2008 Joint Annual Meeting (5-9 Oct. 2008): A Chemical Treatment to Reduce P Desorption From Manure Exposed Fluvial Sediments.

624-2 A Chemical Treatment to Reduce P Desorption From Manure Exposed Fluvial Sediments.



Tuesday, 7 October 2008
George R. Brown Convention Center, Exhibit Hall E
Shalamar Armstrong, Agronomy Department, Purdue University/NSERL-USDA-ARS, Purdue University, 915 West State Street, West Lafayette, IN 47907-2054, Douglas Smith, USDA-ARS National Soil Erosion Research Lab, USDA-ARS National Soil Erosion Research Lab, 275 S. Russell Street, West Lafayette, IN 47907-2077, Phillip Owens, Purdue University-Agronomy Dept., Purdue Univ., 915 W. State St, West Lafayette, IN 47907, Brad Joern, Dept of Agronomy Lilly Hall, Purdue University-Agronomy Dept., Purdue Univ., 915 W State Street, West Lafayette, IN 47907-2054 and Chi-Hua Huang, USDA-ARS, National Soil Erosion Res. Lab, 275 S Russell St. Purdue Univ., West Lafayette, IN 47907-2077
The current remediation methods for manure spills that have reached surface waters give no attention to the P enriched ditch sediments that remain in the fluvial system and continue to impair the water column. Consequently, no method exists to treat P contaminated sediments to reduce their ability to be a P source to the overlying water column. Therefore, the objectives of this study were to determine the impact of a manure spill on sediment adsorption properties and to evaluate the effectiveness of chemically treating manure exposed sediments. These objectives were accomplished using mini-flumes packed with sediment that received the following treatments: (1) no manure and no treatment; (2) manure spill without treating sediment; (3) manure spill followed by 1:1 molar ratio (Al:P) application of aluminum sulfate (alum); and (4) manure spill followed by 2:1 molar ratio (Al:P) application of alum. Phosphorus desorption was monitored using a 24 hr circulation of P free water. Clayey and sandy untreated sediments desorbed 0.09 and 0.23 mg P L-1 within the 24 hour desorption period, respectively. However, treating sediments with a 2:1 application rate of alum and CaCO3 reduced P desorption to soluble P concentrations near background concentrations recorded before the spill occurred. This study suggests that when a manure spill reaches surface waters, sediment P accumulation does occur and untreated sediments become a source of P to the overlying water column. However, treating sediments following a manure spill mitigates P desorption.