In Vitro Test for Effects of Surfactants and Formulations on

The effects of surfactants on water permeability of isolated astomatous cuticles from Citrus leaves were measured. Rates of water loss across cuticles...
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Chapter 3

In Vitro Test for Effects of Surfactants and Formulations on Permeability of Plant Cuticles

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U. Geyer and J. Schönherr Institut für Botanik und Mikrobiologie, Technische Universität München, Arcisstrasse 21, D-8000 München 2, Federal Republic of Germany The effects of surfactants on water permeability of i s o l a t e d astomatous c u t i c l e s from C i t r u s leaves were measured. Rates of water l o s s across c u t i c l e s were determined g r a v i m e t r i c a l l y p r i o r t o and a f t e r a p p l i c a t i o n o f surfactants using coverages ranging from 0.015 t o 25 g/m2. Sodium dodecylsulfate d i d not affect water permeability. Polyoxyethylene p-t-octylphenol and polyoxyethylene nonylphenol in the HLB range of 4 t o 16 increased water permeability by up t o 2.1 f o l d . Polyoxyethylene a l k y l e t h e r in the HLB range of 5 t o 13 increased water permeability by seven- t o e i g h t f o l d . The cationic surfactant dodecyltrimethylammonium c h l o r i d e (HLB 18.5) increased water permeability very e f f e c t i v e l y by up t o twentytwofold. Most formulations of p e s t i c i d e s contain surfactants as e m u l s i f i e r s and as wetting agents. I n a d d i t i o n , surfactants may a f f e c t the b i o l o g i c a l a c t i v i t y of the a c t i v e ingredient o f a f o r n u l a t i o n (1). This e f f e c t i s not w e l l understood (2). Better wetting and greater r e t e n t i o n may be responsible i n p a r t , but e f f e c t s on permeability of cuticles have a l s o been considered t o e x p l a i n improved h e r b i c i d a l a c t i v i t y i n the presence o f surfactants (3, 4 ) . Generally, permeation o f a solute molecule across a c u t i c u l a r membrane depends on the concentration of that molecule i n the membrane (which i s a f u n c t i o n of the concentration gradient i n the adjacent solutions and the p a r t i t i o n c o e f f i c i e n t ) and i t s m o b i l i t y (J> ,M. When analysing the e f f e c t s o f surfactants on penetration of a c t i v e ingredients i t i s therefore necessary t o i n v e s t i g a t e both the e f f e c t s o f surfactants on the concentration and on m o b i l i t y o f the solute i n the c u t i c l e . To date, systematic studies o f t h i s type do not appear t o have been conducted. Plant c u t i c l e s are l i p i d membranes. They have a high sorption capacity f o r l i p o p h i l i c solutes. Cutin i s the main sorbent (7, 8 ) . Transport resistance i s due t o soluble l i p i d s associated w i t h the c u t i n (9, 10, K e r l e r , F.; Schonherr, J . Arch. Environ. Contam. T o x i c o l . , i n press). The permeability of c u t i c l e s increases w i t h 0097-6156/88/0371-O022$O6.00/0 ° 1988 American Chemical Society

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

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increasing l i p i d s o l u b i l i t y o f the solutes. For solutes having the same s i z e (molar volume) permeability i s proportional t o the cuticle/water p a r t i t i o n c o e f f i c i e n t (11). Equilibrium d i s t r i b u t i o n o f a solute between the c u t i c l e and an aqueous s o l u t i o n i s g r e a t l y affected by surfactants when present i n concentrations above the c r i t i c a l m i c e l l e concentration (cmc) (11). L i p o p h i l i c solutes tend t o be s o l u b i l i z e d i n the m i c e l l e s and cuticle/water partition c o e f f i c i e n t s decrease rapidly with increasing surfactant concentration. As a consequence, t h e concentration o f a solute i n the c u t i c l e i s much lower i n presence of surfactants i n the aqueous solutions and the flow across the cuticle i s slowed i n proportion. Surfactant concentration increases during droplet drying. A c t i v e ingredients that d i d not enter t h e c u t i c l e during droplet drying w i l l eventually be dissolved i n pure hydrated surfactant o r formulation. In this simplest case, surfactants reduce rates o f penetration, because they reduce the d r i v i n g f o r c e , i . e . the concentration gradient o f t h e solute i n the c u t i c l e . I t i s important t o r e a l i z e that transport properties o f the c u t i c l e (that i s the m o b i l i t y o f the solute i n the c u t i c l e ) are not affected by the surfactant. I f permeability c o e f f i c i e n t s o r permeances were calculated using the correct driving force, namely t h e concentration gradient o f the solute i n the c u t i c l e , rather than the concentration gradient i n the adjacent bulk s o l u t i o n s , the c o e f f i c i e n t s would be independent o f t h e concentration o f the surfactants. Of course, permeation o f p o l a r solutes, which are not s o l u b i l i z e d i n surfactant m i c e l l e s , w i l l not be slowed, because t h e i r concentration gradient i n the c u t i c l e w i l l be unaffected by the presence o f surfactants i n s o l u t i o n . If permeability c o e f f i c i e n t s f o r solutes depend on t h e concentration o f surfactants, even though they were calculated using t h e concentration gradient i n t h e c u t i c l e , i t must be concluded that transport properties o f the c u t i c l e s were changed by the surfactants. The b a r r i e r l i m i t i n g transport across c u t i c l e s consists o f soluble l i p i d s associated w i t h the c u t i n ( c u t i c u l a r waxes). I f permeability i s increased by surfactants, i t i s l i k e l y that structure and/or composition o f soluble c u t i c u l a r l i p i d s have been a l t e r e d . These considerations show that surfactants can have two opposing e f f e c t s on the flow o f a chemical across the c u t i c l e : (1) They slow i t by decreasing the d r i v i n g f o r c e and (2) they may increase permeability by a l t e r i n g t h e properties o f the wax b a r r i e r . Both e f f e c t s a c t simultaneously and they depend on surfactant concentration and l i p o p h i l i c i t y o f solutes. I n simple experiments they cannot be separated and depending on experimental conditions and type o f solute, surfactants may enhance, depress o r have no e f f e c t on herbicide a c t i v i t y (1). I t f o l l o w s , that e f f e c t s of surfactants on permeation can only be understood i f the above e f f e c t s a r e studied separately. The t e s t we are presenting here measures e f f e c t s o f surfactants on the transport properties o f the b a r r i e r . The p a r t i t i o n c o e f f i c i e n t e f f e c t i s absent, because water permeability i s studied. The d r i v i n g force o f water across c u t i c l e s (the gradient o f water a c t i v i t y ) i s p r a c t i c a l l y unaffected by the presence o f surfactants. Soluble c u t i c u l a r l i p i d s are the l i m i t i n g b a r r i e r f o r water

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

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just as f o r solutes and a good c o r r e l a t i o n between water permeability and solute permeability o f c u t i c l e s has been reported (Schonherr, J . ; Riederer, M. Rev. Environ. Contam. T o x i c o l . , i n press). I t i s , therefore, meaningful t o study the e f f e c t s o f surfactants on transport properties o f c u t i c l e s by measuring the e f f e c t s o f surfactants on water permeability.

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Materials and Methods The astomatous adaxial l e a f c u t i c l e s from healthy and vigorously growing C i t r u s aurantiun L. trees were used. I n one experiment the astomatous c u t i c l e s from commercially supplied green pepper f r u i t s (Capsicum annuum L.) were used. The c u t i c l e s were i s o l g t e d enzymatically (12), a i r d r i e d and stored i n the r e f r i g e r a t o r (4 C) f o r f u r t h e r use. These i s o l a t e d c u t i c l e s w i l l be r e f e r r e d t o as c u t i c u l a r membranes (CM). Mature leaves were taken from |rees grown i n growth chambers (16 h l i g h t a t 500 t o 800 uE m s PAR, 25° C, 50 % r e l a t i v e humidity; 15° C and 9o % r e l a t i v e humidity during the dark period). Leaves were never treated w i t h any p e s t i c i d e t o avoid contact w i t h surfactants and/or formulations p r i o r t o experimentation. Table I . Surfactants used f o r experimentation Trade name BRU 52 BRIJ 30 BRU 56 BRIJ 58 BRIJ 35 RENEX 36 TRITON X-15 TRITON X-35 TRITON X-45 TRITON X-100 TRITON N-57 TRITON N-101

chemical name POE c e t y l ether POE l a u r y l ether POE c e t y l ether POE c e t y l ether POE l a u r y l ether POE t r i d e c y l ether POE p-t-octylphenol POE p-t-octylphenol POE p-t-octylphenol POE p-t-octylphenol POE nonylphenol POE nonylphenol Na-dodecylsulfate Dodecyl trimethyl anmonium c h l o r i d e

HLB

EO 1 3 9 20 20 6 1 3 5 9-10 5 9-10

-

5.2 9.8 12.9 15.8 16.9 11.6 3.6 7.8 10.4 13.5 10.0 13.5 40.0 18.5

Surfactants were purchased from Serva (Heidelberg, FRG) and were used without f u r t h e r p u r i f i c a t i o n . They are l i s t e d i n Table I . The ethylene oxide contents (EO) are averages. The hydrophile l i p o p h i l e balance (HLB) f i g u r e s were taken from the l i t e r a t u r e (13, 14). The t e s t procedure i s very simple. Water permeability of each c u t i c u l a r membrane i s measured g r a v i m e t r i c a l l y (15) p r i o r t o and a f t e r a p p l i c a t i o n o f predetermined amounts o f surfactant. The t r a n s p i r a t i o n chambers depicted i n Figure 1 were used. They are made o f brass and are f i t t e d w i t h a rubber 0-ring t o a t t a i n a good s e a l . Each chamber i s f i l l e d w i t h 0.5 ml deionized water and a CM i s positioned on top o f i t , the morphological inner side f a c i n g the —

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

Permeability of Plant Cuticles

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GEYER AND SCHONHERR

Figure 1: Drawing o f a brass chamber used i n the t e s t .

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

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water. The brass r i n g i s coated l i g h t l y w i t h h i g h vacuum s i l i c o n grease on the surface f a c i n g the CM (to minimize creeping o f surfactant s o l u t i o n between c u t i c l e and metal r i n g ) and i s secured w i t h w i t h 3 screws. These chambers are then inverted and placed i n a desiccator h a l f f i l l e d w i t h d r i e d s i l i c a g e l . To prevent damaging the c u t i c u l a r membranes a coarse metal screen was positioned between the s i l i c a g e l and chambers. The desiccators were kept a t 24.5 t o 25.5 C and the water l o s s from the chambers was followed by p e r i o d i c a l l y weighing them u n t i l about 10 t o 20 mg o f water had been l o s t . Surfactants were dissolved i n deionized water and 50 p i o f these t e s t solutions were applied t o the outer surfaces o f the c u t i c l e s a f t e r p l a c i n g the chambers up r i g h t . The desiccators were closed and a f t e r the water had evaporated, the chambers were inverted again and weighing was resumed as before. A Satorius 1702 MP8 e l e c t r o n i c balance (0.1 mg accuracy) o n l i n e w i t h an O l i v e t t i M24-SP computer was used. At the end o f an experiment the rates o f water l o s s p r i o r t o and a f t e r treatment w i t h surfactant were determined by l i n e a r regression a n a l y s i s . The e f f e c t o f the treatment was judged from the r a t i o o f the slopes a f t e r and before treatment. The r a t i o i s u n i t y i n case o f an i n e f f e c t i v e surfactant and i t i s greater than u n i t y i f water permeability was increased. For each surfactant and coverage 12 t o 15 membranes were used as r e p l i c a t e s . Data are reported as means together w i t h a 95 % confidence i n t e r v a l (p = 95 Z ) . During the second weighing period, the outer surfaces o f the CM were coated w i t h a t h i n l a y e r o f surfactant, rather than w i t h an aqueous s o l u t i o n o f the surfactant. This was intended t o simulate the s i t u a t i o n i n the f i e l d , a f t e r the water o f the spray has evaporated. Initially, a l l surfactants were tested using a r e l a t i v e l y h i g h coverage (mass per area o f 5 t o 25 g/m ) o f surfactant i n order t o screen out the most e f f e c t i v e ones. Later some o f the surfactants were tested using a wide range o f surface coverages (0.015 t o 25 g/m ). During the drying o f the t e s t solutions the surfactant contained i n the droplets were not deposited q u a n t i t a t i v e l y on the surfaces o f the c u t i c l e s as explained below. The y i e l d o f deposition was determined using (phenyl-3H(N))-labelled T r i t o n X100 (NEN, s p e c i f i c a c t i v i t y 48.1 MBq/nfc). A 50 p i droplet containing l a b e l l e d T r i t o n X-100 was placed on each o f 30 CM mounted as usual on top o f the chambers. A f t e r the droplets had d r i e d i n the desiccator the area o f the c u t i c l e s exposed t o the solutions was excised and the r a d i o a c t i v i t y was determined by l i q u i d s c i n t i l l a t i o n counting. Recovery was 46.2 Z (standard d e v i a t i o n 8.5 Z) and 53.4 Z (standard d e v i a t i o n 14.8 Z) f o r t h e o r e t i c a l coverages o f 5 and 10 g/m , r e s p e c t i v e l y . The average recovery f o r both coverages was 49 Z (standard d e v i a t i o n 11 Z). The e f f e c t i v e surface coverages were c a l c u l a t e d from the t h e o r e t i c a l values assuming that only 49 Z were deposited on the surfaces o f the c u t i c u l a r membranes. The remaining 51 Z o f r a d i o a c t i v i t y were probably deposited on the surfaces o f the top metal r i n g s used t o prevent spreading o f the droplets. Some may a l s o have been l o s t due to l a t e r a l d i f f u s i o n between r i n g and c u t i c l e . Since a l l t e s t solutions were applied a t concentrations f a r above the cmc and since the concentration e f f e c t on recovery was small i t was assumed

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

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that wetting o f and sorption on the metal r i n g s (and thus recovery) would be the same (within experimental error) f o r a l l surfactants and concentrations.

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Results I n Figure 2 t y p i c a l r e s u l t s obtained w i t h a c o n t r o l (A) and w i t h a treated c u t i c u l a r membrane (B) are shown. The c o n t r o l membrane was treated w i t h 50 p i water, whereas the CM i n Figure 2 B was treated w i t h gn aqueous Renex 36 s o l u t i o n a t a concentration equivalent t o 5 g/m . Slopes 1 and 2 o f the c o n t r o l membrane do not d i f f e r s i g n i f i c a n t l y , as t h e 95 % confidence i n t e r v a l s o f the slopes overlap. I n experiments w i t h fewer data points than shown i n Figure 2 confidence i n t e r v a l s are l a r g e r , such that slope r a t i o s ranging from 0.7 t o 1.3 are s t a t i s t i c a l l y not s i g n i f i c a n t l y d i f f e r e n t from u n i t y . Treatment w i t h Renex 36 r e s u l t e d i n a 7.4 f o l d increase i n water permeability, which i s s t a t i s t i c a l l y h i g h l y s i g n i f i c a n t (p > 99.9 % ) . Surfactants from the T r i t o n s e r i e s had a very small e f f e c t on water permeability o f CitruSpCM (Figure 3 ) , even a t the rather h i g h surface coverage o f 15.5 g/m . The e f f e c t s o f T r i t o n surfactants on water permeability ranged from 1.6 t o 2.1 and there were no s i g n i f i c a n t (p = 95Z) differences between d i f f e r e n t types o f T r i t o n surfactants. The e f f e c t o f the surface coverage on water permeability was studied using T r i t o n N-101 and T r i t o n X-35 and was found t o be rather small (Figure 4 ) . A very h i g h increase i n water permeability by about a f a c t o r of seven was observed w i t h B r i j 52, B r i j 30 and B r i j 56, while the other two members o f the s e r i e s w i t h HLB values around 16 t o 17 had very l i t t l e e f f e c t (Figure 3 ) . Note that the surface coverage was only 5 g/m , which i s about 1/3 that used w i t h the T r i t o n s e r i e s . Renex 36 increased water permeability very e f f e c t i v e l y . A small, but s t a t i s t i c a l l y s i g n i f i c a n t increase i n water permeability was observed even a t very low coverages o f 15 mg/m (Figure 4 ) . An e f f e c t comparable t o that observed w i t h Renex 36 and the more e f f e c t i v e members o f t h e B r i j s e r i e s was found f o r the c a t i o n i c surfactant dodecyltrimethylammonium c h l o r i d e , whereas the anionic surfactant sodium dodecylsulfate was i n e f f e c t i v e and even reduced water permeability a t higher surface coverages (Figure 4 ) . The e f f e c t o f Renex 36 on water permeability o f green pepper f r u i t CM was much smaller than the e f f e c t observed w i t h C i t r u s CM. At a coverage o f 1.5 g/m water permeability o f pepper CM was only increased by a f a c t o r o f 1.4 (confidence i n t e r v a l 1.3-1.5), whereas w i t h C i t r u s a 3.5 f o l d increase was observed a t the same coverage (Figure 4 ) . Renex 36 increased water permeability o f C i t r u s polymer matrix membranes (CM from which soluble l i p i d s wgre removed w i t h chloroform). A t a surface coverage o f 2.4 g/m an increase by a f a c t o r o f 2.0 (confidence i n t e r v a l 1.8 - 2.1) was observed. A t t h i s coverage the water permeability o f CM would have been increased by a f a c t o r o f about 4.2 (Figure 4 ) .

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

PESTICIDE FORMULATIONS: INNOVATIONS AND DEVELOPMENTS

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TIME

Figure 2: T y p i c a l examples o f computer printouts (redrawn) from a c o n t r o l experiment (A) and a c u t i c l e treated w i t h Renex 36 (B). Arrows i n d i c a t e time o f treatment. The slopes have the dimension g/min.

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

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i

1

1

i

i

0

2

U

6

8 10 HLB

i

i

12

29

i

i

1

U

16

18

Figure 3: The e f f e c t s o f T r i t o n (X o r N) and B r i j surfactants on water permeability o f C i t r u s c u t i c u l a r membranes. The coverage was 15.5 g nf and 5 g m f o r the T r i t o n and B r i j surfactants, respectively. HLB values are given i n parentheses. The e f f e c t i s given as t h e r a t i o o f t h e permeances (F) a f t e r and p r i o r t o treatment. Bars represent h a l f a confidence i n t e r v a l (p = 95 1).

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

PESTICIDE FORMULATIONS: INNOVATIONS AND DEVELOPMENTS

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Figure 4: The e f f e c t o f coverage (mass per area) o f selected surfactants on water permeability o f C i t r u s c u t i c u l a r membranes. Bars represent the confidence i n t e r v a l s (p = 95 Z). The e f f e c t i s given as the r a t i o o f the permeances (P) a f t e r and p r i o r t o treatment.

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

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Discussion The gravimetric method of measuring water permeability i s simple and inexpensive. The t e s t i s very s e n s i t i v e , because i t uses the method o f paired observations. Each membrane serves as c o n t r o l and as treatment and b i o l o g i c a l v a r i a b i l i t y o f water permeability o f CM i s thus eliminated. Furthermore, there was no c o r r e l a t i o n between the e f f e c t o f a surfactant and the water permeability o f the CM before treatment. The s e n s i t i v i t y o f the t e s t can be adjusted a p r i o r i t o t h e needs of the experimenter by using the appropriate number o f data points. There i s a l i m i t t o t h i s , however, because the t o t a l water l o s s from a chamber during the experiment should not exceed 50 tqg. The l o s s o f water i s accompanied by a decrease i n pressure i n t h e chamber. The CM assumes a concave curvature and could rapture. When the gravimetric method was introduced (15), chambers made of p l e x i g l a s s were used. These had a small but f i n i t e water permeability, such that t o t a l water l o s s from the chambers was the sum o f two p a r a l l e l flows, namely across the c u t i c l e s and across the w a l l s o f t h e chambers. The w a l l s o f the brass chambers are impermeable t o water and t h e permeance o f a membrane i s e a s i l y calculated from the slope (g/nrin), the membrane area (7.85 x 10" m ) and t h e d r i v i n g force. The gradient o f water a c t i v i t y i s p r a c t i c a l l y u n i t y , because t h e a c t i v i t y o f pure water i n the chamber i s 1 and the a c t i v i t y over d r i e d s i l i c a g e l i s p r a c t i c a l l y zero. The permeance (P) i s therefore P = slope/ (area x d r i v i n g force) (1) 2 This permeance has the dimension g/min m which can be converted t o the usual u n i t s (m/s) by d i v i d i n g by the s p e c i f i c g r a v i t y o f l i q u i d water and by 60 t o obtain seconds instead o f minutes. Since area and d r i v i n g f o r c e a r e the same before and a f t e r treatment, they cancel and the e f f e c t of a surfactant on permeance ( i . e . the r a t i o of t h e permeance o f the CM treated w i t h surfactant over the permeance p r i o r t o treatment; P /P) i s numerically i d e n t i c a l t o the r a t i o o f the slopes a f t e r aSSFbefore treatment (Figures 3 and 4). There i s no clear-cut dependence o f water permeability on e i t h e r HLB o r surfactant structure. Maximum e f f e c t s were found i n the HLB range 5 t o 13 ( B r i j 52, B r i j 30, B r i j 56, Renex 36). The nonionic surfactants w i t h HLB values above 13 have l i t t l e e f f e c t , but the c a t i o n i c surfactant dodecyltoimethylanmonium c h l o r i d e which has a HLB o f 18.5 very e f f e c t i v e l y increases water permeability. The anionic surfactant sodium dodecylsulfate (HLB about 40) d i d not increase water permeability. The t e s t was designed t o measure the e f f e c t s o f surfactants on water permeability o f c u t i c l e s rather than t o r e v e a l the cause(s) of effectiveness o r ineffectiveness. At t h i s p o i n t , we can only speculate. The b a r r i e r that i s r a t e l i m i t i n g i n both transport o f water and solutes across c u t i c l e s i s made up o f soluble c u t i c u l a r l i p i d s , probably i n a s s o c i a t i o n w i t h c u t i n (10, 11, 160. E x t r a c t i n g soluble c u t i c u l a r l i p i d s w i t h chloroform increases permeability of C i t r u s CM much more than that of pepper f r u i t CM (16). Water permeability

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

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PESTICIDE FORMULATIONS: INNOVATIONS AND DEVELOPMENTS

of C i t r u s CM i s much more affected by Renex 36 than permeability of pepper f r u i t CM i n d i c a t i n g that surfactants i n t e r a c t w i t h the soluble c u t i c u l a r l i p i d s , leading t o an increased m o b i l i t y of water i n the c u t i c l e . Surfactants a l s o i n t e r a c t w i t h the c u t i n , because water permeability of polymer matrix membranes (free of soluble c u t i c u l a r l i p i d s ) was a l s o increased by Renex 36, even though t o a lower extent than permeability of CM. There are b a s i c a l l y two ways, how water permeability of c u t i c l e s could be increased by surfactants. They could swell the polymer matrix and they may s o l u b i l i z e c u t i c u l a r waxes. Swelling of the polymer matrix would increase the water content of c u t i c l e s . As a consequence of s w e l l i n g , the d i f f u s i o n c o e f f i c i e n t of water i n the c u t i c l e might be increased. Both e f f e c t s could e x p l a i n the increase i n water permeability of polymer matrix membranes. Swelling of the polymer matrix of c u t i c u l a r membranes could lead t o defects between wax c r y s t a l l i t e s and thus increase permeability. Surfactants may a l s o p a r t i a l l y s o l u b i l i z e c u t i c u l a r waxes. These hypotheses are currenty under i n v e s t i g a t i o n . F a i r l y h i g h coverages have been used i n most of our screening t e s t s . The C i t r u s CM used had a mass per area of about 2.5 g/m and the soluble c u t i c u l a r l i p i d s amount t o only about 0.1 g/m , which i s 4 Z by weight (17). Only Renex 36 was tested a t coverages equivalent t o the amounts o f soluble c u t i c u l a r l i p i d s (Figure 4 ) . A l l other surfactants were tested using coverages i n excess of the amounts of soluble c u t i c u l a r l i p i d s . This appears t o be necessary f o r large e f f e c t s on water permeability. Sodium dodecylsulfate a c t u a l l y decreased water permeability when applied a t high surface coverages. This surfactant i s i n the s o l i d s t a t e a t 25 C. At a coverage of 25 g/m the l a y e r of surfactant on top of the CM was 10 times t h i c k e r than the c u t i c l e i t s e l f and i t probably acted as resistance i n s e r i e s . Even though i t i s not c l e a r how surfactants increase water permeability of c u t i c l e s , i t i s a f a c t that some of them s i g n i f i c a n t l y do so. Since soluble c u t i c u l a r l i p i d s are the main barrier not only f o r water, but a l s o f o r solutes, solute permeability i s most l i k e l y increased by surfactants that increase water permeability (Schonherr, J . ; Riederer, M. Rev. Environ. Contam. T o x i c o l , i n press). However, as pointed out e a r l i e r , w i t h l i p o p h i l i c solutes t h i s e f f e c t w i l l be confounded w i t h the e f f e c t of surfactants on the p a r t i t i o n c o e f f i c i e n t . Both e f f e c t s act i n opposite d i r e c t i o n . The p a r t i t i o n i n g e f f e c t w i l l decrease permeability, whereas an increase i n m o b i l i t y of solutes i n the c u t i c l e w i l l increase the permeability. I n an experiment comparing the uptake of a p e s t i c i d e w i t h and without a surfactant (or a formulation) the two e f f e c t s could cancel and i t would be concluded that the surfactant had no e f f e c t on the c u t i c l e . The advantage of our t e s t i s , that when measuring water permeability the p a r t i t i o n i n g e f f e c t i s absent and the e f f e c t of surfactants on m o b i l i t y of water (and solutes) can be measured unobscured by other e f f e c t s . The t e s t may a l s o be used f o r mixtures of surfactants, complete formulations containing solvents or f o r other adjuvants. Surfactants that increase water permeability of c u t i c l e s , w i l l probably also increase permeability f o r surfactants. Since

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

3.

GEYER A N D SCHONHERR

Permeability of Plant Cuticles

33

surfactants a r e t o x i c t o c e l l s (18) they can increase t o x i c i t y o f herbicides applied t o the f o l i a g e . Acknowledgment This work was supported by a grant from the Deutsche Forschungsgemeinschaft. L i t e r a t u r e Cited 1.

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2. 3. 4. 5. 6. 7. 8. 9. 10. 11.

12. 13. 14. 15. 16. 17. 18.

Foy, C.I.;Smith, L. W. I n P e s t i c i d e Formulations Research; Gould, R.F. Ed.; Adv. Chem. Ser. 89, p 55, American Chemical Society: Washington, 1969 Bukovac, M.J. I n Herbicides; Audus, L . J . , Ed.; Academic: London, 1976; V o l 1, p 335 Johnstone, D.R. I n P e s t i c i d e Formulations: Valkenburg, W. van, Ed.; Dekker: New York, 1973, p 344 Turner, D.J.P e s t i c . Sci. 1972, 3, 323 Crank, J. The Mathematics of D i f f u s i o n ; Clarendon: Oxford 1975 Hartley, G. S.; Graham-Bryce, I. J. Physical P r i n c i p l e s of P e s t i c i d e Behaviour; Academic: London, 1980 Riederer, M.; Schönherr, J. Ecotoxicol. Environ. Safety, 1984, 8, 236 Riederer, M,; Schönherr, J. Planta, 1986, 169, 69 Schönherr, J. Planta, 1976, 131, 159 Schönherr, J. I n P h y s i o l o g i c a l Plant Ecology II; Lange, O. L.; Nobel, P. S.; Osmond, C.B.; Z i e g l e r , H., Eds.; Springer: B e r l i n , 1982, p 153 K e r l e r , F. Quantitative Bestimmung und Analyse von Sorptions und Transportparametern für l i p o p h i l e organische Verbindungen. Doct. Diss. Technische Universität München, FRG 1986 Schönherr,J.;Riederer, M. Plant Cell Environ. 1986, 9, 459 Becher, P. I n P e s t i c i d e Formulations; Valkenburg W. van, Ed.; Dekker: New York, 1973; p 65 G r i f f i n , W. C. J. Soc. Cosmetic Chemists 1954, 5, 249 Schönherr,J.;Lendzian, K. Z. Pflanzenphysiol. 1981, 102 321 Riederer, M.; Schönherr, J. E c o t o x i c o l . Environ. Safety 1985, 9, 196 Haas K,; Schönherr J. Planta 1976, 146, 399 P a r r , J. F.; Norman, A. G. Bot. Gaz. 1965, 126,86

RECEIVED December 28, 1987

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