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Oral Submission Presentation by Blake Foster - New Zealand ...

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~ Herbaceous cover. Wildings have difficulty establishing within a vigorous<br />

herbaceous cover. This has been demonstrated over on Mt Cook station, where no<br />

wildings can be found in the dense grass / clover cover which established quickly after a<br />

fire destroyed a large area of a wilding Corsican pine forest. Where trees are felled, and<br />

the resulting slash is not so thick as to prevent any light reaching the ground surface,<br />

herbaceous growth, particularly of grasses, can be sufficiently vigorous to prevent wilding<br />

re-establishment from seed for a number of years (see above). Evidence of this can be<br />

seen at a number of sites on Pukaki Downs.<br />

• Maintaining improved pasture and intensive grazing.<br />

Pasture which is improved <strong>by</strong> seeding and fertilising will not be invaded <strong>by</strong> wildings. This<br />

is well shown on the Canterbury plains, despite the presence of a wide range of spreadprone<br />

conifers. There is also good evidence on Pukaki Downs, where the hay paddocks in<br />

block 31 and parts of block 25 are free of wildings despite the fact that there are forests of<br />

contorta pine adjacent. Although improved pasture will prevent wilding invasion, it is<br />

acknowledged that much of Pukaki Downs does not lend itself to this form of wilding<br />

prevention. Also, it must be remembered that a) this improvement and the grazing which<br />

it can support must be maintained, and b) if the seed rain from immediately adjacent trees<br />

is high, then even a relatively small easing of grazing and/or fertiliser regimes can result in<br />

wildings getting established. In addition to improved pasture, the cropping of land for<br />

arable purposes will deliver the same wilding prevention outcome.<br />

• Planting a margin of less spread-prone trees.<br />

The theory here is that in a forest, most cones are produced on edge trees which have<br />

green crowns extending to ground level - as opposed to the smaller and higher canopies<br />

of internal trees. In addition, edge trees are more likely to disseminate seed onto<br />

unplanted adjacent land. Therefore, if the margin of a forest is planted with a zero or less<br />

spread-prone species, the risk of wilding spread is reduced. If the marginal species is<br />

faster growing than the forest species, then it can also create a greater physical barrier to<br />

the spread of seed. However, this marginal planting can only be most effective on flat<br />

land. Where the forest is on rolling or hilly land, especially if this faces into the prevailing<br />

wind, then there are greater opportunities for seed to be picked up from the internal tree<br />

canopy and the effectiveness of marginal planting is diminished.<br />

Assisting containment on Pukaki Downs.<br />

Taking the above points in mind, the best containment management options appear to be<br />

the:<br />

~ Establishment of forests of less spread-prone species, such as the radiata x<br />

attenuata hybrid, on areas immediately to the west of the contorta forests most likely to<br />

remain intact – such as on blocks 12, 13, 19 and the western parts of block 9. In a<br />

continuation of this western edge planting to the north of the property, further<br />

establishment could be made on the eastern slopes under the Little Rhoboro Hills (blocks<br />

20 and 14) - and also along the northern boundary with Ferintosh, down to SH80. Over<br />

time, the 20m strip of less spread-prone species could be extended down the northeastern<br />

margin alongside SH80, there<strong>by</strong> minimising the spread of wildings onto the<br />

highway margin. Such a strip could be established wherever spread-prone trees are likely<br />

to grow alongside SH80. As they would be on the western side of the road, there should<br />

be no risk of promoting highway icing during the winter.<br />

To the east of SH80 in block 32, improved pastures and grazing are restricting fringe<br />

spread westwards from the lakeside forests of contorta pine – and also from smaller<br />

planted areas of Corsican pine and Douglas-fir. Additional forests, or a 4-row strip, of less<br />

spread-prone species could be established along the western margin of these more<br />

spread-prone species, in order to further reduce the risk of unwanted spread.<br />

~ Maintenance of improved pasture and associated grazing (or arable cropping)<br />

where it is currently restricting wilding establishment. This is in blocks 31 (especially<br />

around the Dusky Reserve) and 32 and further to the west in the southern half of block 25,<br />

just beyond the forested blocks 9 and 12. The hilly topography, limited moisture<br />

11

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