Farm facts

• Area: 430 ha effective, 440 ha total
• Dominant soils: Wakanui silty loam, Claremont silty loam over clay, and Cairnlea silty loam over clay.
• Average rainfall: approx. 800 mm
• 163 ha under pivot irrigation
• Crops grown include kale and fodder beet for winter feed, followed by catch crops, and Pasja, leafy turnips, rape, giant rape and maize for autumn feed.
• Animals:
• 2000 breeding Longdown ewes
• 23 breeding South Devon x Angus cattle (before 2017)
• Additional beef calves, R1 dairy heifer and winter dairy cow grazers

What did you get out of the FRNL programme?

• On farm, AgResearch provided some in-depth measurements of pasture growth and composition throughout the year, through the use of pasture cages and c-daxing.
• Being able to visit other properties in the group, seeing different production systems and mixing with some top farmers has been of value.
• Being able to offer a practical view to some research ideas has also been of benefit.

Why did you decide to join the programme?

“As we have winter dairy grazing by the river, we want to know the environmental impact of that and also want to be involved in finding solutions.”

Why do you think it's important?

"As time goes on, focus is shifting more on the environmental sustainability of our business. This has significant implications for society’s perception of the industry and our marketing."

How will farmers and the industry benefit?

“The programme discovered what improvements can be made at the small scale first. Now this can be filtered out to the wider community.”

Annual Summary

Irrigation has a marked effect on the management on farm and ability to cope during droughts. This has a notable effect on stocking rates and nitrogen (N) leaching.

Estimated N leaching increased over the monitoring period (see table below). This was due to an increase in winter grazing and a steady increase in the total amount of dry matter produced and consumed on the farm (2.8 million kg to 3.6 million kg). The area under irrigation also increased producing more herbage with an accompanying increase in stock density from 13 to 19 SU/ha. An increasing proportion of the dry matter was also consumed by dairy cows.

Winter fodder crops were identified as a large source of N leached from the farm and produced 15-20% of the dry matter intake. These are grown on a small proportion (<10%, or 44 ha) of the farm and the timing and intensity of grazing contribute to the higher N leaching losses. Catch crops were found to be the most appropriate solution to the problem.

¹ "Beef" means both beef carcass and that leaving the farm as live weight gain on grazed dairy cattle.
² Weighted average from Farmax (potential + fertiliser N boosted)

• Weather information

  

  Weekly rainfall (blue bars), air temperature (max dashed line, min dotted line) and soil temperature (solid line) from July 2013 to June 2019 based on interpolated weather data from NIWA’s Virtual Climate Station Network (https://www.niwa.co.nz/climate/our-services/virtual-climate-stations)

  

  Average soil moisture assessments from two pastures.

Management and experience with implementing FRNL options

• Plantain and chicory in diverse mixtures

  • Diverse pastures were only transient under sheep and beef grazing and rapidly transformed into grass-dominant swards.
  • Pastures containing plantain were relatively productive in autumn, but most would need a greater proportion of plantain in the herbage to mitigate N leaching.
  • Plantain may persist better on dryland sloping country where there is less competition.
  • Ideas which emerged from this study due to the lack of persistence of plantain were that it could be utilised in pure swards (e.g. for autumn feed for dairy heifers) or could be sown with rape as an autumn feed to help reduce N leaching.

  Plantain and chicory were incorporated into diverse mixtures on the farm following discoveries around their potential to help reduce N leaching. Mixed pastures produced more than those predominantly in grass whether irrigated or not.

  Total dry matter production (kg/ha) assessed using pasture cages from 6 Sept 2017 to 6 Sept 2018 (2017-18), and 6 Sept 2018 to 28 May 2019 (2018-19).

  Name	Water	Slope	Species	DM kg/ha
  				2017-18	2018-19
  Wacca	irrigated	Flat	Grass	15,082	12,042
  Mushroom 2	irrigated	Flat	White clover & chicory	20,900	13,456
  Stable 2*	irrigated	Flat	Grass-white clover-plantain	16,387	16,641
  Stable 2*	irrigated	Slope	Grass-white clover-plantain	15,658	15,777
  Boomerang	unirrigated	Flat	Grass	7,596	9,722
  Rutherford	unirrigated	Flat	Grass-white clover-plantain	8,760	11,433

  *Stable 2 has flat and sloping terrain in one paddock which was sown with the same mixture.

  As shown in the figure below clover and chicory vanished from this pasture within two years of sowing. It is possible that sheep or cattle grazing these pastures targeted the plantain or chicory and grazed them out, or the presence of N gave the grass a competitive advantage.

  

  The species composition of a pasture sown with grass, clover and chicory.

  Plantain was present particularly in the unirrigated pasture. It was also noted that in one paddock ("Stable 2") that there was more plantain on sloping ground (10%) than on the flatter area of the irrigated paddock (<1%). This led to the cautious suggestion that plantain will be more competitive on drier sites compared with the other species sown here. Grass had become the dominant species in all swards by the following year, with the exception of the paddock sown only with clover and chicory. Loss of clover and herbs from these pastures would reduce herbage quality.

  When examined more closely, the proportion of plantain on different topography, and different irrigation conditions showed that for the irrigated slope plantain became a modest proportion of the herbage in late summer and early autumn. In February this area had 30% plantain which is the level at which it has been found to mitigate N leaching. However, the flat areas had very little. The unirrigated area sown in 2016 had more than 30% plantain for much of the period measured and could be expected to reduce N leaching. In this paddock, the plantain had re-established itself from seed following summer drought, whereas other species had not.

  

  The proportion of plantain recorded in samples from three pastures.

  The figure below shows that there was little growth of any of the pastures between May and September.

  • Without irrigation the production would have been lower in total and much more seasonal in 2018.
  • White clover and chicory would be good for finishing stock in the spring and summer, but other pastures are required to feed stock in autumn.

  

  Pasture growth rates for irrigated vs unirrigated pastures from Sept 2017 to May 2019.

• Fodder crops

  

  Kale fodder crop

  • Winter and autumn-grazed fodder crops were identified as a large source of N leached from the farm. This is due to the high grazing intensity at a time of year with the greatest risk of N leaching.

  Fodder beet and kale fodder crops are grown in rotation as winter feed for adult dairy cows each year. Crop yields were monitored for the five years between winter 2015 and 2019 as shown in the tables below. Fodder beet gave consistently high yields (17.5 to 33.3 t DM/ha) under irrigation, whereas kale had lower yields (4.3 to 16.1 t DM/ha). N leaching losses were estimated with Overseer for fodder crops in the 2017-18 and 2018-19 seasons.

  Fodder beet production (kg DM/ha) during five years of observation

  Paddock	Date	DM (kg/ha)	Area of paddock (ha)	N leaching losses (kg N/ha)
  Collard Pie	10/6/15	29,521	4.08
  Railway pivot	13/5/16	24,589	16.83
  Mushroom 1 Mushroom 2	13/5/16 13/5/16	26,491 29,608	4.77 4.59
  Leader pivot	2/5/17	24,139	9.61
  River pivot	2/5/17	25,156	9.61
  Bridge	7/6/18	17,570	7.41	252
  Collard	7/6/18	33,392	4.99	59
  Half-moon & Highway	17/6/19	29,977	4.47	37-58
  Sisters	17/6/19	18,357	4.63	14

  Kale production (kg DM/ha) during five years of observation

  Paddock	Date	DM (kg/ha)	Area of paddock (ha)	N leaching losses (kg N/ha)
  Derry Hill	22/4/15	4,286	5.10
  Derry Hill	1/4/16	10,077	5.10
  Leader pivot (irrigated) Leader (unirrigated)	10/8/16 10/8/16	6,090 4,332	7.40 (7.40)
  Killer shed	2/5/17	11,587	5.24
  Sisters	2/6/17	6,748	4.15
  Railway pivot	7/6/18	16,117	16.83	49 (irr) 8 (dry)
  River pivot	7/6/18	10,861	9.61	190 (irr) 109 (dry)
  Railway pivot Bridge River pivot	17/6/19 17/6/19 17/6/19	8,862 7,885 8,485	16.83 7.41 9.61	108 (irr) 53 (dry) 240 170

  Fodder crops such as Pasja, leafy turnip, rape, giant rape and maize are sown for autumn feed. Some crops are allowed to recover after the initial grazing and are grazed again. This means that N at risk of leaching may be caught by a subsequent crop or pasture following autumn grazing. However, for those grazed in June a catch crop would be required to reduce the risk of high N losses.

  Autumn fodder crop production (kg DM/ha) during the five years of observation

  Paddock	Species	Date	DM (kg/ha)	Area of paddock (ha)	N leaching (kg N/ha)
  Mushroom 1 Leader Half pipe Mushroom 2	Pasja Pasja Pasja Pasja	7/1/15 18/2/15 24/3/15 24/3/15	6,309 6,453 10,140 6,106	4.77 7.84 4.75 4.59
  Kerry’s corner	Leafy turnip	12/2/16	3,318	1.42
  Hayshed Ram	Leafy turnip Leafy turnip	12/2/16 12/2/16	1,547 1,435	6.53 6.01
  Derry Hill Killer shed	Giant rape Giant rape	21/3/16 1/4/16	2,083 3,933	8.08 5.24
  Leader pivot	Maize	21/3/16	9,093	7.4
  Ram Top Gully Jundee	Rape Rape Rape	2/5/17 15/3/17 5/4/17	3,121 3,200 3,800	6.01 5.16 3.45
  Nimary	Rape	5/4/17	3,800	3.69
  Road	Giant rape	5/4/18	8,395	3.32
  Road	Giant rape	28/6/18	14,720	3.32	40
  Collard Road Strip	Giant rape Giant rape Giant rape	17/6/19 17/6/19 17/6/19	6,192 6,679 5,998	4.99 7.5 4.65	377 201 160

• Catch crops

  • Early establishment of catch crops has proven challenging. However, earlier sowing tended to have a yield advantage and greater cost effectiveness. This indicated that it is worth considering earlier sowing of catch crops wherever and whenever possible.
  • Catch crops were shown to reduce the risk of N leaching through their ability to take up N remaining in the soil following winter grazing of fodder crops and appear to be the most appropriate tool to reduce the high N losses associated with winter grazing of fodder crops.

  Catch crops planted in 2017 after fodder beet grazing were not particularly successful due to extremely wet conditions, as shown in the table below. Oats and triticale were sown on 5^th July 2017 (9 days after grazing), and 31^st August 2017 (16 days after grazing). Very few cereal plants survived the July sowing. Despite a poor survival of plants in the August sowing, more than 2 t DM/ha was grown in just 71 days.

  Performance of catch crops sown immediately post-winter grazing of fodder beet, assessed on 10 Nov 2017

  Cereal	Plant counts	Survival*		Composition (%)		Herbage mass (kg DM/ha)
  	(n/m2)		(%)	cereal	other	cereal	other
  Sown 5 July 2017
  Control	0
  Oats	5		1.0
  Triticale	1		0.2
  Sown 31 August 2017
  Control	0			0	0	0	0
  Oats	147		25.2	100	0	2,865	0
  Triticale	78		19.9	100	0	2,215	0

  Further catch crop trials were sown in 2018 after kale grazing. Barley was direct drilled on 27 July 2018 (cultivar “Monty”). Control plots were kept fallow. At the start of November, plots were split in half and SustaiN fertiliser (60 kg N/ha) was applied to one half of each plot. Seedling counts showed reasonable establishment. An average of 5.5 t DM/ha had accumulated by the 26 November 2018 (6.2 t DM/ha for those that received N).

  Seedling establishment on 26 Sept 2018 and dry matter production (kg/ha) from catch crop and fallow plots on 26 Oct 2018 and 26 Nov 2018 (with and without added N fertiliser on 1 Nov).

  Plot	Treatment	Seedling count/m²	DM (kg/ha) 26/10/18	DM (kg/ha) 26/11/18
  				+ N	No N
  1	Fallow		-	-	-
  2	Barley	152	1,391	5,383	6,284
  3	Barley	102	1,441	5,627	5,403
  4	Fallow		-	-	-
  5	Fallow		-	-	-
  6	Barley	123	1,456	7,669	4,899

  Measurements of soil mineral N were collected at three depths (0-15 cm, 15-30 cm, and 30-60 cm) on 6 Dec 2018.

  • Lower amounts of nitrate in the soil were shown for barley than those which were left fallow, at all sampling depths.
  • Where N fertiliser was applied during the season, it appeared to be quickly taken up by the barley, whereas in fallow plots soil nitrate levels increased at all sampling depths.
  • There was 80 kg N/ha in the soil when the barley was sown, and only 20 kg N/ha remained in the soil at harvest, while fallow plots contained 40 kg N/ha (where no N fertiliser was added).
  • This shows that barley as a catch crop can reduce the risk of N leaching by taking up N remaining in the soil following winter grazing of fodder crops.

  

  Nitrate levels in the soil profile under a barley catch crop and fallowed ground on 6 Dec 2018. Half of each plot was fertilised with N fertiliser (+N) or not (-N) during the growing season on 1 Nov 2018.

Concluding comments Blair

“Winter grazing of crops with cattle is our biggest risk of losing N to water. The Trials have shown early sowing of catch crops to take this N back up from the soil to be very beneficial. The practicality of doing this will vary each year, with soil condition, rainfall and stage of rotation of the paddock all needed to be taken into consideration. As farmers we still need sowing a catch crop to be a profitable exercise, and obviously want to minimise the risk of crop failure associated with sowing too early into damp, cold soils.”

“Plantain has shown benefits of lower N being excreted, but has severe limitations in being able to maintain a sward composition of 30%. We have definitely noticed this on our property, and feel that not being a great competitor with companion species will limit its N reduction use going forward.”

Full report

Download the full report on the Sheep and Beef monitor farms, including the catch crop results, here.