A NSW Government website

WA Northern Regional Summary


The region

A map showing the locations covered by this region

The WA Northern agroecological zone extends Kalbarri in the north to Coorow in the south. Rainfall in the zone ranges from > 600 mm annum-1 in the west to < 400 mm annum-1 in the east. Rainfall seasonality ranges from winter-dominant in the south to seasonally neutral in the north. Boundaries for the zone are shown in Figure 1.

Modelling regional practices

Producing models that reflect all farming practices throughout a region is difficult so “common practice” models for wheat, canola and lupins for the region were produced. A wheat crop with a 1.6 t ha-1 yield and 34 kg of fertiliser N applied ha -1, a canola crop with a yield of 0.9 t ha-1 with 60 kg fertiliser N ha -1 applied and a lupins crop with a yield of 1.4 t ha-1 and 0 kg of fertiliser N ha -1 applied were modelled. The key assumptions of these models were that;

  • Only one pass was made at sowing
  • Split fertiliser applications were used for wheat and canola crops
  • It was assumed that wheat and canola crops had two fallow sprays and lupins crops had three. It was also assumed that wheat and lupins had one in-crop herbicide application and canola had two. Canola and lupins also had a pesticide application.
  • Stubble was retained
  • Lime was applied at the equivalent rate of 4 t ha-1 every decade and incorporated through scarification

Impact indicators

Hydrogen ion impacts estimate the release of hydrogen ions to the soil associated with crop production. A negative value indicates a reduction in soil acidity whereas a positive value indicates an increase in soil acidity. Soil erosion is an estimate of soil loss that occurs during the production of the crop. The depth of soil lost will depend on many things but an approximate conversion is that 1.5 t of soil loss equals 1 mm of soil. Global warming impacts are the release of greenhouse gases to the atmosphere expressed as carbon dioxide equivalents (CO2-e), Eutrophication impacts are the release of phosphorous to the environment and are expressed as phosphate equivalents and Particulate Matter impacts are the release of fine particles less than 2.3 micrometres in diameter.

Benchmark results

Results below in Table 1 show the environmental impacts of producing a t of wheat, canola or lupins in the region. Lime use in the region resulted in a reduction in free hydrogen ions in the soil for all crops and soil erosion was estimated at between 3.4 and 6.7 t soil loss t product-1. Analysis indicated that Global warming impacts associated with the production of these crops ranged from between 190 and 733 kg CO2-e, Eutrophication impacts ranged between 1.1 and 3.8 kg PO4-e and Particulate Matter impacts ranged between 0.25 and 0.83 kg of < 2.3 µm particulate matter t product-1.

Table 1: Hydrogen ion changes, soil erosion and Global Warming, Eutrophication and Particulate matter impacts associated with the production of wheat, canola and lupins in the WA Northern agroecological zone.

 

Hydrogen ions

Soil erosion

Global warming

Eutrophication

Particulate matter

 

(kg H+)

(t soil loss)

(kg CO2-e)

(kg PO4-e)

(kg PM2.3)

Wheat

-220.79

3.35

412.49

1.99

0.43

Canola

-422.75

6.46

733.25

3.83

0.83

Lupins

-449.60

6.70

190.12

1.12

0.25



Greenhouse gas emissions

The emissions profile of all three crops are shown below in figure 2. For all crops, the greatest sources of emissions were the production and use of fertiliser. Emissions associated with the breakdown of residues were the next greatest emissions source.

Figure 2: Greenhouse gas emissions profile for the production of wheat, canola and lupins in the WA Northern agroecological zone.

Greenhouse gas mitigation strategies

Mitigation strategies tested for the region were;

  • Sustainable intensification
  • Additional applications of lime
  • Implementation of variable rate fertiliser technology
  • Changing a wheat-wheat rotation to a legume-wheat rotation

More information on the assumptions used to test these strategies and how they might reflect individual enterprises are available on the Mitigation strategies page.

Results (figure 3 below) indicate that emissions of a t of wheat can be reduced by;

  • 85% through the implementation of sustainable intensification
  • 24% by additional lime applications
  • 13% by implementation of variable rate fertiliser technology

Results also indicate the replacing a wheat crop with a legume crop in a two-crop rotation can increase greenhouse gas emissions intensity by 104%.

Figure 3: Reductions in greenhouse gas emissions for wheat production when grown with sustainable intensification, variable fertiliser, additional lime applications and legume - wheat mitigation strategies in the WA Northern agroecological zone

 

Accessible Content

Accessible versions of the raw data used to generate these charts is below.


Greenhouse Gas Emissions Profile

Wheat

Canola

Lupins

Lime production

6.304369

8.405826

12.60874

Lime use

10.69201

14.25601

21.38402

Fertiliser production

112.6365

226.385

126.9062

Fertiliser use

136.1822

289.3152

0

Residue emissions

54.9992

80.29434

78.67765

Transport

6.489579

9.712111

12.45376

Tractor operations

40.36393

53.17628

79.78168

Chemical production

44.81767

51.87345

97.52687

Calc total

395.489

710.7564

395.3462

Mitigation Strategies

StrategyResult

Sustainable intensification

-85

Legume wheat rotation

104

Additional lime applications

-13

Variable rate technology fertiliser

-24