Integration of Conservation Strategies of Plant Genetic ... - Genres
Integration of Conservation Strategies of Plant Genetic ... - Genres
Integration of Conservation Strategies of Plant Genetic ... - Genres
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K. Ham m er<br />
Another factor for estimating the amount <strong>of</strong> plant genetic resourcesTable<br />
6: Number <strong>of</strong> accessions<br />
is the infraspecific variation, particularly <strong>of</strong> old and important cropsevaluated<br />
in the Gatersleben<br />
with a wide geographical amplitude. Some results from thegenebank<br />
1975-1990<br />
Gatersleben school <strong>of</strong> taxonomists have been compiled by Hammer<br />
(1981) and are shown in table 9. These results are based on<br />
Group<br />
morphological traits but they provide a certain impression on the<br />
No. accessions<br />
wealth <strong>of</strong> infraspecific variation.<br />
Cereals<br />
44.548<br />
Pulses<br />
16.221<br />
As a third factor the genepool has to be mentioned. When HarlanVegetables<br />
3.557<br />
and De Wet (1971) published their concept it was rather difficult toTotal<br />
include the secondary genepool in breeding work. Today we known<br />
numerous examples involving even the tertiary genepool and the<br />
range <strong>of</strong> usable material became rather high (see e.g. von Bothmer Source: Hammer (1993b)<br />
et al. 1992).<br />
64.326<br />
In this way maintaining and use <strong>of</strong> plant genetic resources is ever<br />
more becoming a global problem, approaching to and merging withTable<br />
7: Released cultivars bred<br />
the efforts trying to manage biodiversity. This task calls for theusing<br />
accessions from the<br />
inclusion <strong>of</strong> a whole range <strong>of</strong> possible inputs in a concerted actionGatersleben<br />
genebank (1973-<br />
1990)<br />
including the formal as well as the informal sector.<br />
Crop No. cultivars<br />
Ongoing evolution<br />
Spring barley<br />
30<br />
Winter barley<br />
Ongoing evolution within the populations <strong>of</strong> a genebank is a serious<br />
Spring wheat<br />
problem (see Hammer 1993a). Vavilov recommended theWinter<br />
wheat<br />
reproduction under ecologically and climatically similar situations asPeas<br />
3<br />
1<br />
12<br />
9<br />
the collecting sites and created a net <strong>of</strong> stations all over the former Lettuce<br />
1<br />
Soviet Union. Other genebanks without such tremendous<br />
Total<br />
possibilities had to rely on line-splitting to avoid the loss <strong>of</strong> rare and<br />
non-adapted genotypes within populations (Lehmann and Mansfeld<br />
1957). Genebanks try to maintain the original variation particularlySource:<br />
Hammer (1993b)<br />
by effective methods <strong>of</strong> long term storage <strong>of</strong> seeds. In this way they<br />
56<br />
try to reach a static equilibrium. Whereas a dynamic equilibrium, including also the important hostparasite-interactions,<br />
can be only achieved under on farm conditions.<br />
The most spectacular cases <strong>of</strong> ongoing evolution under farm conditions are connected with<br />
introgressions. Therefore, in many cases not only are on farm conditions involved but also more<br />
generally in situ situations when wild plants (progenitors, related races) are included (Hawkes 1991).<br />
In the following some recent examples for introgressions are mentioned. Introgressions have been<br />
observed by us between<br />
- wild (Secale strictum) and cultivated rye (S. cereale) in southern Italy (Hammer et al. 1985a);<br />
- wild/weedy (Hordeum vulgare subsp. spontaneum) and cultivated barley (H. vulgare) in Libya<br />
(Hammer et al. 1985b);