Water quality concerns associated with dairy farms

2017 ◽  
pp. 33-46
Author(s):  
K. F. Knowlton ◽  
P. P. Ray
Keyword(s):  
Author(s):  
S.J. Dennis ◽  
R.W. Mcdowell ◽  
D.R. Stevens ◽  
D. Dalley

Currently spring forage crops are used to manage late calving cows on the dairy platform, protect spring pasture from pugging damage, and allow the animals to feed on a mix of brassica and pasture to transition to a pasture-based diet. In addition, like winter forage crops, they could contribute considerable water quality contaminants via surface runoff. However, it may be possible to manage farms without spring forage crops. Two Southland dairy farms were used to show: 1) flowweighted mean concentrations of many water quality contaminants in surface runoff from a spring-grazed forage crop were similar to those found in studies of winter-grazed forage crops; and 2) that, using growth rate data for 2007-2012, in no year was the modelled forage crop beneficial from a feed supply perspective, and in all years the farms had similar financial performances and fewer feed deficits under all-grass management. Hence, good pasture management (e.g. avoiding treading damage using a stand-off pad and short grazing times) may negate the need for a spring forage crop, decreasing contaminant losses while not impairing farm profitability. Keywords: surface runoff, transition diet, water quality, winter forage crop.


2007 ◽  
Author(s):  
Michael S Lennox ◽  
David J Lewis ◽  
Jon Gustafson ◽  
Kenneth W Tate ◽  
Edward R Atwill

2009 ◽  
Vol 92 (8) ◽  
pp. 3714-3722 ◽  
Author(s):  
N.R. Perkins ◽  
D.F. Kelton ◽  
K.J. Hand ◽  
G. MacNaughton ◽  
O. Berke ◽  
...  

2005 ◽  
Vol 51 (3-4) ◽  
pp. 239-247 ◽  
Author(s):  
D. Fraters ◽  
L.J.M. Boumans ◽  
T.C. van Leeuwen ◽  
W.D. de Hoop

The effect of policy measures on agriculture and water quality with respect to nitrogen have been monitored on farms in the sandy regions since the early 1990s. Nitrogen surplus on dairy farms decreased by 100 kg/ha (30%) in the 1991–1999 period due to demonstration projects and the implementation of MINAS, limiting farm gate balance surplus. Nitrogen surplus on arable farms has slightly decreased (30 kg/ha, i.e. 20%), probably because MINAS became mandatory for arable farms from 2001 onwards. About 25% of the farm-gate balance N surplus leached as nitrate into the upper metre of the groundwater. The NO3-N concentration decreased in the 1992–2001 period, but the decrease was larger for dairy farms (16 mg/l, 46%) than for arable farms (7.7 mg/l, 30%). Of the decrease in NO3-N concentration on dairy farms, 23% is caused by a decrease in N surplus, and 27% by environmental factors, such as a higher precipitation surplus, more wet soils and more peat soils in the second part of the monitoring period. However, unknown factors are responsible for 50% of the decrease.


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