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Baden-Württemberg - Lichens of Wales

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Many lichen species are fairly substrate specific<br />

to the extent that they are limited for the most<br />

part on bark or wood or silicate rock or limestone<br />

or soil and scarcely ever change over to other<br />

substrates. A further substrate related<br />

specialization is caused by pH conditions,<br />

nutrient supply, water capacity (water storage<br />

capacity) and other chemical and physical<br />

properties <strong>of</strong> the substrate. A few examples:<br />

Many bark lichens are limited to acid and<br />

nutrient poor bark and therefore are found<br />

predominately on conifer trees, others are<br />

specialized on base-rich bark, certain rock<br />

lichens live only on heavy-metal rich silicate<br />

rocks, others prefer fine granular, relatively<br />

porous calcareous rock. Very rotted wood is<br />

floristically distinct from tough and hard wood.<br />

pH Value<br />

Soil- as well as bark- and rock-dwelling lichens<br />

at times show pH characterized dependence. For<br />

example certain lichen species occur only upon<br />

calcareous and base rich soils, others only on<br />

very acid.<br />

The evidence for the critical point pHvalue<br />

<strong>of</strong> sites colonized by the species is<br />

supported by extensive pH-measurements with<br />

a portable pH-meter with a flat membrane<br />

electrode (see WIRTH 1972); they were for the<br />

most part accomplished on site on rain moistened<br />

or distilled water moistened substrates. The pH<br />

conditions were described as follows:<br />

Substrate Plants<br />

extremely acid - pH 3.3 extreme.<br />

acidophytic<br />

very acid pH 3.4-4.0 very acidophytic<br />

rather acid pH 4.1-4.8 rthr acidophytic<br />

moderately acid pH 4.9-5.6 mod acidophytic<br />

sub neutral pH 5.7-7.0 sub neutrophic<br />

neutral pH 7 neutrophic<br />

moderately basic pH 7.1-8.5 mod basic<br />

basic over pH 7 basic<br />

embracing a wide pH range euryion<br />

The non eutrophic and substantially unaltered by<br />

air pollution bark <strong>of</strong> conifers and birch is mostly<br />

very acid (stem); <strong>of</strong> spruce and black alder rather<br />

acid; <strong>of</strong> pear rather (-moderately) acid; <strong>of</strong> beech,<br />

ash, apple, and basswood moderately acid; while<br />

most poplars, Norway maples, sycamore, and<br />

elm, moderately acid to sub neutral; and black<br />

elder usually sub neutral.<br />

The buffering capacity in size and range nearly<br />

parallels the pH value: the higher the pH value<br />

the higher the buffering capacity. The buffering<br />

capacity attains a great significance, above all<br />

through the onset <strong>of</strong> wide distribution <strong>of</strong> acid air<br />

pollution, which acidifies the tree bark. A<br />

relatively high buffer capacity possessed by the<br />

bark <strong>of</strong> the ash, which <strong>of</strong>ten bears a flora, which<br />

is typical for trees with higher pH values. The<br />

sycamore is unchanged. Here a relatively small<br />

buffer capacity in the case <strong>of</strong> a relatively higher<br />

pH goes along with an <strong>of</strong>ten narrow acidophilic<br />

lichen flora.<br />

Mineral Content, Nutrient Content, and<br />

Eutrophication<br />

Only little is known today about mineral content<br />

and above all about the nutrient content ( in a<br />

narrower sense, foremost nitrogen and<br />

phosphorus compounds) <strong>of</strong> lichen inhabited<br />

substrates. Justifiable are statements about the<br />

extent <strong>of</strong> eutrophication <strong>of</strong> the habitat by animal<br />

manuring (e.g. bird roosts), by dust films (tree<br />

bark, rocks, walls, etc.) and by mineral fertilizer<br />

(vineyard walls). For the ecological characterization<br />

<strong>of</strong> the lichens <strong>of</strong> this kind <strong>of</strong> habitat one<br />

can use the relatively appropriate and neutral<br />

expression “coniophytic” (in the case <strong>of</strong> dust<br />

impregnation) and “coprophytic” (in the case <strong>of</strong><br />

animal manuring). Here is employed a known but<br />

without doubt truly problematic term based on<br />

the nitrogen content: “nitrophytic”; here it makes<br />

use <strong>of</strong>, the quantity <strong>of</strong> nutrient supply to<br />

illustrate.<br />

Substrate: Plant:<br />

not eutrophic anitrophytic<br />

moderately eutrophic m. nitrophytic<br />

(m. nutrient-rich)<br />

rather eutrophic rthr. Nitrophytic<br />

( rather-nutrient rich)<br />

very eutrophic v. nitrophytic<br />

(strongly nutrient-rich)<br />

extremely eutrophic ext. nitrophytic<br />

(extremely nutrient-rich)<br />

Perhaps tree bark on the interior <strong>of</strong> extensive<br />

forests are not eutrophic, bark <strong>of</strong> field and<br />

avenue trees rather eutrophic, extremely etrophic<br />

are very nitrogen-rich habitats as well as very<br />

strongly dunged tops <strong>of</strong> bird roosts, the dog urine<br />

impregnated base <strong>of</strong> walls, and the surfaces near<br />

manure piles. Rock habitats naturally nutrientpoor<br />

are not eutrophic, but not counting others in<br />

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