Tighter margins increase the need to maximise output from grass, whether for grazing or conservation. Independent adviser Ian Richards of Suffolk-based Ecopt consultancy outlines the principles of fertiliser requirement.
So you have a fertiliser plan for grassland? But did you realise the main principles of grassland nutrition were developed in the 1970s and yet their implementation is still not fully achieved.
Targeting fertiliser use to grass crop, use, soil condition and nutrient status, availability of organic fertiliser from muck, slurry or arable by-products must all factor. Equally, there is no point in growing more grass than can be used.
For explanatory purposes grassland can be split into three types: Intensively managed grassland typically supporting a stocking rate of two cow equivalents/ha (where each cow is 600kg live weight and sheep equate to 0.15 cow) and where fertiliser is the major source of N.
Moderately intensive grassland supports 1.5-2 cow equivalents/ha and clover often makes a significant contribution to N supply. Where stocking rate is under 1.5 cow equivalents/ha - low input or extensive systems - N supply is usually heavily dependent on clover within the sward.
Nitrogen - how much?
The type of livestock enterprise - stocking rate, feed policy and use of arable by-products - will determine dependence on grass and the growth, or more accurately yield, needing to be achieved.
Growth is controlled largely by the total amount of N available to the crop. It combines N made available from mineralisation or breakdown of soil organic N, that fixed by clover, deposition from the air and applications of manures and fertiliser. Of these, fertilisers offer the most rapid and effective control of N available to the crop and should therefore be adjusted to suit the enterprise.
It is possible to give examples of N total supply and contributions from other sources which influence the amount of N fertiliser needed (see Table 1).
| Table 1. Total N needed and amounts supplied from other sources. |
| | Intensively managed | Moderately intensive |
| Permanent grass, grazed | One year cut ley, arable rotation | Permanent grass/clover, grazed |
| Total N supply needed | 450 | 450 | 340 |
| Mineralisation/deposition | 80 | 40 | 70 |
| Clover | 40 | 0 | 60 |
| Excreta | 80 | 0 | 60 |
| Fertiliser needed | 250 | 410 | 150 |
| Source: Richards, I. Ecopt 2008. |
N uptake is affected little by temperature (although 5C at 10cm is desirable) and day length, unlike dry matter accumulation. Allowing time for full dry matter response was the basis for the 2.5kg/ha N a day of growth rule of thumb developed back in the 1960s and which remains a good guide today.
For example, for a 30-day rotation 75kg/ha N is a good starting point. For grass growing 50 days from fertiliser application to cutting 125kg/ha N will be about right. The same rule applies equally to set-stocked grassland, for example 60kg/ha N every 30 days.
Phosphate and Potash
Intensively managed grass can take up 80-100kg P205/ha a year. Soils should be analysed every three to four years to assess availability and testing typically costs 15p/ha a year. Some phosphate is best applied in spring and the amount required varies little between cut and grazed swards.
To this end research from IGER's Grassland Development Centre, Aberystwyth, suggests an early season application of a 26:13:0, although appearing more costly, can give better response than the same amount of phosphate applied through the season.
Do not rely on animals to return phosphate back to grassland through dung as typically only 8% of grass by area will be covered after a seasons grazing. Look out for deficiency shown as purpling of grass leaves and, in ryegrass, reddening of the stem base.
Demand for potash varies according to grass use. For example, silage crops can quickly deplete soil reserves and need addressing in fertiliser application plans.
Stock pass back most potash within urine but even on intensively managed grassland distribution can be patchy and soil levels should be tested every three to four years. Remember clover is more susceptible to potash deficiency than grass.
One element in fertiliser plans often overlooked is sulphur. SO3 emissions from industry have fallen four-fold to 25kg/ha SO3 a year today and, as a result, deficiency is more common and seen as yellowing of younger leaves (unlike N deficiency that shows as yellowing on older leaves).
An application of about 40kg/ha SO3 is typically required per cut of silage. Manufactured fertiliser provides guaranteed amounts unlike SO3 found in manures which can lose availability during storage to just 5-10% after six months.
| Table 2. Fertiliser value of manures. |
| Nutrient value (£/t) | Cattle slurry | Cattle FYM |
| N2 | 0.42 | 0.85 |
| P2O5 | 0.66 | 1.92 |
| K2O | 1.15 | 2.60 |
| Total | 2.23 | 5.37 |
| Source: Richards, I. Ecopt 2008. |
What's it worth?
Manures and slurry have a value as providers of nutrients to crop needs (Table 2). Typical nutrient values are well established (Table 3) and - while these can vary according to dry matter - should be taken into account when planning total fertiliser application plans. If in doubt, several organisations as well as commercial companies can test slurry and manure to give an accurate idea of nutrient content.
For example, an application of slurry at 40t/ha would provide N worth £17/ha, P2O5 worth £26/ha and K2O worth £46/ha a total contribution of £89/ha.
There is a strong risk of N loss as ammonia during application of slurry. Losses can be reduced by up to 50% where using a trailing hose, 70% for trailing shoe, 90% by injection and 80% when incorporated by cultivation.
| Table 3 Typical nutrient value of slurry and manure. |
| | Cattle slurry kg/cu m | Cattle FYM kg/t | Pig slurry kg/cu m | Pig FYM kg/t |
| Total N | 3.0 | 6.0 | 4.0 | 7.0 |
| Total P2O5 | 1.2 | 3.5 | 2.0 | 7.0 |
| Total K2O | 3.65 | 8.0 | 2.5 | 5.0 |
| Source: Richard, I. Ecopt 2008. |
Timing and palatability
Do not treat all fields the same, as uptake and usage of N depend to varying degrees on soil structure and temperature, quality and mix of grass types, and intended use of grass as a crop.
Manure application technique will also have a major impact on palatability of grass as a crop for livestock. Residues from manure or slurry can lead to rejection by livestock.
Ensure, where possible, a minimum of six weeks between application of manures and grazing and only apply when the crop is actively growing. This is especially important in dairy systems where the need to graze down well in the first grazing affects the quality and quantity of subsequent growth.
Likewise, applications too close to harvest can lead to high nitrate levels in herbage. A low nitrate level of under 0.1% is essential to prevent the production of ammonia nitrogen that restricts fermentation of silage in the clamp.
Although rules of thumb exist for planning of N applications remember a flexible approach will pay dividends. Fertiliser is an essential, but often costly, input - use it wisely.