaces. These were then placed inside the porometer chamber and readings of percentage rh and temperature taken at regular i n t e r v a l s . Vapour pressures were calculated (21) and a l i n e - f i t t i n g computer program was used to determine the actual time at which the drops were dry. A

C-2-deoxvglucose uptake. The 2-deoxy-D-[U- *C] glucose (14c-DOG; Amersham, UK) solutions (approx. 5 to 15 ng^ul) with surfactants (0.05% to 0.5%) were applied as four 0.5>ul droplets to

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

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equivalent regions of selected leaves on intact plants i n the growth room. At the end of the treatment period (6 h to 48 h) the treated leaf was excised and the treated leaf surface washed with at least 10 ml methanol:water (10:90 r a t i o for beans; 40:60 r a t i o for eucalypt and Citrus) to remove residual unabsorbed 14C-D0G. Aliquots (1 ml) of the washings were analysed for r a d i o a c t i v i t y ( i n 10 ml s c i n t i l l a n t s o l u t i o n ; 2:1 toluene:Triton X-100 plus 5.5 g/1 Permablend). The washed leaves were freeze-dried, ground, and portions oxidised using a Nicromat BF5010. A l l samples were radioassayed i n a Packard 4430 s c i n t i l l a t i o n counter (10 ml s c i n t i l l a n t s o l u t i o n :15% MeOH/toluene with 5.5 g/1 Permablend; plus 0.5 ml phenethylamine). Percentage uptake into the leaf was calculated from the r a d i o a c t i v i t y recovered. S t a t i s t i c a l treatments. Standard errors (SB) were calculated and least s i g n i f i c a n t differences (LSD) were determined where appropriate. The non-linear regressions (shown i n P i g . 2) were determined by an optimisation procedure using GENSTAT. The regression equation for wax f i l m r e s u l t s was found to be y = 319.917 x -0.39086 2 0.86); for leaf surface data $ = 460.743 x -0.47715 ( 2 = 0.82). In each case y i s time (seconds) and x i s area (mm ). ( R

=

R

2

Results Contact angle measurements were used as an i n i t i a l screening of surfactant solutions at different concentrations. Bach solution showed s i m i l a r behaviour on wax films regardless of the plant source (Figure 1). Overall they could be grouped into three categories. These were: solutions that caused t o t a l wetting ( l i k e Silwet L-77); those that gave adequate wetting ( l i k e T r i t o n X-45 or Silwet L-7607); and those that had high CA values i n d i c a t i n g poor wetting (values of 80o or more, not i l l u s t r a t e d ) . Spread areas are presented i n Table I . The organic surfactant solutions had s i m i l a r (and low) SA values on both wax films and leaf surfaces. In contrast Silwet solution SA values were generally greater on leaves than on wax films. The largest difference was seen with eucalypt. when viewed under the SEM, bean leaves had l i t t l e e p i c u t i c u l a r wax; C i t r u s had larger quantities but with an even surface, while eucalypt had a dense coating of wax platelets. The drying times of droplets of the same solution were tested on C i t r u s leaf and wax f i l m surfaces. The results (Table II) show that the solutions with the largest SA values also dried the fastest (90 vs 299 sees for Silwet L-77 and water on wax films) and the same trends were observed on leaf surfaces (127 vs 322 sees for Silwet L-77 and water). Drying times on leaf surfaces were longer i n a l l cases except for Silwet Y-6652 for unknown reasons.

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

Droplet Spreading and Drying Rates

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ZABKIEWICZ ET AL.

i

i

•01

'02

i

i

»03 -04

i -05 % SURFACTANT

^

i

i

0*1 CONCENTRATION

H

i

i

0*5

Figure 1. Contact angle v a r i a t i o n of surfactant s o l u t i o n s (3.0 pi droplets) on bean, eucalypt and C i t r u s wax f i l m s

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988. 2

Species BEAM EUCALYPT Solution Film Leaf Film Leaf water 1.0(0.1) 2.8(0.2) 1.4(0.1) 1.6(0.1) 0.5% Agral* 2.6(0.1) 3.1(0.2) 2.1(0.1) 2.7(0.1) 0.5% T r i t o n X-45 3.0(0.1) 4.3(0.1) 2.5(0.1) 3.7(0.1) 0.5% Silwet L-7607 3.6(0.1) 3.9(0.3) 2.9(0.1) 16.6(0.3) 0.5% Silwet Y-6652 25.4(2.3) 23.4(5.2) 11.7(0.2) 19.4(0.3) 0.5% Silwet L-77 89.2(3.7) 79.6(11.7) 16.5(0.6) 146.9(1.9) SE i n brackets *Agral 90 for bean; Agral LN (30% active) for eucalypt and Citrus

CITRUS Film Leaf 1.3(0.1) 1.8(0.1) 3.0(0.1) 3.3(0.1) 3.1(0.1) 4.1(0.1) 4.1(0.1) 5.8(0.4) 7.6(0.2) 8.6(0.1) 12.2(0.7) 50.8(4.5)

TABLE I . Comparison of droplet (0.5 jul) spread area ( i n ram ) on wax films and leaf surfaces

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TABLE I I . Droplet (0.5 Ail) drying times on C i t r u s leaf and wax f i l m surfaces Drying time (seconds) Leaf Film 322(23.7) 299( 7.5) 305(11.5) 232( 5.8) 261( 9.5) 215( 8.0) 202(11.5) 187( 6.4) 119( 2.4) 134( 4.9) 127( 4.1) 90( 2.7)

Solution Water 0.5% Agral LN 0.5% T r i t o n X-45 0.5% Silwet L-7607 0.5% Silwet Y-6652 0.5% Silwet L-77 SB i n brackets

The percentage uptake of Hc-DOG i n t o leaves of the three species over a 48 h period varied markedly (Table I I I ) . There was nearly complete uptake into bean from a l l solutions (even water alone), v a r i a b l e uptake into eucalypt, and much reduced uptake o v e r a l l into C i t r u s f o l i a g e . Though only the data for 0.5% surfactant solutions are shown i n Table I I I , the same r e l a t i v e behaviour was noted for a l l the surfactants over the range of concentrations from 0.05% to 0.5%. Reduced uptake was evident with lower surfactant concentrations (data not presented).

TABLE I I I . Uptake of 14C-D0G i n t o foliage over a 48 h period

Solution Water +0.5% Agral 90 +0.5% T r i t o n X-45 +0.5% Silwet L-7607 +0.5% Silwet Y-6652 +0.5% Silwet L-77

Bean 98.7(0.1) 99.4(0.1) 99.5(0.1) 99.5(0.2) 99.7(0.1) 99.9(0.1)

uptake (%) Eucalypt* 25.6(0.7) 98.4(0.1) 90.5(4.0) 90.8(1.6) 60.4(5.8) 37.4(2.5)

Citrus 16(1.4) 31(3.2) 32(4.7) 41(5.5) N/A 30(2.6)

3

N/A not available •Determined from 100(total a p p l i e d - l e a f r e s i d u e / t o t a l applied) The influence of the surfactant solutions was tested further on bean foliage over a reduced time period (6 h) and showed that the r e l a t i v e behaviour of the solutions was the same (Table I V ) . Under equivalent growing conditions highest uptake was shown from Silwet L-7607, T r i t o n X-45 and Agral 90 surfactant solutions, with lesser amounts from Silwet L-77 and Silwet Y-6652 solutions. At other times Silwet L-7607 effects were i n f e r i o r to those of Silwet L-77 (as shown i n column 3).

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TABLE IV. Uptake of

14

C-DOG into bean foliage over a 6 h period

uptake (%) Solution (3) (2) (U* Water 4.0(0.7) 18.5(3.2) 12.0(0.5) 0.5% Agral 90 48.7(1.5) N/A 62.9(5.6) 0.5% T r i t o n X-45 61.4(4.5) N/A 61.3(3.7) 0.5% Silwet L-7607 56.6(3.1) 57.6(6.2) 78.2(2.2) 43.6(5.5) 0.5% Silwet Y-6652 N/A 33.8(5.6) 77.2(2.7) 0.5% Silwet L-77 30.0(6.3) 44.4(5.2) SE i n brackets; (1) LSD (0.05)=11.15; (2) LSD (0.05)=11.7; (3) LSD (0.05)=11.02 N/A = not available •Determined from 100(total applied-leaf r e s i d u e / t o t a l applied) (1) and (2) treatments i n growth room; (3) treatment i n growth cabinet The p o s s i b i l i t y existed that uptake into leaves of low surface tension solutions, such as Silwet L-77 and Silwet Y-6652, could also be through flooding into open stomata. In eucalypt the adaxial surface i s astomatous, the abaxial surface has many stomata. Application of surfactant solution droplets to upper (adaxial) and lower (abaxial) eucalypt leaf surfaces gave the results shown i n Table V . TABLE V . Uptake of 14c-DOG into eucalypt leaf from adaxial and abaxial surfaces (over 48 h) treated with Silwet L-77 solutions uptake (%) Abaxial Solution Adaxial N/A Water 17.2(0.4) 41.1(1.5) 0.05% Silwet L-77 43.5(2.5) 47.3(4.2) 0.1% Silwet L-77 36.1(8.3) 43.2(2.2) 0.5% Silwet L-77 34.7(0.2) SE i n brackets: 0.05% L-77, LSD (0.05)=6.38; 0.1% L-77, (LSD 0.05)=17.07; 0.5% L-77, LSD (0.05)=6.2 There was an i n d i c a t i o n that Silwet L-77 solutions enhanced uptake when applied to abaxial surfaces. The test was repeated but over a much shorter period of time (2 minutes) before the applied solution droplets were washed o f f . An Agral 90 solution treatment was included for comparison (Table V I ) . 1

TABLE V I . Uptake of 4c-DOG into eucalypt leaf from adaxial and abaxial surfaces (after 2 min) treated with Agral 90 and Silwet L-77 solutions uptake (%) Solution 0.5% Silwet L-77 0.5% Agral 90

Adaxial 4.7(0.4) 0.5(2.3)

Abaxial 18.6(3.1) 1.4(2.3)

surfactant concentration •Determined from 100(total applied-leaf r e s i d u e / t o t a l applied)

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Only the 0.5% Silwet L-77 solution showed substantial uptake from the abaxial surface. None of the Agral solutions (at 0.05% to 0.5% cone, range) nor Silwet L-77 at 0.3% or less gave accelerated uptake (data not presented). This result suggests that there can be rapid flooding of leaf stomata by surfactant solutions and confirms v i s u a l observations of stomatal penetration by Silwet L-77 solutions (unpublished observations).

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Discussion There are a number of non-ionic organosilicone surfactants which can reduce solution surface tension very substantially and i t i s surprising that this c a p a b i l i t y has not been exploited further, as the performance of several such surfactants had been demonstrated over a decade e a r l i e r (22, 23). However, i n place of the f i e l d testing methods used to evaluate them then, measurements of formulation droplet behaviour were deemed to be a more p r a c t i c a l method i n t h i s wider-ranging, screening program. The four laboratory techniques described i n t h i s paper have been used for t h i s purpose on a wide range of organic and organosilicone surfactants. Contact angle (CA) measurement i s a simple means of ranking surfactants i n order of their solution wetting c a p a b i l i t y . It was known that surface roughness would reduce droplet contact angle (24), so the i n i t i a l screening of surfactants was for those having CA values substantially less than 80o on smooth wax f i l m s . This resulted i n the selection of several organosilicones which had excellent wetting properties (Figure 1). However, droplet spread and behaviour on plant surfaces are more relevant to agronomic s i t u a t i o n s . The magnitude of these effects cannot be measured nor predicted by CA determinations. The data i n Table I show that the three species chosen exhibited a wide range of leaf surface/surfactant interactive e f f e c t s . Comparing the effects on wax films and leaf surfaces, addition of surfactant gave minimal increase i n SA on bean leaves (having a very sparse e p i c u t i c u l a r wax); s i g n i f i c a n t l y larger increases (4-fold) were found with Citrus leaves (which have a continuous covering of smooth wax); and much larger increases with eucalypt (9-fold; the leaf surfaces having a "micro-rough" covering of dense wax p l a t e l e t s ) . It i s obvious that the more irregular the surface, the greater i s the degree of spreading, as was shown i n p a r t i c u l a r by the organosilicones. The expectation that greater SA values would lead to faster droplet drying was confirmed (Tables I and I I ) . A good c o r r e l a t i o n was also derived between spread area and drying time on wax films (Figure 2) for surfactant solutions that do not have very large enhancement of SA values on leaf surfaces. In the case of Silwet L-77 and Silwet ¥-6652 where there was proportionately greater spread area on the leaf surface, drying times were longer than expected. It i s known that these surfactants are hygroscopic and this property may be part of the reason for this behaviour (26). Greatest spreading occurred on eucalypt leaves, hence shortest droplet drying times and lowest uptake could be expected. This was not the case as shown by the uptake for 14c-DOG i n Table I I I . Lowest uptake (for a l l treatments) was by C i t r u s ; highest by bean, indicating that other plant or leaf c h a r a c t e r i s t i c s e.g. c u t i c l e

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

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Figure 2. Relationship between droplet (0.5 pi) drying time and spread area on C i t r u s leaf ( ) and wax f i l m ( )

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thickness were more dominant. Nor could greater amounts of 14c-D0G/deposit area be the sole c o n t r o l l i n g f a c t o r . A comparison of droplet spread areas, SA values r e l a t i v e to water, dose of DOG applied and percentage uptake for eucalypt leaves i s given i n Table V I I . Highest "dose" was with the pure water solution but t h i s gave the lowest uptake. However, within the surfactant s o l u t i o n series there appeared to be a trend that the larger the dose or amount/unit leaf area the larger the uptake. These results are i n agreement with previous findings (11, 25) that uptake may or may not depend on the concentration of surfactant and/or active used. TABLE V I I . Comparison of surfactant properties and influence on uptake of 1*C-D0G into eucalypt leaves (48 h) Solution

Vater 0.5% Agral 90 0.5% T r i t o n X-45 0.5% Silwet L-7607 0.5% Silwet Y-6652 0.5% Silwet L-77 * for 0.5 Ail droplet

Spread area* (mm2) 1.6 2.7 3.7 16.6 19.4 146.9

Spread area ratio 1 1.7 2.3 10.4 12.1 91.8

14C-D0G (ng/cm2) 245.0 110.3 38.9 8.1 7.3 2.0

% uptake

25.6 98.4 90.5 90.8 60.4 37.4

In the case of previous studies with gorse (19), Silwet L-77 surfactant (at 0.5% v/v) was best at enhancing uptake of glyphosate applied at "field" rates. In the present study, using "tracer" or "research" rates of h e r b i c i d a l l y inactive C-DOG, there was superior uptake at the same surfactant concentration by Silwet L-7607, Agral 90 and T r i t o n X-45 i n t o eucalypt leaves. On bean, there was a s i m i l a r trend, but at times Silwet L-77 was superior to these three surfactants (Table I V ) , suggesting that either plant or growing conditions can strongly influence f o l i a r uptake. One of the recognised problems with formulations i s that of contact phytotoxicity by the spray droplets, which may l i m i t the uptake and translocation of the active chemical (27-29). This may be due to either the t o x i c i t y of the adjuvant i t s e l f or to too rapid an uptake of the h e r b i c i d a l component. In the present t r i a l s the use of a non-herbicidal, r a d i o l a b e l e d chemical at low concentration prevented the l a t t e r p o s s i b i l i t y . It can also be argued that large spread areas would minimise the potential phytotoxicity from either surfactant or herbicide since the amount/unit leaf area would be less (by a factor of 10 at least i n the case of some of the Silwet products) and would reduce the l i k e l i h o o d of c e l l u l a r damage. The low surface tension of the Silwet solutions should also permit stomatal flooding. A substantial amount of information exists to support such a c a p a b i l i t y either on theoretical grounds (30) or by experimentation and observation (4, 31, 32). However, i n none of the previous studies i s there a report of stomatal flooding from small droplets applied to a leaf surface. In the present studies bean leaves placed on the surface of 0.5% Silwet L-77 solutions were i n f i l t r a t e d within seconds. Similar behaviour 14

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could be observed under the microscope with flooding of i n d i v i d u a l stomata when droplets were applied to the bean leaf surface. Studies with C-DOG and eucalypt leaves attempted to quantify this e f f e c t . A short-term (2 min.) uptake experiment (Table VI) demonstrated convincingly that there was enhanced uptake from the abaxial treatment. Thus, on the evidence a v a i l a b l e , 10-15% of r a d i o l a b e l e d material was taken up v i a the stomata. I f larger proportions were to be taken up into stomata from higher volume applications, then t h i s could be a s i g n i f i c a n t contribution to making the spray solution "rainfast" i n f i e l d s i t u a t i o n s . Such behaviour could be of considerable significance i n situations where "ideal" spraying conditions do not e x i s t . These c h a r a c t e r i s t i c s can a l s o explain the observed enhanced f i e l d efficacy when Silwet L-77 i s added to c e r t a i n herbicides. Namely, i t could be due to a combination of (1) the a b i l i t y of the spray s o l u t i o n to reach the true leaf surface; (b) further r e d i s t r i b u t i o n to stem, p e t i o l e e t c . which may be more r e a d i l y penetrated; and (c) uptake v i a stomata.

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Conclusions The Silwet organosilicone surfactants are a further c l a s s of non-ionic surfactants for use with p e s t i c i d a l formulations i n aqueous spray a p p l i c a t i o n s . Addition of low concentrations of these surfactants gives solutions good wetting and spreading properties on leaf surfaces. This i n turn enhances droplet drying. Several members of the Silwet organosilicone surfactant family have been characterised by these properties as well as by their influence on the uptake of l C-2-deoxyglucose into different p l a n t s . Obvious species differences exist as shown by the uptake of t h i s compound, which cannot be overcome e n t i r e l y by the surfactants tested to date. The Silwet solution c h a r a c t e r i s t i c s are such that i t i s possible to obtain stomatal penetration and t h i s may have implications for spray "rainfastness" properties i n f i e l d s i t u a t i o n s . 4

Acknowledgments We wish to thank S. Bodle, T . Faulds, C . Faulds, M. Godfrey and J . Hobbs for assistance with plant materials and growth room f a c i l i t i e s ; S.O. Hong with s t a t i s t i c s ; ICI and Rohm and Haas i n New Zealand for supplying samples of t h e i r surfactants; Union Carbide (USA) for samples of their surfactants and f i n a n c i a l support to DC and FB. Literature c i t e d 1. Hodgson, R . H . : Adjuvants for Herbicides; Weed Science Society of America: Champaign, Il, 1982. 2. P r i c e , C.E.: In Herbicides and Fungicides - Factors Affecting their A c t i v i t y ; McFarlane, N . R . , E d . ; Special Publication No. 29; The Chemical Society: London, England, 1976, pp. 42-66.

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.

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ZABKIEWICZ E T AL.

Droplet Spreading and Drying Rates

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3. Kirkwood, R . C . : In Herbicides and Fungicides - Factors Affecting their A c t i v i t y ; McFarlane, N . R . , E d . ; Special Publication No. 29; The Chemical Society: London, England, 1976; pp. 67-80. 4. Becher, P. and Becher, D . : In P e s t i c i d a l Formulations Research; Van Valkenburg, J.W., Ed; Advances i n Chemistry Series No. 86; American Chemical Society; Washington, DC, pp. 15-23. 5. Tadros, T . F . In Studies of Pesticide Transfer and Performance; Aspects of Applied Biology No. 14; Association of Applied B i o l o g i s t s ; Vellesbourne, England, 1987; pp. 1-22. 6. Dybing, C.D.; C u r r i e r , H . B . : Plant Physiology 1961, 169-174. 7. Furmidge, C.G.L.: J . S c i . Food A g r i c . 1959, 10, 267-273. 8. Baker, E.A.; Hunt, G . M . ; Stevens, P . J . G . P e s t i c . S c i . 1983, 14, 645-658. 9. Sands, R . ; Bachelard, E.P.: New Phytol. 1973, 72, 69-86. 10. Sutton, D . L . ; Foy, C.L.: Bot. Gaz. 1971, 132, 299-304. 11. M e r r i t t , C . R . : Ann. Appl. B i o l . 1982, 101, 517-525. 12. B r i a n , R . C . : P e s t i c . S c i . 1972, 3, 121-132. 13. Furmidge, C . G . L . : J . S c i . Food A g r i c . 1965, 16, 134-144. 14. Conibear, D.I.; Furmidge, C.G.L.: J . S c i . Food A g r i c . 1965, 16, 144-149. 15. Anderson, N . H . ; G i r l i n g , J.: P e s t i c . S c i . 1983, 14, 399-404. 16. Furmidge, C.G.L.: J . S c i . Food A g r i c . 1962, 13, 127-40. 17. P r i c e , C.E.: Anderson, N . H . : P e s t i c . S c i 1985, 16, 369-377. 18. Hess, F . D . ; Bayer, D.E.; F a l k . R . H . : Weed Science 1974, 22, 394-401. 19. Zabkiewicz, J.A.; Gaskin, R.E.; Balneaves, J.M.: In Symposium on Application and Biology; Southcombe, E.S.E., E d . ; BCPC Monograph No. 28; B r i t i s h Crop Protection Council; Croydon, England; 1985; pp. 127-134. 20. Fogg, G . E . Proc. Royal Soc. London 1947, Series B, 134, 503-522. 21. Monteith, J.L. In P r i n c i p l e s of Environmental Physics; Barrington, E . J . W . ; Willis, A.J., E d s . ; Edward Arnold; London, England, 1975 p. 172. 22. Jansen, L.L. Weed Science 1973, 21, 130-135. 23. Neumann, P . M . , P r i n z , R . : J . S c i . Food A g r i c . 1974, 25, 221-226. 24. Holloway, P . J . P e s t i c . S c i . 1970. 1, 156-163. 25. M e r r i t t , C . R . : Ann. Appl. B i o l . 1982, 101, 527-532. 26. Stevens, P.J.G.; Bukovac, M.J.: Proc. B r i t i s h Crop Protection Conf. 1985, pp. 309-316. 27. Parr, J.F.: In Adjuvants for Herbicides: Hodgson, R . H . , Ed.; Weed Science Society of America: Champaign, Il, 1982; pp. 93-114. 28. Midgley, S.J.: In Broad-Leaved Weeds and t h e i r Control i n Cereals; Aspects of Applied Biology No. 1; Association of Applied B i o l o g i s t s Wellesbourne, England; 1982, pp. 193-200. 29. Parr, J.F.; Norman, A.G.: Bot. Gaz. 1965, 126, 86-96. 30. Schonherr, J.; Bukovac, M.J.: Plant P h y s i o l . 1972, 49, 813-819. 31. Sands, R . ; Bachelard, E . P . New Phytol. 1973, 72, 87-99. 32. Dybing, C.D.; C u r r i e r , H.B. Weeds 1959, 7, 214-222. RECEIVED December 28, 1987

Cross and Scher; Pesticide Formulations ACS Symposium Series; American Chemical Society: Washington, DC, 1988.