Cropping Wind erosion Prevent valuable soil from blowing away Failure to take steps to maintain soil cover can accelerate topsoil losses caused by wind erosion, particularly during late spring and summer when soil cover is at a minimum. This article outlines farming and grazing management methods that can minimise wind erosion and its impact on farm production. by John Leys, CENTRE FOR NATURAL RESOURCES, DEPARTMENT OF INFRASTRUCTURE, PLANNING AND NATURAL RESOURCES T here is no single recipe for controlling wind erosion but steps can be taken to protect soil resources. There are three basic control methods maintaining ground cover, surface roughening and chemical bonding. Ground cover (pasture, stubble and weeds) needs to be more than 50 per cent (as measured when cover is flattened). Shrubs and grass tussocks more than 100 millimetres high need to be spaced no more than three times their height when they are distributed evenly across the paddock. Surface roughening (soil clods and tillage ridges) need to have 50% of the surface covered with soil clods more than 20mm in diameter and tillage ridges about 100mm high. Surface roughening with clods is best suited to loam and clay textured soils and not This space is deliberately blank 36 Farming practices that maximise residue conservation such as retaining stubble and maintaining a surface-roughened paddock can help reduce wind erosion. sands, which are best suited to ridging. Chemical bonding requires the entire eroding area to be treated with enough bonding material to stop any erosion. How wind erosion works Wind erosion results in soil and nutrient loss, scalding, reduced water infiltration and the burying of on- and off-farm infrastructure. It can also affect health, reduce visibility and disrupt electricity supplies. Wind erosion occurs when the force of the wind exceeds the resistance of the soil surface. On-farm, the most damaging wind erosion process is saltation, which occurs when soil particles, sized 0.10.5mm, are bounced across the surface by the wind. As the saltating particles crash into the surface, they splash up more particles that also bounce across the surface. This bombardment of the surface causes an avalanche that spreads out in a fan shape, with more and more soil particles being moved downwind. Off-farm, the most damaging wind erosion process is dust, which occurs when particles less than 0.1mm are carried off-farm by the wind. Larger dust particles (0.10.05mm) are often dropped within a few kilometres of the erosion site. Smaller particles (less than 0.005mm) travel thousands of kilometres and are only washed out of the air by rainfall. The erosion rate of a paddock will change downwind and will be different at the start and end of the erosion event. The amount of soil being moved by wind erosion increases downwind until it reaches a maximum. For sandy soils, erosion can start 200mm downwind and reach the maximum erosion rate in about five metres from where the erosion starts (such as the edge of a paddock). The erosion rate of a paddock will increase to a peak as the surface is bombarded by eroding particles, then slow to equilibrium. This occurs because as the erosion continues, the surface starts to armour up. This amouring layer comprises mainly of soil Strip ripping at 750-millimetre spacing can catch bouncing soil particles to reduce erosion. The foreground of the photograph was ripped at six kilometres per hour, while the background was ripped at 13km/h which gave more clod. Inset: 50mm ripper points were used for strip ripping. FA R M I N G A H E A D No. 140 September 2003 Wind erosion Cropping particles that are too large for the wind to blow away and of the remaining ground cover. Armouring layers are a sign that significant soil has already been lost because it is formed when the finer particles in the top few millimetres have blown away. If the armouring layer is disturbed then there is the potential for increased soil loss of newly exposed soil. Prevention is better than cure In most sandy soils, it is difficult to control wind erosion after it has started. Prevention is the best control method, especially in sandy soils where mechanical and binding methods are either less effective or too expensive (more than $500 per hectare). Sandy soils tend to have little soil structure and as such are better protected by ground cover. On cropping paddocks, adopt farming practices that maximise ground cover and reduce soil pulverisation. On grazing land or fallow paddocks, destock early and keep ground cover at more than 50%. Rabbits are particularly destructive of vegetation and loosen the surface when digging for food. If erosion is already a problem, do not use warren ripping because it loosens soil. Baiting and fumigation are preferred options for rabbit control in these conditions. In sandy or sodic soils, it is an advantage to throw up a ridge (requiring a wide point or delver) as well as a clod. Pictured left is a 50-millimetre ripper point with delver for throwing a ridge in loose soil and pictured right is a 50mm point with a Turlec wing. Goats and kangaroos also can reduce ground cover and need to be managed to ensure cover does not drop below the critical level. Preserving ground cover Maintaining more than 50% ground cover is the preferred method of erosion control. If erosion does start on a paddock, then try to maintain any remaining ground cover. Ground cover helps to control erosion by: Acting as a blanket that prevents the wind from picking up any soil particles. Absorbing the force of the wind and reducing the wind speed at ground level. This space is deliberately blank FA R M I N G A H E A D No. 140 September 2003 37 Cropping Wind erosion many clods. Incorporate ridging into control measures. Tillage ridges need to be about 100mm high and cover the entire erosionprone area. Ridges less than 100mm quickly fill with sand and if more than 100mm the ridge crest tends to erode quickly. Loam and clay soils provide better results with surface roughening. Treat the entire eroding area plus some additional buffer areas. Start roughening on the upwind edge and work downwind if the landscape is flat. On slopes, roughen on the contour. Methods of surface roughening include strip ripping and cultivation. Cultivation with insufficient clod and low ridges created with 250-millimetre points on 230mm spacing (left), while 50mm points on a chisel plough with 305mm spacing created good clod cover (right). Trapping eroded soil particles and reducing the amount of bombardment in the soil surface. Aim to keep ground cover (stubble, weeds, pasture and crop) at more than 50% when viewed straight down. Stubble, plants, grass butts or small bushes (higher than 100mm) that sit up into the air offer even more protection and mean slightly less cover will be required. Protection from bushes and tussock-type grasses occurs when the spacing between the plants is no more than three times their height, distributed evenly across the paddock. Surface roughening Surface roughening helps to control erosion by covering more than 50% of the soil surface with clods that are too large (more than 20mm) to be lifted by the wind. Extra roughness can be made with tillage ridges and furrows that can trap any loose soil that may be moving. Consider using this method only when there is insufficient vegetation to protect the soil surface (less than 50%) or the soil type produces sufficient clods to protect the surface. Sandy soils are not suited to surface roughening alone as they do not produce This space is deliberately blank 38 Strip ripping Strip ripping can be used to catch the bouncing particles before the soil erosion rate reaches its maximum. This has the advantage that the entire paddock does not need to be cultivated. A ripper penetrates the surface to a depth of 100200mm and creates a furrow lined with cloddy material. The aim is to create clod that covers the loose material and catches any moving particles. Spacing of the rip lines is critical. Since erosion can reach its maximum rate in less than 5m, space out rip lines to no more than 2m apart (for example, 750mm). If erosion has started or the area receives erosive winds from different directions, rip lines need to be close together and work best when the entire surface is covered in clod. Extra rip lines can be placed between the first lines or ripped at right-angles if they fill with sand and a second treatment is necessary. In sodic soils, rainfall will disperse clods, reducing roughness and requiring follow-up ripping. In sandy or sodic soils, it is an advantage to throw up a ridge as well as a clod as this will last longer than just a rip line. To throw up a ridge a wide point or delver is required. Factors to be aware of when strip ripping: On sloping ground, rip lines may concentrate water and result in gullies. When insufficient clod is produced during ripping, rip lines simply provide more fresh soil to be eroded. On soils with salty, sodic or acid subsoils, rip lines may turn over soil that will reduce crop and pasture growth in the future, so be careful not to bring subsoils to the surface. When rip lines fill with sand, they form a ridge that is difficult to level out after the erosion season finishes. The aim is to have enough rip lines to limit sand drift and the ridges catch all the loose sand. In rangelands, rip lines may remove valuable grass butts and fodder bushes, making an ideal environment for woody weed infestations. Plan carefully to minimise damage to existing vegetation. FA R M I N G A H E A D No. 140 September 2003 Wind erosion soil surface to form a crust that inhibits soil movement. The method is expensive and is best only considered if capital improvements or highvalue crops are threatened. In New South Wales, if the ground cover consists of more than 50% naturally occurring native vegetation, consent for clearing by ripping may be required under the Native Vegetation Conservation Act (1997). If unsure, contact the local office of the Department of Infrastructure, Planning and Natural Resources before starting ripping or cultivation. In other States, check with relevant State or local authorities as to whether any consents are required. Cultivating land For rough or ridged surfaces to be effective traps, they need to be made of clods that are too big to be eroded by the wind and ridged enough to catch moving sand. The aim is to keep the soil rough and ridged to either prevent any movement in the first place or to trap bouncing soil particles quickly in the surface depressions. Soil clods more than 20mm should comprise more than 50% of the soil surface, otherwise erosion will start again. Cultivate a trial area to determine the correct surface conditions are being created before attempting to cultivate the entire eroding area. Tined implements such as chisel ploughs and scarifiers with narrow (50mm) points penetrate soil well and provide good clod. Cropping A surface with good ridge and clod formation was created using 50-millimetre narrow points at 900mm spacing on the first row and 150mm points on the last two rows at 450mm spacing. If implements cannot penetrate dry soil, wait for moist soil conditions. To modify implements remove every second or third tine to decrease draft. Using narrow points (50mm) at 900mm spacing on the first row and 150mm points on the last two rows at 450mm spacing has produced good clods and ridges. Chemical bonding Chemical bonding agents can cement the surface temporarily. These are sprayed on the Managing land after rainfall After rainfall, soil crusts form that reduce erosion. If the crust or paddock roughness and ridging is still adequate, no action is required. But if the crust has sand grains on the surface or the clods and roughness have been flattened, it may be necessary to re-roughen the surface as the crust will break down through erosion from the loose sand grains. The most common mistake with all remedial measures is restocking the treated area too soon. Prevent livestock from entering a treated or eroding paddock until there is enough vegetative cover to control erosion (more than 50% cover). Keeping livestock out also increases the ability of the soil crust and clods to control erosion. About the author John Leys is with the Department of Infrastructure, Planning and Natural Resources, Gunnedah, NSW Email: [email protected] Phone:(02) 6742 9509, Fax: (02) 6742 3129. This space is deliberately blank FA R M I N G A H E A D No. 140 September 2003 39
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