Rd. Longhurst et al., Farm dairy effluent: A review of published data on chemical and physical characteristics in New Zealand, NZ J AGR RE, 43(1), 2000, pp. 7-14
Increased concern about environmental degradation and a move towards sustai
nable farming systems has lead to closer attention being paid to farm dairy
effluents (FDE). Treatment of FDE in New Zealand is mainly through land ap
plication, or through oxidation ponds. Since the introduction of the Resour
ce Management Act, 1991, regional councils require dairy farmers to be more
accountable for the management of effluent from their dairy farms. Regulat
ions have been imposed to limit the application of nitrogen (N) to land fro
m FDE, and these limits range from 150 to 200 kg N ha(-1) yr(-1). Farmers,
consultants, and regional councils require information on the chemical comp
osition, particularly N content, of effluents, so that land effluent applic
ation systems can be designed and managed within the guidelines or regulati
ons imposed. Data gathered from previous investigations on effluents in New
Zealand found an average solids content of 0.9% dry matter. Between 1977 a
nd 1997 the mean N content of FDE doubled from approximately 200 to 400 mg
N l(-1) The trend for higher N concentrations is likely to continue as dair
y herd numbers increase. The most likely reason for the increase in N is th
at volume of washwater used per cow has proportionately decreased as herd s
ize has increased, thus, FDE has become more concentrated with levels above
400 mgN l(-1) increasingly common. Average values of phosphorus (P) and po
tassium (K) in FDE were 70 and 370 mg l(-1), respectively. Slurries obtaine
d from anaerobic ponds, which require periodic desludging about every 5 yea
rs, had average nutrient concentrations of 1650, 290, and 510 mg l(-1) for
N, P, and K, respectively, representing an accumulation of minerals over th
e 5 years.