sdu faculty of forestry journal special edition 2009 - Orman Fakültesi
sdu faculty of forestry journal special edition 2009 - Orman Fakültesi
sdu faculty of forestry journal special edition 2009 - Orman Fakültesi
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SDÜ Faculty <strong>of</strong> Forestry Journal<br />
designers or planners <strong>of</strong> the green spaces, since some disturbances such as sunburn<br />
lesions or leaning stems by light deficit are generally due to inadequate designs. In<br />
fact, in natural environment most <strong>of</strong> these problems are very unusual. For all these<br />
reasons, the municipal green spaces management programmes should be look<br />
through in order to adapt conservation strategies to deal better with abiotic<br />
problems.<br />
Besides, abiotic diseases were much less frequent in shrubs, with 20-48% <strong>of</strong><br />
total disturbances depending on the considered year. Aphids were responsible <strong>of</strong> a<br />
great number <strong>of</strong> the biotic diseases, since it was the second problem, after dead<br />
plants. However, this result would have been pretty different if dead plants had<br />
been considered as an abiotic or biotic agent.<br />
4.9 Abiotic diseases affect a greater rank <strong>of</strong> tree and shrubs species.<br />
Abiotic diseases affect a greater variety <strong>of</strong> species (Table 7), which is<br />
reasonable if it is taken into account the fact that they are prompted by human<br />
activities or physical agents. However, biotic diseases seemed to be more specific<br />
in some plant species; for example, lace bugs (Corythuca ciliata), leaf beetle<br />
Galerucella luteola and Pseudomonas syringae subsp. savastanoi affected only one<br />
species (plane tree, Siberian elm and oleander, respectively). Concerning pests, this<br />
result would confirm the idea held by some authors who maintain that most<br />
herbivorous pests are <strong>special</strong>ized and only eat few taxa <strong>of</strong> plants (Rocray, 1983;<br />
Galvin, 1999; Raupp et al., 2001).<br />
Table 7. Affected species by biotic and abiotic diseases. Tree and shrub species affected<br />
by biotic and abiotic diseases and the percentage <strong>of</strong> the total species, in all the years and in<br />
all the inventoried green spaces.<br />
Trees Total<br />
Affected by<br />
biotic<br />
diseases<br />
Affected by<br />
abiotic<br />
diseases<br />
228<br />
Shrubs Total<br />
Affected by<br />
biotic<br />
diseases<br />
Affected by<br />
abiotic<br />
diseases<br />
Species 73 38 57 Species 77 32 40<br />
% <strong>of</strong><br />
species<br />
100 52.1 78.1<br />
% <strong>of</strong><br />
species<br />
100 41,6 51,9<br />
4.10 Positive association between naturalness <strong>of</strong> tree species and their<br />
health status.<br />
Pyšek’s criteria are used to define the naturalness <strong>of</strong> the tree (Pyšek , 1995). It is<br />
considered the national scale, therefore, all those species defined as natural <strong>of</strong><br />
Spain according to those criteria, are classified as native in this survey.<br />
Bibliography is used to make easier this controversial task (López González, 2002;<br />
Real Jardín Botánico, <strong>2009</strong>).<br />
A ji-squared test on the data shows that the relationship between health status<br />
(damaged or undamaged SYG) and naturalness (native or exotic SYG) is<br />
significant at 95% level (Table 8). The probability for an exotic SYG to be<br />
damaged is greater (0.68) than the probability for a native SYG (0.59). However,