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Bushland Weeds Manual - Environmental Weeds Action Network

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Chapter 4 Corms, Bulbs and Tubers Case Studies<br />

and the current policy is to allow<br />

indigenous species to recolonise<br />

treated sites unassisted.<br />

One of the major weeds that<br />

invades sites where bulbous weed<br />

control has taken place on the<br />

sandy soils of the Swan Coastal<br />

Plain is Perennial Veldgrass<br />

(Ehrharta calycina). A spray<br />

program using Fusilade ® is<br />

successfully controlling this weed<br />

over much of Shenton <strong>Bushland</strong><br />

including the study site.<br />

Stopping the spread<br />

The distribution of Yellow Soldier in<br />

Shenton <strong>Bushland</strong> is not dependent<br />

on disturbance, with populations<br />

extending into relatively intact<br />

bushland (Figure 1, Chapter 2).<br />

Preventing spread into undisturbed<br />

areas is the primary aim of the<br />

control program.<br />

Yellow Soldier spreads within the<br />

bushland via seed. The populations<br />

are generally quite discrete<br />

suggesting seed is not easily<br />

dispersed over long distances.<br />

Table 1. Costing of Yellow Soldier control over time.<br />

Source: Brown et al. (2002).<br />

Water movement and human<br />

activity play a role in the spread.<br />

Fire reduces competition from the<br />

native vegetation and creates bare<br />

areas where the seed can<br />

germinate.<br />

Fire, however, can also create<br />

opportunities for land managers to<br />

prevent further spread and<br />

establishment. After fire, Yellow<br />

Soldier plants are clearly visible and<br />

the reduced cover of native<br />

vegetation makes the resprouting<br />

flowering bulbs an easy target for<br />

herbicide control.<br />

Understanding the current<br />

distribution of the weed allows any<br />

new infestations to be recognised,<br />

recorded and targeted for control.<br />

Note: In this trial, the metsulfuron methyl<br />

was, where possible, targeted at Yellow<br />

Soldier and not applied as a blanket<br />

treatment over all vegetation. This is not a<br />

difficult or time consuming task but does<br />

require responsible operators with a<br />

reasonable knowledge of the flora. There is<br />

evidence from other studies that some native<br />

species, particularly seedlings, are<br />

susceptible to metsulfuron methyl at 5 g/ha<br />

(Moore 1999).<br />

How the study was used<br />

In the two years since the results of<br />

the study became available to the<br />

Friends of Shenton <strong>Bushland</strong>, they<br />

have secured funding to implement<br />

control of Yellow Soldier across the<br />

bushland. The map helped provide<br />

information for costing the project<br />

and indicated clear objectives to<br />

funding bodies. The Friends have<br />

since hired an experienced<br />

contractor with knowledge of the<br />

flora who has carried out the work.<br />

With approximately one hectare of<br />

bushland currently invaded the cost<br />

of control is relatively low. In the<br />

first year funding was obtained<br />

through a state government grant<br />

and in the second year the local<br />

government authority agreed to<br />

fund the follow-up work and should<br />

continue to do so until the<br />

populations require only occasional<br />

hand-removal.<br />

YEAR TREATMENT COST/HECTARE AREA COST<br />

2001 Brush-off @ 2.5 - 5 g/hectare + pulse@2 mL/L. $300.00/hectare ~ 1 hectare (from maps) $300.00<br />

2002 Brush-off @ 2.5 - 5 m/hectare + pulse@2 mL/L. $300.00/hectare check 1 hectare $300.00<br />

2003 As above but also consider hand weeding isolated plants. $300.00/hectare check 1 hectare $300.00?<br />

2004 Now only hand weeding isolated plants may be required. check 1 hectare<br />

45

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