Fertilisers - Pollution - Environment - Cycles

Leaving Cert Higher Level Agricultural Science revision notes with diagrams.

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Slurry Management, Water Quality, and Climate Impacts

Animal manure is a valuable organic fertiliser, but improper storage or spreading damages waterways, soil, and the air.

Slurry versus Farmyard Manure (FYM)

HeadingSlurryFarmyard Manure (FYM)
Nutrient valueLiquid; higher available nitrogen; fast-actingSolid; rich in organic matter; slow-release nutrients; builds soil structure
StorageUnderground slatted tanks or slurry lagoonsSolid dungstead or concrete manure slab with effluent collection tank
Spreading methodTanker fitted with trailing shoe, dribble bar, or splash plateMuckspreader
DisadvantagesStrong odours; releases toxic gases; risk of spreading disease to pastureSlower return to grazing; can spread weed seeds; bulky to transport and spread

Protecting Water Quality: Eutrophication and Buffer Zones

Under the Nitrates Regulations (Good Agricultural Practice), farmers must have 16 to 22 weeks of winter slurry storage (depending on the county) to hold waste during the winter closed period, when land spreading is prohibited by law.

Spreading slurry on wet, frozen, or steeply sloping ground causes runoff into rivers and lakes. Phosphate and nitrate enrichment causes eutrophication:

  1. High nutrient levels trigger a rapid algal bloom.
  2. Algae cover the surface, blocking sunlight from underwater plants.
  3. The algae die and sink to the bottom.
  4. Aerobic decomposers (bacteria) multiply and use up the dissolved oxygen as they break down the dead algae.
  5. Dissolved oxygen levels collapse, suffocating fish and other aquatic life.
Nutrient runoff feeds surface algae; dead algae sink, bacteria decompose them and dissolved oxygen falls, causing fish deaths.
Nutrient runoff feeds surface algae; dead algae sink, bacteria decompose them and dissolved oxygen falls, causing fish deaths.

To prevent runoff, statutory buffer zones must be observed: chemical fertiliser must not be spread within 2 m of a watercourse, while organic slurry and FYM must not be spread within at least 5 m (with wider buffer zones near lakes and drinking water sources).

A splash plate sprays slurry above grass, while a trailing shoe parts grass and deposits a narrow band on the soil surface.
A splash plate sprays slurry above grass, while a trailing shoe parts grass and deposits a narrow band on the soil surface.

Low-Emission Slurry Spreading (LESS)

Traditional splash plates throw slurry into the air, losing up to 80% of available ammonium-nitrogen as ammonia (NH3NH_3) gas. Low-Emission Slurry Spreading (LESS) techniques, such as the trailing shoe and dribble bar, apply slurry in narrow bands directly below the grass canopy onto the soil surface. This cuts ammonia loss by 30% to 60%, keeps nitrogen in the soil for plant growth, reduces pasture soiling, and allows stock back onto pasture sooner.

Climate Mitigation and Biodiversity

  • Enteric methane (CH4CH_4): Produced by microbes in the cow's rumen during grass fermentation and belched out. Reduced by feeding highly digestible leafy grass, using clover and multi-species swards, and breeding more efficient animals with high Economic Breeding Index (EBI) values.
  • Nitrous oxide (N2ON_2O): Potent greenhouse gas released from wet, compacted soils. Reduced by using protected urea instead of CAN, spreading slurry in spring when grass is growing actively, and aerating compacted ground.
  • Biodiversity: Retaining native hedgerows, establishing field margins, maintaining buffer zones, and sowing multi-species swards provide habitats for wildlife and pollinators while intercepting overland nutrient runoff.
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