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The effect of changing irrigation strategies on biodiversity.pdf

The effect of changing irrigation strategies on biodiversity.pdf

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Executive summary<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> industry is facing substantial change that is likely to affect the quantity and timing <str<strong>on</strong>g>of</str<strong>on</strong>g> water<br />

supply, as well as the infrastructure involved in water delivery and use. Effective adaptati<strong>on</strong> to this change<br />

while ensuring envir<strong>on</strong>mental sustainability requires knowledge <str<strong>on</strong>g>of</str<strong>on</strong>g> the <str<strong>on</strong>g>effect</str<strong>on</strong>g>s <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> practices<br />

and landscapes up<strong>on</strong> local and regi<strong>on</strong>al <strong>biodiversity</strong>, and the potential implicati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> predicted policy,<br />

supplier and farm changes. Here we report <strong>on</strong> a three year project c<strong>on</strong>ducted by CSIRO in collaborati<strong>on</strong><br />

with the Ricegrowers Associati<strong>on</strong> who have been c<strong>on</strong>ducting an Envir<strong>on</strong>mental Champi<strong>on</strong>s Program since<br />

2005. This program aims to assist landholders to improve envir<strong>on</strong>mental and ec<strong>on</strong>omic returns <str<strong>on</strong>g>of</str<strong>on</strong>g> their<br />

farm businesses and also allows them to be recognised for their past, current and future envir<strong>on</strong>mental<br />

stewardship at an industry level.<br />

Future changes in <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> practices will be driven by reduced availability <str<strong>on</strong>g>of</str<strong>on</strong>g> water. This will lead to the<br />

development <str<strong>on</strong>g>of</str<strong>on</strong>g> water c<strong>on</strong>servati<strong>on</strong> <str<strong>on</strong>g>strategies</str<strong>on</strong>g> and fewer areas under irrigated, broad acre crops. Overall<br />

these changes will result in a reducti<strong>on</strong> in the amount <str<strong>on</strong>g>of</str<strong>on</strong>g> water in irrigated landscapes available in<br />

c<strong>on</strong>structed wetland habitats. <str<strong>on</strong>g>The</str<strong>on</strong>g>se reducti<strong>on</strong>s may have some negative c<strong>on</strong>sequences for some comm<strong>on</strong>,<br />

generalist species that are tolerant <str<strong>on</strong>g>of</str<strong>on</strong>g> human disturbance and that also occur in natural wetland habitats.<br />

However it is likely that changes to <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> practices will not have large regi<strong>on</strong>al‐scale negative <str<strong>on</strong>g>effect</str<strong>on</strong>g>s <strong>on</strong><br />

these widespread species. A more significant issue in irrigated landscapes is likely to be how future<br />

changes to <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> practices will affect the remaining native vegetati<strong>on</strong>, particularly woodlands, because<br />

many <str<strong>on</strong>g>of</str<strong>on</strong>g> the terrestrial fauna species in these regi<strong>on</strong>s are associated with this vegetati<strong>on</strong>. Hence, we<br />

suggest that the landscape should be managed to provide the best c<strong>on</strong>diti<strong>on</strong>s for <strong>biodiversity</strong> in these<br />

remnant woodlands. We suggest that c<strong>on</strong>servati<strong>on</strong> <str<strong>on</strong>g>strategies</str<strong>on</strong>g> at the landscape and patch scale in irrigated<br />

regi<strong>on</strong>s should be the same as those recommended for other intensively managed landscapes, namely to<br />

improve natural vegetati<strong>on</strong> c<strong>on</strong>diti<strong>on</strong> and where possible increase its total area and c<strong>on</strong>nectivity.<br />

Irrigated agriculture in Australia has increased water availability to native flora and fauna in some areas by<br />

creating artificial open‐water habitats and raising water tables. However at the same time it has resulted in<br />

loss <str<strong>on</strong>g>of</str<strong>on</strong>g> native woodlands and serious reducti<strong>on</strong>s in the frequency, extent and durati<strong>on</strong> with which<br />

floodplains are inundated. <str<strong>on</strong>g>The</str<strong>on</strong>g> <str<strong>on</strong>g>effect</str<strong>on</strong>g>s <str<strong>on</strong>g>of</str<strong>on</strong>g> such changes <strong>on</strong> terrestrial floodplain vegetati<strong>on</strong> and fauna<br />

communities are poorly understood. This study examines 1) vegetati<strong>on</strong> c<strong>on</strong>diti<strong>on</strong> and structure; and 2)<br />

abundance <str<strong>on</strong>g>of</str<strong>on</strong>g> selected bird species in remnant Eucalyptus largiflorens floodplain woodlands <str<strong>on</strong>g>of</str<strong>on</strong>g> two<br />

c<strong>on</strong>trasting regi<strong>on</strong>s within the same drought‐affected catchment. It assesses the <str<strong>on</strong>g>effect</str<strong>on</strong>g>s <str<strong>on</strong>g>of</str<strong>on</strong>g> varying levels <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> landuse intensity surrounding woodland sites and <str<strong>on</strong>g>of</str<strong>on</strong>g> flood history within sites, testing the<br />

following propositi<strong>on</strong>s: a) floodplain woodlands with greater intensity <str<strong>on</strong>g>of</str<strong>on</strong>g> surrounding <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> landuse will<br />

be in worse c<strong>on</strong>diti<strong>on</strong> and have less structural complexity than other floodplain woodlands; b) floodplain<br />

woodlands with flood histories closer to ‘natural’ regimes will be in better c<strong>on</strong>diti<strong>on</strong> and will have greater<br />

structural complexity than other floodplain woodlands; c) greater surrounding <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> intensity will be<br />

associated with higher bird abundance in remnant floodplain woodlands; and d) lower flood frequency will<br />

be associated with lower bird abundance in remnant floodplain woodlands.<br />

This study dem<strong>on</strong>strates that where groundwater tables have fallen, rainfall is in deficit and surface<br />

flooding occurs less than <strong>on</strong>ce every two years, E. largiflorens trees will be in poor c<strong>on</strong>diti<strong>on</strong> and are more<br />

likely to die. In the absence <str<strong>on</strong>g>of</str<strong>on</strong>g> sufficient rainfall and groundwater, more frequent flooding is required to<br />

maintain E. largiflorens in good c<strong>on</strong>diti<strong>on</strong> (less crown death and greater crown density) than would<br />

normally be required. Irrigati<strong>on</strong> landuse intensity affects variables that create habitat complexity in<br />

woodlands, such as the presence <str<strong>on</strong>g>of</str<strong>on</strong>g> old and young trees, and the abundance <str<strong>on</strong>g>of</str<strong>on</strong>g> shrubs such as lignum and<br />

sclerolaena. Flow regimes (particularly prior wetting frequency) affect both structure and c<strong>on</strong>diti<strong>on</strong>. Two<br />

c<strong>on</strong>trasting levels <str<strong>on</strong>g>of</str<strong>on</strong>g> the <str<strong>on</strong>g>effect</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> landuse intensity <strong>on</strong> woodland bird abundance were found.<br />

Firstly, a broad scale positive relati<strong>on</strong>ship between <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> water availability and bird abundance at a<br />

regi<strong>on</strong>al scale; and sec<strong>on</strong>dly, a within‐regi<strong>on</strong> negative <str<strong>on</strong>g>effect</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> very high intensity <str<strong>on</strong>g>irrigati<strong>on</strong></str<strong>on</strong>g> landuse up<strong>on</strong>

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