Literature review: Impact of Chilean needle grass ... - Weeds Australia
Literature review: Impact of Chilean needle grass ... - Weeds Australia
Literature review: Impact of Chilean needle grass ... - Weeds Australia
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Slashing and mowing<br />
Slashing can reduce the production <strong>of</strong> panicle seed and stem cleistogenes but has little other benefit, apart from stimulating<br />
regrowth that is more palatable to grazing livestock (Snell et al. 2007). Britt (2001) found that plants slashed to 1 cm in early<br />
May at Greenvale had failed to produce flowering stems by late October, whereas 60% <strong>of</strong> unslashed plants had produced<br />
flowering heads by that time. Hocking (2005b) found that mowing in spring had no major effect on the number <strong>of</strong> mature<br />
tussocks and failed to significantly reduce tussock size. Slay (2001) incorrectly attributed to N. neesiana the findings <strong>of</strong> Mulham<br />
and Moore (1970) about mowing Austrostipa swards. Those authors found that mowing in late September prevented seed<br />
maturation and that late mowing could allow seed maturation on cut stems. Slay (2001) found that mowing twice at early seed<br />
head emergence (Feekes stages 10-10.4) totally prevented the formation <strong>of</strong> viable panicle seed and stem cleistogenes and<br />
resulted in regrowth acceptable for livestock grazing. Grech (2007a) also studied slashing impact in pastures and quantified some<br />
benefits in terms <strong>of</strong> palatable regrowth that could be exploited by grazing. Mowing before emergence <strong>of</strong> the panicle may result<br />
in the growth <strong>of</strong> more reproductive tillers, so repeated treatments are generally required. The best time to slash or mow is before<br />
flowering when 25-75% <strong>of</strong> the heads have emerged from the flag leaf sheath (Slay 2002c), or at the flowering stage (Grech<br />
2007a, Snell et al. 2007). Slay (2002c) noted that the resultant reduction in shade may facilitate the survival <strong>of</strong> seedlings.<br />
Mowing can encourage the formation <strong>of</strong> prostrate swards, so may also reduce the production <strong>of</strong> stem cleistogenes (Snell et al.<br />
2007).<br />
Fire<br />
Published information on the value <strong>of</strong> fire as a managment method are equivocal. According to Bourdôt (1989) the New Zealand<br />
experience was that repeated fires favour the <strong>grass</strong>, and when tried as a means <strong>of</strong> control in Marlborough appeared to have<br />
“eliminated other species resulting in pure stands”. Muyt (2001 p. 73) stated that fire “stimulates vigorous regrowth”, <strong>of</strong>ten<br />
promotes spread, but is useful for improving access and effectiveness <strong>of</strong> herbicide application by removal <strong>of</strong> litter and dead<br />
material. However he also noted that fire “generates bare ground and reduces immediate competion, conditions that are ideal for<br />
seed germination” (Muyt 2001 p. 73) so should therefore should be followed by herbicide application (Muyt 2005). In pastures,<br />
Slay (2002c) recommended spraying with glyphosate to dry out the <strong>grass</strong> before burning and follow-up herbicidal control to kill<br />
seedlings that grow from cleistogenes in burnt tussocks.<br />
Snell et al. (2007) advocated the use <strong>of</strong> fire to prevent seed set, burn <strong>of</strong>f standing seed and to stimulate growth <strong>of</strong> seed from the<br />
soil seed bank, but advised integration with other selective control techniques. They also noted its usefulness in enabling a<br />
clearer indication <strong>of</strong> intensity and pattern <strong>of</strong> infestations.<br />
In T. triandra <strong>grass</strong>lands burning in spring is recommended, so competing cover establishes quickly (Muyt 2001). Hocking<br />
(2005b) found that burning in spring in a native <strong>grass</strong>land under drought conditions resulted in major reduction <strong>of</strong> large, mature<br />
tussocks and proliferation <strong>of</strong> small tussocks, probably derived from the large. The total area occupied by tussocks was decreased<br />
by >75% without decreasing the density <strong>of</strong> the population. Late spring burns reduced seed production by half, and did not lead to<br />
major seedling recruitment. He suggested that fire was therefore useful to weaken the stand, making it more susceptible to<br />
subsequent control activities <strong>of</strong> a different type and in limiting seed production, and could play a role in a containment strategy<br />
and integrated management. Hocking (2007) noted that fires kill few plants and that seed production resumes within a year. Snell<br />
et al. (2007) agreed that burning usually does not result in much kill <strong>of</strong> mature plants. However reductions in density <strong>of</strong> c. 90%<br />
have been reported after annual November burning for 5 years at Plenty Gorge Parklands, Victoria, however N. neesiana was<br />
replaced by Phalaris aquatica (Snell et al. 2007 p. 34), which may have even worse biodiversity impacts.<br />
The effects <strong>of</strong> repeated periodical burning and <strong>of</strong> fires in autumn do not appear to have been adequately assessed by scientific<br />
tests. In particular better knowledge <strong>of</strong> the effects <strong>of</strong> fire on the litter and near-surface soil seed banks would be desirable.<br />
Cultivation and cropping<br />
The objective <strong>of</strong> cultivation and cropping is too reduce the soil seed bank before re-establishment <strong>of</strong> a vigorous pasture that can<br />
suppress any seedlings that may subsequently appear. Cultivation stimulates seed germination and shallow cultivations are<br />
supposedly superior in depleting the seed bank because most <strong>of</strong> the seed is close to the surface (Snell et al. 2007). Herbicides<br />
applied by boom spray are recommended as the intitial treatment, followed by a series <strong>of</strong> shallow cultivations interspersed with<br />
dense, uniform sowing <strong>of</strong> annual fodder crops (Bourdôt 1988, Duncan 1993, Slay 2002a 2002c). Shallow cultivation (no greater<br />
than 5 cm) is recommended so that seed will not buried and the maximum amount will germinate. Slay (2002a) warned that the<br />
cultivation technique and timing were critical to minimise dispersal <strong>of</strong> cleistogenes. Duncan (1993) recommended winter<br />
cropping for two years followed by pasture establishment, and in less arable areas herbicide spraying, direct drilling <strong>of</strong> fodder<br />
crops, and fertiliser application. Bourdôt (1988) recommended three years <strong>of</strong> such management before sowing <strong>of</strong> ‘permanent’<br />
pasture. Storrie and Lowien (2003) broadened the range <strong>of</strong> recommended crops to include summer forage species and summer<br />
grains, and the aerial application <strong>of</strong> herbicide, seed and fertiliser to treat steep, rocky, inaccessible areas. Establishment <strong>of</strong><br />
lucerne after glyphosate spraying, with residual <strong>grass</strong> herbicide application and winter spraying with <strong>grass</strong>-selective paraquat and<br />
metribuzin is an alternative approach (Bourdôt 1988).The best methods, including crop and pastures to sow, depend on the<br />
specific characteristics <strong>of</strong> the infestation, regional agronomic factors, etc. (Slay 2002c).<br />
Grazing<br />
Overgrazing is likely to favour N. neesiana, due to its lower palatability (Bourdôt 1988) at least during its reproductive period<br />
(Grech 2007a). Crude protein, metabolisable energy and digestible dry matter contents <strong>of</strong> N. neesiana peak in winter and early<br />
spring and decline markedly from September to December, corresponding with the onset <strong>of</strong> reproductive phase (Grech 2007a).<br />
Strategic grazing in pastoral ecosystems to best utilise the green feed produced by N. neesiana in winter and spring has been<br />
intensively studied (Gardener 1998, Grech 2005a 2007a). Intense grazing pressure over a short period is required to suppress<br />
seed production (Storrie and Lowien 2003) but in practice is very difficult to achieve and probably not feasible in most grazing<br />
enterprises (Slay 2002a, Grech 2007a). In addition there is a risk that overgrazing will encourage further N. neesiana<br />
establishment (Slay 2002a). Set stocking with sheep exacerbates the problem by reducing the cover <strong>of</strong> desirable pasture <strong>grass</strong>es<br />
and creating more bare ground suitable for further N. neesiana establishment (Grech 2007a, Snell et al. 2007). Preliminary<br />
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