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Soil, land care and environmental research
RESEARCH ARTICLE

Land application of farm dairy effluent to a mole and pipe drained soil: implications for nutrient enrichment of winter-spring drainage

D. J. Houlbrooke A D , D. J. Horne B , M. J. Hedley B , V. O. Snow C and J. A. Hanly B
+ Author Affiliations
- Author Affiliations

A AgResearch, Invermay Agricultural Centre, Private Bag 50034, Mosgiel, New Zealand.

B Institute of Natural Resources, Massey University, Private Bag 11-222, Palmerston North, New Zealand.

C AgResearch, Grasslands Research Centre, Private Bag 11008, Palmerston North, New Zealand.

D Corresponding author. Email: david.houlbrooke@agresearch.co.nz

Australian Journal of Soil Research 46(1) 45-52 https://doi.org/10.1071/SR07124
Submitted: 24 August 2007  Accepted: 18 December 2007   Published: 8 February 2008

Abstract

Spray irrigation of farm dairy effluent (FDE) to artificially drained land in accordance with deferred irrigation criteria causes minimal direct drainage of partially treated FDE at the time of irrigation. The influence of deferred irrigation of FDE on the subsequent nutrient enrichment of winter–spring drainage from mole and pipe systems is unknown. Research was conducted in the Manawatu region, New Zealand, to investigate the influence of deferred irrigation of FDE on the quality of water in artificial drainage. The experimental site was established on a Pallic soil (Tokomaru silt loam) at the No. 4 dairy farm at Massey University, Palmerston North. There were 6 plots (each 40 m by 40 m), each with an isolated mole and pipe drainage network. Four of the plots received fertiliser according to the farm’s fertiliser program (non-effluent plots), while the other 2 plots received applications of FDE according to the deferred irrigation scheduling criteria (effluent plots). All of the plots were subject to the farm’s standard grazing management.

The average concentrations of N and P in the 2003 winter drainage (average 236 mm) from both the non-effluent and FDE irrigated plots were well above the threshold concentrations that stimulate aquatic weed growth in fresh water bodies. Annual nutrient losses of 31.4 kg N ha/year and 0.65 kg P ha/year in drainage were recorded for non-effluent plots. Deferred irrigation of FDE in the summer period did not increase the loss of N in winter–spring drainage (N loss from effluent plots was 31.1 kg N ha/year) but did cause a significant increase (P < 0.001) in total P in drainage (an additional 1.03 kg P/ha, c. 160% of losses from non-effluent plots, a loss of 3.3% of applied P). Furthermore, an irrigation of FDE to near-saturated soil in mid September resulted in the direct drainage of partially treated effluent, and hence, N and P concentrations in drainage were 6–10-fold greater than those that would normally be expected from drainage events induced by winter–spring rainfall. This illustrates the importance of scheduling FDE irrigation in accordance with deferred irrigation principles.

Additional keywords: effluent irrigation, artificial drainage, nitrogen, phosphorus, nutrient leaching.


Acknowledgments

The authors are grateful for financial assistance from Dairy InSight, the C. Alma Baker Trust, Marley NZ Ltd, and Horizons Regional Council. Spitfire Irrigators Ltd is thanked for the use of a traveling irrigator. The support of staff from Massey University’s Institute of Natural Resources, No. 4 Dairy Farm and Drainage Extension Service, is also gratefully acknowledged. Thank you to Dave Scotter (Massey University) for calculating soil water balances for the research site and Roger Littlejohn (AgResearch) for statistical analysis.


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