Water and Solute Permeability of Plant Cuticles: Measurement and ...
Water and Solute Permeability of Plant Cuticles: Measurement and ...
Water and Solute Permeability of Plant Cuticles: Measurement and ...
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160 6 Diffusion <strong>of</strong> Non-Electrolytes<br />
penetration, it is not possible to manipulate the receiver. Donor concentrations can<br />
be adjusted <strong>and</strong> held constant, but the influx is measured by analysing the entire leaf<br />
after blotting or rinsing <strong>of</strong>f the donor solution. The entire leaf serves as receiver,<br />
<strong>and</strong> it is not known a priori where the solute is located. Depending on water <strong>and</strong><br />
lipid solubility it will be distributed in aqueous <strong>and</strong>/or lipid compartments, including<br />
cuticular wax <strong>and</strong> cutin. With intact leaves, permeances can be estimated from timecourse<br />
experiments, <strong>and</strong> using a desorption technique sorption compartments can<br />
be characterised. We will demonstrate this with barley leaves <strong>and</strong> conifer needles.<br />
Slender leaves as typical for conifer needles <strong>and</strong> some monocot species can be submerged<br />
in large volumes <strong>of</strong> donor solutions in glass test tubes. They are maintained<br />
at constant temperature, <strong>and</strong> are lightly agitated for mixing to minimise unstirred<br />
boundary layers.<br />
6.2.2.1 Penetration into Cut Edges<br />
Whenever leaves or needles are removed from the plants a wound is generated, <strong>and</strong><br />
solutes can penetrate into the wound. This necessitates corrections for solute penetration<br />
into the wound. Wounds may be closed by dipping into paraffin wax, grease,<br />
glue or other materials. In these cases, it must be established that the seal is effective<br />
<strong>and</strong> that the materials do not sorb solutes. With barley leaves <strong>and</strong> conifer needles we<br />
have used a different approach. The cut edge was dipped into a shallow (1 mm)<br />
aqueous solution <strong>of</strong> 14 C-labelled triadimenol (Kcw = 760), the vessels were closed<br />
to establish 100% humidity, <strong>and</strong> they were incubated in the dark to minimise transpiration.<br />
After 6 or 24 h the leaves were removed from the bath, the base was blotted<br />
dry, <strong>and</strong> leaves were dissected in 1 mm-wide strips. These strips were combusted,<br />
14 CO2 was trapped <strong>and</strong> radioactivity was determined by scintillation counting. If<br />
M0 is the radioactivity associated with the first mm <strong>of</strong> leaf <strong>and</strong> Mx is the amount<br />
contained in segments above, the concentration gradient along the leaf is proportional<br />
to Mx/M0. With increasing distance from the solution, radioactivity (that is,<br />
Mx/M0) decreased, <strong>and</strong> in the segments 9 (6 h incubation) to 15 from the cut edge<br />
(24 h incubation) practically no radioactive triadimenol had arrived (Fig. 6.4).<br />
This approach is superior to trying to seal the wound, as it gives a result that can<br />
be generalised to other non-volatile compounds which are not readily metabolised.<br />
Cyan symbols represent Mx/M0 values calculated from (6.9)<br />
�<br />
Mx<br />
x<br />
= 1 − erf<br />
2 √ �<br />
, (6.9)<br />
Dt<br />
M0<br />
where x is the distance from the cut edge <strong>and</strong> t is the duration <strong>of</strong> incubation. The<br />
error functions <strong>of</strong> the term in brackets are tabulated (Crank 1975, Table 2.1, p. 375).<br />
With x <strong>and</strong> t given, various D values must be tried which result in the best fit to<br />
the data. With triadimenol, the best fit was obtained with a diffusion coefficient<br />
<strong>of</strong> 2 × 10 −10 m 2 s −1 . This is a value typical for diffusion in water at 25 ◦ C. Hence,<br />
triadimenol diffused up the leaf in an aqueous compartment, <strong>and</strong> viscous flow by