Fact Sheet |
FS 04/02 |
Well-designed windbreaks can benefit every farm. They can be used to:

A windbreak of trees and shrubs works by filtering and breaking the force of the wind. Permeable windbreaks that let some wind pass through are most suitable. The slight movement of air through the windbreak forms a cushion of slow-moving air on both sides of the windbreak (see diagram).
For best results, plant windbreaks at right angles to the winds from which protection is needed. These are not necessarily the prevailing winds. Crops are often worst affected by hot, drying winds from the north. Livestock are at greatest risk from cold winds and rain which come from the south or south-west.
To keep costs down, establish windbreaks against existing fence lines where possible, but consider the best location to match land capability boundaries. If practical, a good location for a windbreak is high in the landscape (e.g. along a ridge line) as a greater area in the lee is protected from wind. Take care to avoid planting close to windmills and do not plant under power lines.
The windbreak height determines the size of the sheltered area. The taller the trees in the windbreak, the greater the area it protects. As a guide windbreaks are most effective for a distance of 12 to 15 times the height of the tallest trees, and protection of crops has been observed up to 25 times the height.
Wind is deflected around the ends of windbreaks. The deflected wind can accelerate around the end of the belt causing localised crop damage. For this reason windbreaks should be long continuous lines of trees and shrubs to minimise any end effects. Gaps within the windbreak can have the same effect so where these are essential, for example where a gate is needed, the gap should be angled at 45 0 to prevent the wind from accelerating through the space.

Windbreaks incorporating both trees and shrubs in three to six rows are effective for most farm situations. Multiple-row windbreaks are less affected by gaps caused by missing trees than single row windbreaks. Where land is limited, a staggered two-row design of tall trees and lower shrubs should be used for the best shelter effect. Single-row windbreaks should only be used where land is so valuable that only a small amount of space can be spared for tree planting - for example, on high-value horticultural land. When only one row of trees can be planted, try to use trees that have foliage from the ground up if possible. Belts, with trees only, can be established for wood production, but they may be less effective in providing low shelter for animals.
The distance between plants in windbreaks is based on the size of suitable plants for the local climate and soils (see Appendix 1). It is also important to allow access for tractors and machinery for weed control and maintenance. Use the spacings in the diagram as a guide.

Direct seeding is a method using a specialised machine to sow a mixture of native seed straight into the ground. It is very quick, low-labour and low-cost. Recommended for all soils except heavy cracking clays where tubestock seedlings are preferred. Local nurseries and contractors specialising in farm trees include:
Weed control. Many areas in the Upper South East where landholders wish to establish windbreaks carry pastures and weeds that compete strongly with new seedlings for moisture and light. To be successful with revegetation, you must get rid of all existing pasture and weeds well in advance of planting seedlings or direct seeding. Particular attention should be given to perennials such as sorrel, veldt grass, primrose, couch grass, kikuyu, lucerne, bracken and phalaris. This is usually achieved by spraying out the site with broad-spectrum knockdown herbicides such as glyphosate several times before planting or seeding.
Aim to start weed control 12 months before planting. Start in late winter or early spring and again in summer (depending on weeds present). Spray next after the following break of season and again just prior to planting if a new flush of germination has occurred. Residual herbicides (eg Oust ®, Ally ®, Goal ®, simazine) can be used for more effective weed control but they can harm seedlings if not used appropriately (note that some are not registered for use with natives).
Weed control should be carried out again in the year after planting/seeding. This can be done with shielded sprays but special over-spray mixtures can also be used.
Seek advice from revegetation consultants or contractors prior to using residual chemicals or over-sprays.
Ripping to allow better root penetration should be considered if limestone or a clay hardpan is within 10 to 15cm of the soil surface. Rip-lines in clay soils can tend to open up later in summer so only rip if absolutely necessary. For heavy soils, rip in summer or early autumn when soils are dry so that the ripper shatters the soil rather than slices through it. Slicing glazes the soil surface and prevents lateral root penetration. On the other hand, rip non-wetting sands (if needed for planting tools) only if moist for best results.
Ripping should be at least 50cm deep if possible. Use a concrete roller (at least 60 cm wide) over the rip line afterwards to help crush rocks, remove air pockets and settle the soil. Avoid rolling with narrow tractor tyres as this can cause compaction and guttering. Where planting or spraying machinery is to be used, any large rock pieces brought to the surface by ripping should be removed if they cannot be crushed.
Mounding of the soil to 50cm high and 50cm wide can help plant survival in waterlogged and saline areas. Bear in mind though that the surface of mounds will dry out quicker in summer so this technique should only be used in very wet areas. When mounding in long rows, consider leaving breaks every now and then to allow for natural water flows.
It is usually best to keep windbreaks permanently fenced to prevent gaps being created by livestock browsing on the lower limbs of established trees and shrubs. Fencing may not be required in situations of continuous cropping; in timber belts with trees only, which are not likely to suffer bark damage from stock; or in some alley farming situations with fodder shrubs where stock grazing of the windbreak is expected.
Financial assistance maybe available through the Natural Heritage Trust Envirofund. Contact South East Natural Resource Management Board, Community Landcare Coordinator (8724 6033) for details.
You maybe able to claim a tax deduction in the year you incur capital expenditure on landcare measures for land in Australia provided you incur it "erecting fences to keep out livestock or vermin from areas affected by land degradation to prevent or limit further damage and assist in reclaiming the areas" or "erecting fences to separate different land classes in accordance with an approved land management plan" (ATO, Information for Primary Producers). A recoupment of the deductible expenditure is assessable under Subdivision 20-A of the Income Tax Assessment Act 1997 (ITAA 1997). Contact the Australian Taxation Office or your taxation adviser for an information pack for primary producers.
Further information:
PIRSA Rural Solutions Environmental Consultants: Struan Office 8762 9100.
Useful references:
Last update: February, 2008.
Acknowledgments: Based on a fact sheet originally prepared by Jim Burston.
Agdex: 301/31
Author: Peter Tucker and Zita Stokes, Environmental Consultants, Struan.
When selecting species for a windbreak firstly consider what your goals are. Apart from shelter, if you wish to enhance wildlife habitat, choose a diverse range of local native species. If you wish the belt to also provide products, you will need to seek specialist advice about species suitable for timber, firewood, pollen for honey, seeds etc. Ultimately the species chosen, whether native or exotic, need to suit the soil type and climatic conditions of the site. The following soil type information and species table will help give an indication of some species suitable for windbreaks in the Upper South East.
Soil type is a very important consideration when planting trees. Some species will survive well on waterlogged clays, others will only thrive in well-drained sands. Choosing the wrong species for a soil type can end in poor growth and premature deaths. The table on the following pages shows native plant species which are suitable for windbreaks on eight major soil types found in the Upper South East region (defined here as the areas north of Kingston - Lucindale - Padthaway – Kybybolite up to the Coorong District Council area).
A uniform clay profile, being very sticky when wet. The surface soil is self-mulching and the pH is alkaline. In uncultivated areas, gilgai are common (e.g. Wolseley district).
A variable depth of sand over clay, ranging from 10 to 100cm, usually on flats. Soil pH is generally acidic and has a moderate water holding capacity. The upper 10 to 20cm is coloured grey-brown by organic matter.
Generally found in Bordertown/Wolseley/Mundulla region, these soils have a brown sandy-loam to loam surface texture, which sets hard when dry. Good water holding capacity. Soil pH is generally neutral to slightly acidic.
Sandy range country with undulating to rising terrain. Accumulation of organic matter at surface. The sands have a low water-holding capacity, low soil fertility, often non-wetting and the pH is mildly acidic.
Typical of old inland ranges where dune limestone underlies a shallow sandy topsoil. The sand can be grey or brownish to white depending on organic matter.
For example in the Keith/Culburra/Coonalpyn area; these soils are typically shallow, grey or brown in colour, and hard setting when dry. Frequent limestone outcrops and/or free limestone in the topsoil. Soil pH is generally neutral to alkaline.
A red-brown soil (varying from sandy- to clay-loam) overlying limestone. Soil depth is shallow, with frequent limestone outcrops. Soil pH is generally neutral to slightly acidic in the surface but neutral to alkaline above the limestone.
Deep, pale yellow loose coastal sand consisting mainly of fragments of marine shells. The upper 20 to 30cm is coloured grey-brown by organic matter. The soils are generally alkaline and have a low water holding capacity.
Note: this list is only a guide. If you are seeking species local to your particular area, talk to a revegetation consultant. Remember: a windbreak works best if using a mixture of trees and shrubs. Do not rely on only trees if they shed lower limbs as they mature. Height is that at maturity (range depends on site conditions); Rainfall is that for best survival/growth; Waterlogging tolerance – more ticks = better survival at sites that become waterlogged. Asterisk * = generally not suited to large-scale direct seeding either due to lack of available seed or problems with germination times. Soil types explained in text prior page.
|
Botanic name |
Common name |
Form |
Height (m) |
Rainfall (mm) |
Water logging tolerance |
Special notes |
Soil type suitability |
|||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
|||||||
|
Acacia brachybotrya |
Grey Mulga |
Medium shrub |
1-3 |
250-500 |
√ |
√ |
√ |
√ |
√ |
|||||
|
Acacia calamifolia |
Wallowa |
Medium shrub |
2-4 |
200-700 |
√ |
√ |
√ |
√ |
√ |
|||||
|
Acacia cupularis |
Coastal Umbrella Bush |
Small shrub |
1-2 |
350-700 |
√ |
Fast growing |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Acacia farinosa |
Mealy Wattle |
Small shrub |
1-2 |
300-600 |
√ |
√ |
√ |
|||||||
|
Acacia hakeoides |
Hakea Wattle |
Medium shrub |
1-4 |
250-500 |
√ |
√ |
||||||||
|
Acacia halliana |
Hall's Inland Wattle |
Small shrub |
1-2.5 |
250-400 |
Spreads 4-5 m wide |
√ |
√ |
√ |
||||||
|
Acacia leiophylla |
Limestone Wattle |
Medium shrub |
1-2.5 |
500-800 |
√ |
√ |
√ |
|||||||
|
Acacia mearnsii |
Black Wattle |
Medium tree |
7-10 |
>600 |
Padthaway area; fast growing |
√ |
||||||||
|
Acacia melanoxylon |
Blackwood |
Medium tree |
8-15 |
>550 |
√ |
Native in southerly areas |
√ |
|||||||
|
Acacia microcarpa |
Manna Wattle |
Small shrub |
1-3 |
250-600 |
√ |
√ |
√ |
√ |
||||||
|
Acacia myrtifolia |
Myrtle Wattle |
Small shrub |
1-2 |
>500 |
√ |
√ |
√ |
√ |
√ |
√ |
√ |
|||
|
Acacia paradoxa |
Prickly Acacia or Kangaroo Thorn |
Medium shrub |
2-3 |
>300 |
Fast growing; may be invasive; provides good protective habitat for small native birds |
√ |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Acacia pycnantha |
Golden Wattle |
Medium tree |
4-8 |
>350 |
Fast growing; national floral emblem |
√ |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Acacia rigens |
Needle Bush Wattle |
Shrub |
2-3 |
200-300 |
√ |
√ |
√ |
|||||||
|
Acacia rupicola |
Rock Wattle |
Shrub |
1-2.5 |
300-800 |
√ |
√ |
√ |
√ |
√ |
|||||
|
Adriana klotzschii |
Coastal Bitter Bush |
Shrub |
1-2 |
>300 |
Coastal plant |
√ |
√ |
|||||||
|
Allocasuarina leuhmannii |
Buloke, Bull Oak |
Medium-tall tree |
7-15 |
450-650 |
√√√ |
Found on clays near Vic border; food source for red-tailed black cockatoo; suckers |
√ |
√ |
||||||
|
Allocasuarina mackliniana |
Macklin's She-oak |
Small shrub |
1-2 |
400-600 |
√ |
√ |
√ |
|||||||
|
Allocasuarina muelleriana |
Slaty She-oak |
Medium shrub |
2-4 |
350-600 |
√ |
√ |
√ |
|||||||
|
Allocasuarina paludosa |
Scrub / Swamp She-oak |
Medium shrub |
2-3 |
>500 |
√ √ |
√ |
||||||||
|
Allocasuarina pusilla |
Dwarf She-oak |
Small shrub |
1-1.5 |
350-750 |
√ |
√ |
√ |
√ |
||||||
|
Allocasuarina verticillata |
Drooping She-oak |
Medium tree |
5-8 |
>350 |
√ |
Excellent for firewood |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Atriplex cinerea |
Coast Saltbush |
Small shrub |
1-1.5 |
350-700 |
√ |
OK for moderately saline sites; found naturally on coasts, sandy shore lines |
√ |
|||||||
|
Baeckea behrii |
Short-leaved Broombush |
Small shrub |
1-2 |
300-500 |
√ |
√ |
√ |
|||||||
|
Banksia marginata* |
Silver Banksia |
Small-tall shrub |
2-5 |
>400 |
√ |
Flowers abundant in nectar provide good food source for wildlife; small on poor sands, tall on fertile loams |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Banksia ornata* |
Desert Banksia |
Medium shrub |
1-3 |
400-650 |
Flowers abundant in nectar provide good food source for wildlife |
√ |
||||||||
|
Bursaria spinosa* |
Christmas Bush |
Medium-tall shrub |
2-5 |
>300 |
Slow growing; germinates in cold months |
√ |
√ |
√ |
√ |
√ |
√ |
|||
|
Callistemon rugulosus |
Scarlet Bottlebrush |
Medium shrub |
2-4 |
450-700 |
√√√ |
Prefers damp areas; flowers rich in nectar are food source for birds |
√ |
|||||||
|
Callitris gracilis |
Native Pine |
Medium tree |
5-15 |
350-450 |
Slow growing |
√ |
||||||||
|
Callitris verrucosa |
Scrub Pine |
Small tree |
2-5 |
250-400 |
Slow growing |
√ |
||||||||
|
Calytrix tetragona* |
Fringe Myrtle |
Small shrub |
0.5-2 |
>400 |
Showy pink to purple flowers |
√ |
√ |
|||||||
|
Casuarina glauca (native to NSW & QLD only) |
Swamp Oak |
Medium tree |
10-15 |
>350 |
√√√ |
Caution: weed potential, suckers freely; use on saline sites only |
√ |
√ |
||||||
|
Casuarina obesa (native to WA only) |
WA Swamp oak |
Medium tree |
10-15 |
>350 |
√√√ |
Non-suckering unless disturbed, use on saline sites only |
√ |
√ |
||||||
|
Dodonaea viscosa spatulata |
Sticky Hopbush |
Medium shrub |
2-4 |
>450 |
√ |
√ |
√ |
√ |
√ |
√ |
||||
|
Eucalyptus arenacea |
Sand Stringybark |
Small tree |
3-6 |
400-650 |
Hardy on poorest sands |
√ |
√ |
|||||||
|
Eucalyptus baxteri |
Brown Stringybark |
Medium tree |
10-15 |
>500 |
Hardy on poor sands |
√ |
√ |
|||||||
|
Eucalyptus behriana |
Broad-leaved Mallee Box |
Medium tree |
8-12 |
400-550 |
√ |
√ |
√ |
√ |
||||||
|
Eucalyptus camaldulensis |
Red Gum |
Tall tree |
15-25 |
500-750 |
√√√ |
Good timber, firewood, habitat |
√ |
√ |
√ |
|||||
|
Eucalyptus diversifolia |
Coastal White Mallee |
Small-medium tree |
5-15 |
350-750 |
Hardy coastal tree; excellent for well-drained soils with limestone |
√ |
√ |
√ |
√ |
|||||
|
Eucalyptus dumosa |
White Mallee |
Medium tree |
5-8 |
300-650 |
√ |
√ |
||||||||
|
Eucalyptus fasciculosa |
Hill or Pink Gum |
Medium tree |
10-15 |
450-750 |
Excellent for firewood |
√ |
√ |
√ |
√ |
√ |
√ |
|||
|
Eucalyptus gracilis |
Yorrell |
Small tree |
4-7 |
250-450 |
√ |
√ |
√ |
|||||||
|
Eucalyptus incrassata |
Ridge-fruited Mallee |
Small tree |
4-8 |
350-550 |
√ |
|||||||||
|
Eucalyptus largiflorens |
River or Black Box |
Medium-tall tree |
6-15 |
350-550 |
Usually close to watercourses |
√ |
√ |
|
Eucalyptus leptophylla |
Narrow-leaved Red Mallee |
Small tree |
2-6 |
200-550 |
√ |
√ |
√ |
√ |
||||||
|
Eucalyptus leucoxylon megalocarpa |
Large Fruited SA Blue Gum |
Medium tree |
6-10 |
450-800 |
√ |
Rounded shrubby coastal form |
√ |
√ |
||||||
|
Eucalyptus leucoxylon pruinosa |
Inland SA Blue Gum |
Medium-tall tree |
8-17 |
450-650 |
√ |
Blue-leaved inland form |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Eucalyptus leucoxylon stephaniae |
Scrubby Blue Gum |
Small tree |
4-15 |
450-650 |
√ |
Northern form |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Eucalyptus microcarpa |
Grey Box |
Medium-tall tree |
10-20 |
500-600 |
√√ |
Found close to Victorian border |
√ |
√ |
||||||
|
Eucalytpus occidentalis (native to WA) |
Flat-topped Yate |
medium-tall tree |
10-20 |
>350 |
√√ |
Caution: may be short-lived; use only on saline sites; firewood/timber |
√ |
√ |
||||||
|
Eucalyptus odorata |
Peppermint Box |
Medium tree |
4-16 |
350-500 |
Mainly found around Bordertown |
√ |
√ |
√ |
√ |
|||||
|
Eucalyptus oleosa |
Red Mallee |
Small tree |
5-8 |
300-450 |
Valued for honey production |
√ |
√ |
√ |
√ |
|||||
|
Eucalyptus porosa |
Mallee Box |
Medium tree |
5-10 |
300-500 |
√ |
√ |
√ |
√ |
||||||
|
Eucalyptus socialis |
Summer Red Mallee |
Small tree |
5-10 |
250-450 |
√ |
√ |
√ |
√ |
||||||
|
Eucalyptus viminalis cygnetensis |
Rough-barked Manna Gum |
Medium tree |
10-15 |
>450 |
√ |
Preferred koala food |
√ |
√ |
√ |
√ |
√ |
|||
|
Goodia lotifolia |
Golden Tip |
Medium shrub |
1-3 |
550-700 |
√ |
√ |
||||||||
|
Hakea muelleriana* |
Desert Hakea |
Medium shrub |
1-3 |
350-500 |
√ |
√ |
√ |
|||||||
|
Hakea nodosa* |
Yellow Hakea |
Medium shrub |
2-3 |
>550 |
√√ |
√ |
||||||||
|
Hakea rostrata* |
Beaked Hakea |
Small shrub |
1-2 |
>500 |
√ |
√ |
||||||||
|
Hakea rugosa* |
Dwarf Hakea |
Small shrub |
1-2 |
350-700 |
√ |
√ |
√ |
√ |
√ |
|||||
|
Leptospermum continentale |
Prickly Tea Tree |
Small shrub |
1-3 |
>500 |
√√ |
Prefers damp locations |
√ |
|||||||
|
Leptospermum coriaceum |
Green Tea Tree |
Medium shrub |
2-3 |
350-500 |
√ |
√ |
√ |
|||||||
|
Leptospermum lanigerum |
Silky or Woolly Tea Tree |
Medium-tall shrub |
2-4 |
>600 |
√√√ |
Best near natural (fresh) soaks; found mainly near Kingston area |
√ |
√ |
||||||
|
Leptospermum myrsinoides* |
Heath Tea Tree |
Small shrub |
0.5-2.5 |
>450 |
√ |
√ |
||||||||
|
Leucophyta brownii* |
Cushion Bush |
Small shrub |
0.5-1 |
400-700 |
OK for moderately saline sites |
√ |
||||||||
|
Leucopogon parviflorus* |
Coast Beard-heath |
Medium shrub |
2-3 |
>500 |
Fruits edible when ripe |
√ |
||||||||
|
Melaleuca acuminata |
Mallee Honey Myrtle |
Medium-tall shrub |
2-4 |
400-550 |
√ |
√ |
√ |
√ |
|
Melaleuca brevifolia |
Dwarf Salt Honey-myrtle |
Medium shrub |
2-3 |
250-700 |
√√√ |
Good for mildly saline and swampy sites; slow growing |
√ |
√ |
√ |
|||||
|
Melaleuca decussata |
Cross-leaved Honey-myrtle |
Small shrub |
1-3 |
450-600 |
√√ |
Flowers pink-mauve; prefers damp areas |
√ |
|||||||
|
Melaleuca halmaturorum |
Salt Paperbark |
Tall shrub |
3-8 |
>350 |
√√√ |
Excellent for very saline and swampy sites; slow growing |
√ |
√ |
||||||
|
Melaleuca lanceolata |
Moonah / Dryland Tea Tree |
Medium tree |
5-10 |
>250 |
√ |
Slow growing; good on limestone |
√ |
√ |
√ |
√ |
√ |
√ |
||
|
Melaleuca uncinata |
Broombush |
Medium shrub |
1-3 |
350-650 |
√ |
Good for mildly saline sites |
√ |
√ |
√ |
√ |
√ |
|||
|
Melaleuca wilsonii |
Violet Honey Myrtle |
Medium shrub |
1-2 |
500-600 |
√√ |
Mauve flowers; prefers damp sites |
√ |
√ |
√ |
|||||
|
Pittosporum phylliraeoides |
Native Apricot |
Small tree |
5-7 |
250-450 |
√ |
√ |
√ |
√ |
√ |
|||||
|
Xanthorrhoea caespitosa |
Yacca |
Small shrub |
1-2 |
>350 |
Slow growing |
√ |
√ |
√ |
√ |
√ |
Disclaimer
Use of the information in this Fact Sheet is at your own risk. The Department of Primary Industries and Resources and its employees do not warrant or make any representation regarding the use, or results of the use, of the information contained herein in terms of its suitability, correctness, accuracy, reliability, currency or otherwise. The entire risk of the implementation of the information which has been provided to you is assumed by you. All liability or responsibility to any person using the information is expressly disclaimed by the Department of Primary Industries and Resources and its employees.
| Windbreaks for the Upper South East | ISSN 1323-0409 |