In confined animal feeding operations, liquid manure systems present special handling and storage challenges because of the large volume of diluted wastes. Water treatment polymers and mineral phosphorus (P) immobilizing chemicals [Al-2(SO4)(3)(.)18H(2)O, FeCl(3)(.)6H(2)O, and Class C fly ash] were used to determine particulate and dissolved reactive phosphorus (DRP) reduction mechanisms in high total suspended solid (TSS) dairy manure and the P release from treated manure and amended soils. Co-application exceeded the aggregation level achieved with individual manure amendments and resulted in 80 and 90% reduction in metal salt and polymer rates, respectively. At marginally effective polymer rates between 0.01 and 0.25 g L-1, maximal aggregation was attained in combination with 1 and 10 g L-1 of aluminum sulfate (3 and 30 mmol Al3+ L-1) and iron chloride (3.7 and 37 mmol Fe3+ L-1) in 30 g L-1 (TSS30) and 100 g L-1 TSS (TSS100) suspensions, respectively. Fly ash induced particulate destabilization at rates greater than or equal to50 g L-1 and reduced solution-phase DRP at all rates A g L-1 by 52 and 71% in TSS30 and TSS100 suspensions, respectively. Aluminum and Fe salts also lowered DRP at rates less than or equal to10 g L-1 and higher concentrations redispersed particulates and increased DRP due to increased suspension acidity and electrical conductivity. The DRP release from treated manure solids anti a Typic Paleudult amended with treated manure was reduced, although the amendments increased Mehlich 3-extractable P. Therefore, the synergism of flocculant types allowed input reduction in aggregation aid chemicals, enhancing particulate and dissolved P separation and immobilization in high TSS liquid manure.