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The Greenland White-fronted Goose Anser albifrons flavirostris

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<strong>Goose</strong> droppings/m 2<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

Phleum<br />

Phleum<br />

Phleum<br />

and clover<br />

Poa pratensis<br />

and clover<br />

Poa<br />

pratensis<br />

Figure 4.5. Dropping density (as an index of goose use<br />

+ SE) of pure sown stands of different grass species in<br />

seed trial plots in a single field at Hvanneyri from<br />

spring 1997.<br />

similar pattern can be seen based upon mean<br />

dropping densities (as an alternative assessment<br />

of goose use) in plots of sown single species<br />

stands of different grass species on trial plots<br />

within one field at Hvanneyri in 1997 (Figure 4.5).<br />

Note that the young establishing Deschampsia<br />

caespitosa formed a continuous open sward prior<br />

to tussock development and for this reason was<br />

therefore probably as attractive to geese as Poa.<br />

<strong>The</strong> total goose use of any particular field can be<br />

seen as the product of 4 elements over time:<br />

1) food density (which in turn determines the<br />

settlement density of geese)<br />

2) food intake rate (which determines food depletion<br />

rate)<br />

3) the 'giving up' density of food (the threshold<br />

at which the food resource is depleted to the<br />

point where it is more profitable to forage elsewhere)<br />

4) the rate of regrowth of forage plants (which<br />

determines the time until the food resource<br />

exceeds the 'giving up' density of food and<br />

geese return for sequential harvesting<br />

In the context of individual field units, containing<br />

grasslands of different sward composition, the<br />

settlement density represents the aggregative response<br />

of geese as predators to their 'prey' (i.e.<br />

grass blades, MS26). <strong>The</strong> length of stay of geese<br />

in that field represents the interaction between<br />

standing crop biomass and intake rates (i.e. the<br />

rate of depletion of prey items down to a threshold<br />

'giving-up' density). Finally, the length of absence<br />

is defined by the regrowth rate and quality<br />

of the prey to the point where this exceeds a profitability<br />

threshold for the geese, at which time<br />

Deschampsia<br />

caespitosa<br />

Festuca<br />

rubra<br />

Agrostis<br />

tenuis<br />

Festuca<br />

pratensis<br />

Alopecurus<br />

pratensis<br />

Deschampsia<br />

beringensis<br />

they will return in appropriate numbers to regraze<br />

the accumulated green biomass regrown in their<br />

absence.<br />

<strong>The</strong> three major grass species differ in their quality,<br />

biomass accumulation and growth pattern.<br />

<strong>The</strong> Phleum is an ecotype introduced from Norway,<br />

valued for its early season growth, which<br />

commences before other grasses begin above<br />

ground production. Even in the early stages of<br />

growth, this species responds to defoliation by<br />

geese by increasing leaf elongation and elevated<br />

protein levels, a feature which together with its<br />

growth form, makes it the most attractive forage<br />

species for sequential harvesting by geese (MS15,<br />

MS25, MS26). After reseeding of a field with<br />

Phleum, leaf densities are high, but as the tussockforming<br />

Deschampsia and the stoloniferous Poa<br />

invade, densities of Phleum decline rapidly (Fox<br />

1993). In the early stages of the spring staging<br />

period, geese therefore assort themselves in response<br />

to the shoot densities of this, the most<br />

abundant green plant material available (MS26),<br />

although geese select for the longest leaves<br />

(MS25). As a consequence, highest densities of<br />

geese tend to settle on Phleum fields and eat out<br />

most leaves of suitable length, returning only<br />

when regrowth has occurred above a threshold<br />

bite size (Figure 4.6, MS15).<br />

Poa grows at very low leaf densities and although<br />

of moderate nutrient quality, its later and (in some<br />

years) faster growth rate results in supporting<br />

lower densities of grazing geese throughout the<br />

staging period (unpublished data). In contrast to<br />

Phleum, where the high quality (low fibre, high<br />

protein) youngest leaf is always removed, leav-<br />

Cumulative percentage bird use<br />

100<br />

90<br />

80<br />

Phleum fields<br />

70<br />

Field 29<br />

60<br />

Field 36<br />

50<br />

Field 58<br />

40<br />

Field 59<br />

30<br />

20<br />

10<br />

0<br />

Field 48<br />

15-Apr 20-Apr 25-Apr 30-Apr 05-May 10-May<br />

Figure 4.6. Cumulative goose use of five hayfields<br />

dominated by Phleum pratense at Hvanneyri in spring<br />

1997. Note the rapid exploitation episodes, followed<br />

by short periods with reduced or little exploitation.<br />

39

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