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The use of habitat models in conservation of rare and endangered ...

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254<br />

Cover <strong>of</strong> Festuca rubra / F. ov<strong>in</strong>a [%]<br />

0% 40% 70%<br />

1<br />

1<br />

1<br />

P<br />

P<br />

P<br />

0<br />

35<br />

100<br />

0<br />

35<br />

100<br />

0<br />

35<br />

100<br />

Age<br />

[years]<br />

0<br />

Moss<br />

Cover [%]<br />

Age<br />

[years]<br />

0<br />

Moss<br />

Cover [%]<br />

Age<br />

[years]<br />

0<br />

Moss<br />

Cover [%]<br />

Figure 3. Best <strong>habitat</strong> model for Rhopalopyx vitripennis. Occurrence probability (P) on the z-axis, aga<strong>in</strong>st age <strong>and</strong> moss cover. Three<br />

levels <strong>of</strong> Festuca rubra/ov<strong>in</strong>a-cover are represented <strong>in</strong> the three diagrams.<br />

Cover <strong>of</strong> Corynephorus canescens [%]<br />

Proportion <strong>of</strong> brownfields with grassy, sparse vegetation with<strong>in</strong> 75m [%]<br />

0%<br />

40%<br />

80%<br />

1<br />

P<br />

1<br />

P<br />

1<br />

P<br />

0<br />

12<br />

50%-<br />

Height [cm]<br />

0<br />

12<br />

50%-<br />

Height [cm]<br />

0<br />

12<br />

50%-<br />

Height [cm]<br />

0% 15% 30%<br />

Litter<br />

Cover [%]<br />

0<br />

1<br />

1<br />

P<br />

P<br />

0<br />

0<br />

100<br />

12<br />

100<br />

12<br />

50%-<br />

Litter<br />

50%-<br />

Height [cm]<br />

Cover [%]<br />

Height [cm]<br />

0<br />

0<br />

Litter<br />

50%-<br />

Cover [%]<br />

Height [cm]<br />

0<br />

1<br />

P<br />

0<br />

100<br />

12<br />

Litter<br />

50%-<br />

Cover [%]<br />

Height [cm]<br />

0<br />

1<br />

P<br />

0<br />

100<br />

12<br />

0<br />

0<br />

Litter<br />

50%-<br />

Cover [%]<br />

Height [cm]<br />

0<br />

1<br />

P<br />

0<br />

100<br />

12<br />

Litter<br />

50%-<br />

Cover [%]<br />

Height [cm]<br />

0<br />

1<br />

P<br />

0<br />

100<br />

12<br />

100<br />

Litter<br />

Cover [%]<br />

100<br />

Litter<br />

Cover [%]<br />

100<br />

Litter<br />

Cover [%]<br />

Figure 4. Best <strong>habitat</strong> model for Neophilaenus m<strong>in</strong>or. In each diagram, P is plotted aga<strong>in</strong>st 50%-Height <strong>and</strong> litter cover. Columns<br />

represent different levels <strong>of</strong> Corynephorus canescens-cover <strong>and</strong> rows represent different proportions <strong>of</strong> BGS75.<br />

context might be due to two factors. First, most<br />

Auchenorrhyncha species seem to not need large<br />

sites to build up viable populations (Biedermann<br />

2002, 2004; Cron<strong>in</strong> 2004). Second, it is likely that<br />

for Auchenorrhyncha, most brownfield sites are<br />

not truly isolated. Small patches <strong>of</strong> potential<br />

<strong>habitat</strong> are found along most roads <strong>and</strong> tracks <strong>and</strong><br />

connect the larger sites.<br />

Overall, univariate responses <strong>of</strong> all four species<br />

corresponded well to <strong>habitat</strong> requirements<br />

described <strong>in</strong> Nickel (2003). For <strong>in</strong>stance,<br />

M. quadripunctulatus is regarded as a pioneer<br />

species preferr<strong>in</strong>g s<strong>and</strong>y, sparsely vegetated <strong>and</strong><br />

moderately dry to dry sites. This agrees with our<br />

results that the species was restricted to young sites<br />

with very scarce vegetation.

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