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a AgResearch Ltd, Invermay Agricultural Centre, Private Bag 50034, Mosgiel, New Zealand
b National Institute of Water and Atmospheric Research, P.O. Box 11 115, Hamilton, New Zealand
* Corresponding author (richard.mcdowell{at}agresearch.co.nz)
Received for publication April 14, 2004. There is interest in quantifying phosphorus (P) loss from intensively grazed dairy landscapes to identify key pathways and target remediation methods. The Bog Burn drains a dairying catchment in Southland, New Zealand, and has been monitored at fortnightly intervals over a 12-mo period at four sites for suspended sediment (SS), dissolved reactive phosphorus (DRP), and total phosphorus (TP). Time-integrated samplers, deployed at 0.6 median water depth at each site (calculated from previous year's flow data), collected sediment samples, which were analyzed for SS, bioavailable phosphorus (BAP), and TP. Mean concentrations of DRP and TP in stream flow and BAP and TP in sediment were generally highest in summer or autumn (0.043 mg DRP L1, 0.160 mg TP L1, 173 mg BAP kg1, 2228 mg TP kg1) and lowest in winter or spring (0.012 mg DRP L1, 0.034 mg TP L1, 6 mg BAP kg1, 711 mg TP kg1), while loads were highest in winter. Analysis of 137Cs concentrations in trapped sediment, topsoil, subsoil, and stream bed and bank sediment indicated that trapped sediment was derived from topsoil and entered the stream either through tile drainage or, to a lesser extent, overland flow. Because concentrations of DRP and TP in stream flow are in excess of recommended limits for good water quality (>0.01 mg DRP L1, 0.033 mg TP L1), management should focus on the topsoil and specifically on decreasing P loss via tile drainage. This is best achieved by decreasing soil Olsen P concentrations, especially because, on average, Olsen P concentrations in the catchment were above the agronomic optimum.
Abbreviations: BAP, bioavailable phosphorus DRP, dissolved reactive phosphorus PP, particulate phosphorus SS, suspended sediment TP, total phosphorus
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