Soil erosion after a bushfire can impact your farm. Small-scale erosion control can help to limit further soil loss and aid recovery.
Farm-scale erosion control
Read transcriptCommon types of erosion after bushfire
These types of water erosion may increase in risk after bushfire:
- gully erosion
- sheet erosion
- streambed and streambank erosion
- existing erosion.
Burnt areas are more erosion prone due to lost tree canopy and groundcover (living vegetation and dry matter). The chemistry and structure of the soil may also have changed in these areas and could be hydrophobic (unable to absorb water).
Farm-scale erosion control after bushfire
The key to minimising erosion after a bushfire is to retain or re-establish groundcover.
Ways to do this include:
- destocking burnt areas
- installing sediment traps in water flowlines or across steep slopes
- hand broadcasting seed
- avoiding further disturbance
- monitoring groundcover and plant regeneration
- seeking expert advice if gully erosion is activated/re-activated.
Impacts to infrastructure
Dams, roads and fences can be impacted by organic matter, ash and debris washed from the fireground.
High levels of run-off can overwhelm pipes under roads, causing overtopping which damages surfaces and erodes road material.
Organic matter, ash and debris can wash over unburnt paddocks into farm dams at some distance away from the fireground and higher rates of runoff can damage fencing by trapping debris.
Broader landscape impacts
Organic matter, ash and debris flowing off properties can impact:
- the environmental values of waterways
- animal and plant habitat
- pollute drinking water catchments.
The water quality of major waterways can be severely impacted a long way from firegrounds.
Increased run-off and large debris can also cause further erosion downstream.
Erosion control techniques
These are some of the low cost and relatively low labour options for small-scale control structures:
- coir logs
- silt fence
- jute mesh
- seedlings
- straw bales
- revegetation
- cover crops
- rock
- large woody debris.
Tubestock or seedlings can also be planted into coir logs.
Place burnt tree trunks or large branches across slopes to trap sediment and debris.
Use hardwood stakes on steep slopes to secure them in place.
Rushes and sedges may be useful in moist areas including species like:
- Carex
- Juncus
- Lomandra.
Jute mesh and straw bale erosion control
A head cut is protected by a combination of techniques, with jute mesh pinned down by straw bales to stop fast flowing water from causing further erosion.

Coir logs and woody debris erosion control
Coir logs and large woody debris are pinned across a steep slope to slow water and trap debris and sediment.

How to prioritise erosion control works
The key factors for determining where to focus efforts and what structures to design include:
- soil type and steepness of slope
- fire intensity and groundcover condition
- catchment size above structure location
- size of flowline or order of creek
- proximity to dams, wetlands and waterways.
Soil type, slope and fire intensity can change the level of erosion risk. You can use this information to help prioritise erosion control works on your property.
Fire intensity depends on many factors, including:
- fuel loads
- temperature
- wind speed and direction.
This table shows how the steepness of a slope and the intensity of a fire, can change the level of erosion risk.
| Fire impact | Flat to shallow slopes | Moderate slopes | Steep slopes | Very steep slopes |
|---|---|---|---|---|
| 0-5% slope | 5-10% slope | 10-20% slope | >20% slope | |
| Cool-Moderate burn | Low | Low | Medium | Medium/High |
| Hot burn | Low | Medium | High | High |
| Very hot burn | Low/Medium | High | High | Extreme |
This table shows how the steepness of a slope and the soil type can change a farm's level of erosion risk.
| Soil landscape | ||||
|---|---|---|---|---|
| Flat slopes | Moderate slopes | Steep slopes | Very steep slopes | |
| Basalt soil | 130 Low | 235 Low/Moderate | 540 Moderate | 900 Very high |
| Grey loam soil | 130 Low | 270 Low/Moderate | 700 High | 1,000 Very high |
| Granite soil | 130 Low | 310 Moderate | 800 High | 1,200 Very high |
- All numbers above are calculated as tonnes/hectare (t/ha).
- 1200t/ha is equivalent to a loss of 12mm of soil.
- Dispersive (sodic - or that which contains sodium) soils and other inherent limitations may increase the risk of erosion.
- Where the risk of erosion is high-extreme, avoid undertaking risky practices such as ripping, clearing or even just tracking machinery.
Where to place structures in the landscape
Important things to consider when you are placing structures include:
- rock and large woody debris from on-site can also be used in head cuts or holes
- slowing water will help to retain sediment
- seeding or planting can improve stability but take care with selection of the species to avoid introducing exotic species to fire affected areas unless already present
- an option for seeding is to broadcast sterile cover crops such as rye corn to re-establish groundcover quickly on small erosion-prone areas
- the catchment size and likely flow volumes should come into play to design suitable road drainage when constructing new roads
- roll over banks constructed across slopes can carry run-off but must spill into thick groundcover to avoid erosion occurring off the road
- there are modified fencing designs available to use in flood-prone areas, for example drop-down fencing and using plain wire rather than hinge joint.
Roll over bank placement
The blue arrow in the photo points to a suitable place for a roll over bank to be installed that should reduce water erosion down the steep slope.

Head cut formation
The blue arrow points to a place where a head cut is forming after a very hot burn and when soil has washed away. This is an ideal place to put a protective structure.

Heavily eroded gully
Blue arrows point to two places in this heavily eroded dry gully, with a larger catchment size where multiple structures may be needed to be placed.

Groundcover management
The speed of pasture recovery will depend on the rainfall patterns in the months following fire. Exposed soil may make the land more vulnerable to wind erosion and invasion of weeds.
To help predict pasture recovery after fire, consider watering small test areas several times to see what regrows. A poor response may indicate that new pasture may need to be sown, but it is best to wait for adequate rainfall before making any decisions.
If the pasture was highly weedy and/or degraded prior to the fire, consider sowing annual forages to help provide groundcover, such as:
- oats
- wheat
- grazing brassicas.
This will also assist with weed control prior to sowing a new pasture in future.

The heat of the fire will impact the ability of the soil to recover. Different levels of burns include:
- a cool-moderate burn where most dead plant material is burnt, some seed, perennial grasses and clovers survive. Usually, a small residue of unburnt pasture remains.
- a hot burn where all dead plant material, many seeds, young and weaker perennial grasses destroyed. Topsoil usually appears charred and bare.
- a very hot burn where soil is virtually sterilised. All plant material and seed are destroyed as the fire burnt into the top organic matter layer of the soil. Usually under tree cover.
Grazing practices after bushfire
It can take some time for pastures to return to pre-fire (and pre-drought) condition.
Reducing stocking rates or using stock containment areas can enable pastures to rest and start to recover through a growing and seed-setting season.
This will allow the seed to set to replenish the seed bank and allow the plant to re-establish its root reserves, both of which will result in faster pasture recovery.
Pasture recovery after bushfire
The post fire period may be a good opportunity to control persistent weeds and rejuvenate pastures through a combination of:
- strategic spraying
- application of fertiliser or ameliorants
- re-sowing in perennial improved pastures.
Agronomic advice should be sought to help make the most appropriate decisions for your landscape context and type of farming enterprise.
If your pastures were largely native grasses prior to burning, they will recover given time- often much more efficiently then improved exotic pastures.
If you want to change your native pasture system to an exotic, improved pasture, it may involve getting permission for native vegetation clearing under the Native Vegetation Code.
Local Land Services can provide advice on your specific circumstances.
Monitoring
Monitoring your property for weed invasion, pest animal activity and worsening erosion is especially important after bushfires.
Monitoring for weeds
Early identification and control before seed-set are the most important steps in weed control and eradication.
Perennial weeds with deep root systems are likely to survive bushfire and regrow, however their seed bank may be depleted. Weeds are some of the first plants to recover and are often prominent after bushfires, including:
- flatweed
- docks
- sorrel
- onion grass.
These weeds provide a short-term groundcover but may need to be controlled in time.
In bushland contexts, weeds suited to disturbance may regrow quickly in the following areas:
- on forest margins
- in waterways
- along tracks
- on containment lines.
The post-fire period may provide an opportunity to reduce weed infestations in these areas. If identified at the seedling stage, many weed species may be hand pulled. Other bush regeneration techniques may also be used.
The post-fire period may also be a good time to establish competitive pasture, like phalaris, cocksfoot and sub clovers in pastures with high infestations of difficult perennial weed grasses like Chilean needlegrass, serrated tussock and African lovegrass.
The type of land will determine if cultivation or no till methods of seed broadcasting are appropriate, and which species may establish effectively.
Be vigilant about monitoring areas where stock feed has been introduced, and earthmoving machinery has been operating.
Monitoring for pest animals
Controlling pest animal species (both herbivores and carnivores) is a crucial post-fire management activity.
From an erosion control perspective, grazing species including rabbits, pigs and deer may destroy regenerating groundcovers, compact or disturb the soil further and may place additional pressure on erosion control structures.
Local Land Services provides advice and assistance in controlling pest species, developing vertebrate pest management plans and cooperative management programs. Local Land Services can:
- coordinate group pest animal control programs
- provide vertebrate pest management training
- provide baits to control pest animals.
Monitoring erosion control structures
It is important to see if erosion control structures are trapping sediment and groundcover is re-establishing.
Keeping a photo record of these sites is helpful.
If safe to visit, look at how the structures are performing during periods of heavy rainfall. Ask yourself the following questions:
- are the structures working in slowing the speed of the flow?
- are they secure or being dislodged or undercut by heavy flow?
- are structures needed in other areas?
Contact Local Land Services NSW
Our team welcome your enquiries, feedback and comments.
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