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esulting seedlings were then rooted. In spring, 1970, rooted ramets of each clone were planted using 2x2 m spacing. The<br />
planting was done in a west-facing, gently sloping agricultural field where underground drain pipes had been installed and the<br />
clayey soil tilled bef<strong>or</strong>e planting. The homogeneous soil and the exact planting array reduced phenotypical variation in the<br />
stand to a minimum.<br />
From each of two clones, #194 and #582, twelve ramets were selected. Trees of Clone 194 had been used in an<br />
earlier mass-inoculation experiment with O. polonicum, and had proved relatively resistant to the infection (Christiansen,<br />
unpubl.). Nothing was known about the susceptibility of Clone 582 as to its susceptibility.<br />
The continuous rows of clones followed the slope of the field. The row of trees between Clone 194 and Clone 582<br />
had been cut in early October 1992, and so had the two rows on their other side. Thus both rows had a distance of 4 m to<br />
their nearest neighbours. Trees at both ends of the two rows were discarded as phenotypically aberrant, having much larger<br />
crowns than trees inside the stand.<br />
In late October, 1992, all branches below ca. 2.5 m were removed from all 24 trees. These branches were all dead<br />
due to shading. The ground on both sides of the upper six trees in each row was then covered with plastic sheets to prevent<br />
autumn and winter precipitation from percolating into the ground. Instead, <strong>this</strong> water was led down to the lower six trees in<br />
the two rows. On 20 April t993 the plastic ground cover was removed. Ropes were strung at 2 m above ground between the<br />
upper six trees of the rows, and non-transparent plastic tarpaulins were suspended from these ropes down to drains fastened<br />
to the stumps of the tree rows that had been removed. The drains collected the rain falling through the canopy, and channelled<br />
it down to the lower six trees in the rows.<br />
This way the six upper trees in a row were deprived of most of the precipitation falling from October till the end of<br />
the experiment. The lower six trees of the two rows served as unstressed controls. Because the early summer of 1993 was<br />
very dry, these control trees were given an extra 47 mm of water, applied under the canopy by means of a garden sprinkler.<br />
Monit<strong>or</strong>ing of Drought Stress<br />
Starting on 12 May 1993, drought stress was monit<strong>or</strong>ed by repeated measurements of pre-dawn xylem water potentials<br />
(hereafter termed "WP"), using a pressure chamber. Freshly excised shoots taken 4-5 m above ground were used. To<br />
detect a possible natural WP gradient along the slope, trees at the upper and lower ends of the rows were measured. By mid-<br />
June WPs of the experimental trees were clearly different from those of the controls, and after a monit<strong>or</strong>ing of all 24 trees on<br />
23 June we decided that they had reached a satisfact<strong>or</strong>y level of stress f<strong>or</strong> inoculation with the fungus.<br />
Fungal Inoculation<br />
Pri<strong>or</strong> to inoculation a 80 cm long template was attached around the stern between 1.2 and 2.0 m above ground. In the<br />
template evenly spaced holes had been punched at a density of 4 per dm 2,and the points of inoculation were marked through<br />
these holes. The choice of <strong>this</strong> particular dose was based on earlier experience with the susceptibility to infection by trees of<br />
Clone 194 and of two other clones growing in the same stand. Inoculation occurred on 25 June. Bark plugs were removed<br />
with a 5 mm c<strong>or</strong>k b<strong>or</strong>er. The inoculum, actively growing O. polonicum mycelium on malt agar, was placed in the cambiumholes,<br />
whereupon the bark plug was returned to its <strong>or</strong>iginal position (cf. H<strong>or</strong>ntvedt et al. 1983).<br />
Further Field and Lab<strong>or</strong>at<strong>or</strong>y Procedures<br />
Around the time of inoculation, exudation of constitutive resin was estimated twice (cf. Christiansen and H<strong>or</strong>ntvedt<br />
1983): on each tree 10 thin plastic tubes were inserted into holes cut with a c<strong>or</strong>k b<strong>or</strong>er about 2.1 m above ground. After 24<br />
hours the length of the resin column in the tube was measured.<br />
On l August, about 5 weeks after inoculation, exudation of resin from the point of inoculation was rec<strong>or</strong>ded on a<br />
subjective scale from 0 to 5, and used as an estimate of induced resinosis. On 14 September 1993, 81 days after inoculation<br />
all trees were felled, and tree height and height of the lowest green wh<strong>or</strong>l of branches were measured. The inoculated stem<br />
section was cut out, and brought to the lab<strong>or</strong>at<strong>or</strong>y.<br />
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