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Forages for Reduced Nitrate Leaching, Brent and Maryn Austin (Canterbury)

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Farm facts Getting out of FRNL programme Deciding to join the programme Why do you think it's important? Farm & Industry Benefits Annual summary N leaching and drainage Fertiliser N applied and N uptake Demonstrations on farm Further information

Brent and Maryn, arable farmers from Mayfield, have actively contributed to FRNL's research, sharing knowledge and experiences to guide its direction. On their 552 ha farm, they mainly grow cereals and fodder crops. Their involvement with FRNL has led them to focus on the APSIM model's nitrogen fertiliser recommendations. You'll learn how crucial it is to trust these forecasts. Through computer modelling, they've understood nitrogen leaching effects, which led them to try different crop rotations. This page emphasises not leaving fields empty in autumn and winter, as it can increase nitrogen loss, impacting New Zealand's environmental image. Joining such programmes can enhance your farming methods by understanding nitrogen leaching better.


Brent and Maryn are arable farmers from Mayfield. They were part of a network of farmers in Canterbury who contributed to the direction of FRNL’s research, influenced priorities, shared experiences and provided a practical check to research.

Farm facts

Area:

552 ha

Dominant soils:

Templeton silt loam, Wakanui silt loam, Lismore stony silt loam

Dominant soils (sandy):

Eyre stony sandy loam

Average rainfall:

approx. 700 mm

Main crops:

cereals for grain harvest

Main crops (for stock grazing):

fodder crops; crop residues are grazed by sheep

Trading as:

Austin Farming Limited

What did you get out of the FRNL programme?

  • It has been good to be a part of the programme. We are particularly interested in the field tests being carried out comparing the APSIM model nitrogen (N) fertiliser recommendations with our current N rates. Getting the models right so that farmers can trust forecasts is really important.
  • I'm able to see the leaching losses of what I am doing through comprehensive computer modelling and in-depth soil N testing. This has encouraged me to try different crop rotations to mop up any leftover N before it is leached out of the soil profile.
  • The modelling has also shown what heavy rainfall events do to increase N leaching which in-turn shows the importance of not leaving paddocks fallow over the autumn and winter months.

Why did you decide to join the programme?

“The programme looked interesting and very relevant to what is happening with current environmental issues.”

Why do you think it's important?

"We all have to do our part to keep New Zealand’s “clean green” image for future generations and I see this programme as an important part to reduce N leaching into our waters."

How will farmers and the industry benefit?

“We should be able to farm with more confidence in the future by having more knowledge about N leaching and how we can reduce or mitigate our leaching. Hopefully we should be able to improve our cropping rotations to produce more from the same inputs compared to what we are currently doing.”

Annual summary of modelling study

Annual summary

The Simple Crop Resource Uptake Model operating within the Agricultural Production Systems sIMulator (SCRUM-APSIM) was used to simulate N balances at Brent and Maryn’s farm. APSIM predictions indicated that paddocks with high N leaching (≥30 kg N/ha) had greater residual soil N after the summer harvest.

Modelling outcomes of two seasons on the farm identified the following factors that increased the amount of leachable soil N:

  • application of N fertiliser in excess of crop N requirements,
  • mineralisation of N-rich crop residues,
  • paddocks remaining fallow during the high N leaching risk period (autumn-winter), and
  • “leaky” soils e.g. the free-draining Eyre and Lismore soils.

Leaching was greater when at least two of these factors were in play. For example, excessive N application to spring-sown crops resulted in high residual soil N at risk of leaching if no crops were sown after the summer harvest to take up the N. Similarly, mineralised N from residues retained in paddocks was available for leaching if there was no vegetation in autumn/winter to take up water and N to reduce drainage and N leaching.

N leaching mitigation options that reduced N leaching and increased gross margins included:

  • growing oats as a cover/catch crop on paddocks that remained fallow after summer harvest
  • using lower rates of fertiliser N for high soil residual N paddocks

When fertiliser N applications were modelled to match crop N demand (taking into account soil mineral N levels) without affecting yield and/or growing of catch crops, this resulted in a reduction in N leaching. These findings encouraged Brent to modify management in subsequent seasons. Demonstration paddock results supported the modelling of lower N fertiliser inputs and greater N use efficiency, and this translated into greater farm profitability and reduced N footprint.

Overall, results have shown that leaching is mainly influenced by rainfall through its impact on drainage, but farm management practices determine the amount of soil N at risk of leaching. Strategies that can reduce the amount of soil N available for leaching include: sowing catch crops immediately after the summer harvest to mop up residual soil N or N mineralised from soil organic matter and crop residues, and reduced N fertiliser use by calculating requirements with a recommendation system that accounts for soil mineralisation.

N leaching and drainage

The below table shows N leaching and drainage over five seasons (season = 01 Apr – 31 Mar) as estimated by SCRUM-APSIM at a depth of 150 cm.

Paddock ID Leaching (kg N/ha) Drainage (mm)
2014-15 2015-16 2016-17 2017-18 2018-19 2014-15 2015-16 2016-17 2017-18 2018-19
Camb A 45.8 22.1 8.6 13.5 - 271 167 144 351 -
Camb B 10.5 3.9 17.7 22.3 - 240 60 125 425 -
Camb C 53.5 9.2 22.7 32.2 - 316 97 260 442 -
Camb D 18.5 13.5 3.4 16.1 - 222 160 50 266 -
Dane A 16.3 14.3 0.4 20.9 9.4 177 156 21 317 160
Dane B 17.6 17.3 6.2 31.5 15.3 155 129 48 333 227
Dane D1 6.8 1.9 2.9 22.4 16.7 305 90 56 292 148
Dane D2 7.4 1.9 3.0 28.3 11.4 305 77 52 335 124
Dane E 23.6 7.0 0.2 27.9 5.9 197 44 2 264 273
Dane G 19.1 4.4 3.0 24.1 13.7 270 99 45 357 307
Dane JK 13.5 3.4 0.0 16.5 24.0 255 70 0 328 224
Dane ST 19.4 13.2 6.3 10.8 9.2 221 135 48 328 151
Dane W 38.2 19.1 24.9 29.6 4.5 226 91 110 355 127
Dane X1 57.2 1.8 0.7 5.6 10.8 565 66 22 296 313
Dane X2 14.6 2.5 0.6 4.9 14.2 324 78 17 410 306
Dane Y1 19.6 3.9 1.5 4.4 7.7 256 80 31 409 246
Dane Y2 22.2 8.2 0.8 13.2 15.4 216 74 7 282 219
Tav A 38.5 7.9 15.0 11.6 8.6 326 139 160 393 322
Tav A2 7.7 3.0 13.5 11.4 10.0 196 125 165 405 435
Tav AB - - - - 10.1 - - - - 265
Tav B 6.4 1.7 0.0 24.3 15.1 246 133 0 292 235
Tav B2 5.4 6.3 13.8 9.1 5.9 371 348 234 259 135
Tav C 19.2 1.3 0.1 5.8 3.6 246 45 8 242 126
Tav CD - - - - 4.3 - - - - 134
Tav D 6.1 1.2 2.0 14.0 13.9 232 71 236 327 123
Tav D2 6.1 2.7 1.1 32.3 16.3 232 146 30 293 162
Tav E 4.2 2.7 7.7 12.5 11.6 129 89 289 385 206
Tav E2 4.2 2.7 7.0 19.3 13.1 129 89 306 305 225
Tav F 6.6 1.2 3.1 13.4 11.3 336 85 76 438 254
Tav G 20.5 5.0 8.4 19.3 8.4 212 53 94 369 159
Tav H 25.3 19.3 33.9 17.3 19.7 205 70 223 404 284
Tav J 29.1 29.9 14.2 29.1 8.8 188 121 146 418 147
Tav K 15.0 10.7 14.9 13.3 10.7 176 107 124 318 156
Whole-farm average 20.2 8.5 8.0 17.9 11.3 247 105 101 347 209

Fertiliser N applied and N uptake

The below table shows fertiliser application and N uptake (as estimated by SCRUM-APSIM) over five seasons (season = 01 Apr – 31 Mar).

Paddock Applied fertiliser (kg N/ha) N uptake (kg N/ha)
2014-15 2015-16 2016-17 2017-18 2018-19 2014-15 2015-16 2016-17 2017-18 2018-19
Camb A 183 183 95 236 - 249 265 145 232 -
Camb B 229 30 83 182 - 176 122 262 161 -
Camb C 146 194 166 231 - 218 296 205 289 -
Camb D 183 204 89 70 - 266 190 131 81 -
Dane A 196 183 164 246 274 247 194 140 347 241
Dane B 181. 204 124 276 230 224 191 211 262 218
Dane D1 229 201 150 230 105 231 270 227 178 223
Dane D2 229 201 143 115 151 225 280 250 113 202
Dane E 229 133 176 68 83 242 206 225 132 137
Dane G 104 201 210 303 388 96 280 230 427 258
Dane JK 229 183 92 253 184 204 258 231 258 199
Dane ST 181 194 30 21 162 191 210 119 75 291
Dane W 229 201 114 159 158 232 252 178 254 232
Dane X1 100 114 184 184 227 114 193 184 232 268
Dane X2 196 198 135 184 227 178 116 289 192 284
Dane Y1 247 23 120 197 205 276 70 255 174 201
Dane Y2 247 275 99 230 23 101 314 340 239 119
Tav A 167 240 152 184 0 192 252 181 165 36
Tav A2 167 240 152 147 - 195 259 196 234 -
Tav AB - - - - 243 - - - - 219
Tav B 167 215 47 170 231 153 265 68 269 199
Tav B2 167 229 92 101 231 148 315 131 218 215
Tav C 137 158 89 23 297 110 185 171 125 302
Tav CD - - - - 92 - - - - 198
Tav D 167 206 229 66 21 175 140 352 235 152
Tav D2 167 200 184 205 44 186 255 251 231 259
Tav E 220 161 184 235 205 283 164 278 241 232
Tav E2 220 161 92 0 205 318 171 209 275 232
Tav F 181 193 30 138 231 160 174 265 145 274
Tav G 90 182 257 218 134 150 190 302 315 245
Tav H 196 137 0 293 251 198 197 36 304 255
Tav J 134 194 143 0 205 128 325 157 106 289
Tav K 0.0 201 152 134 257 34 321 163 194 380
Whole-farm average 178 165 124 166 185 181 206 193 196 227

Demonstrations on farm

2017 – oats and faba beans as catch crops

Crops sown in autumn, following summer cropping, or sown in winter, following grazing of forage crops, can be very useful in mopping up residual mineral N from the soil and therefore reducing the risk of N leaching during winter and spring. The key to maximising the benefit is to plant a catch crop as early as practical and to select a winter-active species.

A grazed fodder beet paddock had oats and faba beans sown as catch crops on 26 May 2017 and these were compared to a fallow in an unreplicated demonstration. The cover crops were in the ground for three months, with dry matter cuts taken on 7 September 2017 prior to the sowing of a spring barley. Due to the wet winter conditions the catch crops were slow to establish. Even though overall yields were low, soil mineral N levels in September were higher in the fallow and indicated that around 25 kg/ha of N was mineralised (see below table). Changes in mineral N for the two catch crop treatments are a net result of N mineralisation (increasing mineral N), crop N uptake and immobilisation of N during the decomposition of the residual fodder beet. These numbers suggest that there was greater immobilisation in the presence of catch crops, despite the low yields.

Catch crop yields (t/ha), N uptake (kg N/ha), baseline and harvest profile soil mineral N (kg/ha); soil sampling dates 30/5/17 and 7/9/17 respectively.

Paddock Pervious crop Catch Crop sown Baseline profile soil mineral N (kg/ha) Harvest profile soil mineral N (kg/ha) Catch crop yield (t/ha) Catch crop N uptake (kg/ha)
TAV B Grazed fodder beet Faba beans 66.2 51.3 0.34 17.12
TAV B Grazed fodder beet Oats 60.9 42.2 0.06 4.83
TAV B Grazed fodder beet Fallow 39.7 63.1 - -

2018 – autumn barley vs fallow then spring barley

Autumn sown barley was compared to leaving the paddock fallow (i.e. prior to sowing spring barley) to see how much N the autumn sown barley takes up prior to fertiliser being applied. Barley (Tavern) was sown 10 May 2018.

Autumn sown barley was shown to utilise N which would otherwise be at risk of leaching, compared with fallow and spring sown barley. Autumn barley also has the potential to decrease spring N leaching losses as it will be well established compared to an August or September sown crop and able to take up more N.

Note: Brent’s experience of sowing barley earlier, instead of having a winter fallow, is that this can be risky as there are no true winter barleys and if it does not get established well due to unfavourable establishment conditions the spring sown crops will yield better.

Baseline (1 June 18), 11 July and 22 November soil mineral N (kg/ha) from the fallow and autumn sown barley (0-60 cm).

Further information

An article relating to the SCRUM-APSIM modelling work was published in Agronomy NZ.

A full report on the arable monitor farms, including the detailed results of the catch crop demonstrations on this farm and at Chertsey, and an N fertiliser rate demonstration on another arable monitor farm.

Last updated: Aug 2023
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