Relationships among liming, fertilization, water and soil chemistry, p
hytoplankton response, and aquatic animal production are still poorly
understood. There is considerable confusion about critical nutrients a
nd fertilizer formulations for pond fertilization. The literature does
not support the high application rates of nitrogen often used. Nitrat
e is more desirable than ammonium or urea as a source of fertilizer ni
trogen. Problems in ponds with water and soil quality that are related
to feeding result primarily from high inputs of feed. Organic matter
is decomposed mostly to stable humus during a growing season, and ther
e is little accumulation of highly decomposable organic matter from on
e crop to the next. High input of fresh organic matter to the bottom d
uring. a crop period can cause high oxygen demand in sediment, but sed
iment removal between growth cycles does not greatly reduce soil oxyge
n demand for the next crop. Organic matter resuspension without erosio
n of mineral soil has the potential for improving bottom soil conditio
n during crops. This can possibly be achieved by new approaches to mec
hanically induced aeration and water circulation and the use of sodium
nitrate as a soil oxidant. Chemical precipitation of phosphorus by ap
plication of aluminum, iron, or calcium ions has the potential for red
ucing phytoplankton blooms that result from feeding. The most importan
t principle regarding water quality and soil management is that a pond
has a finite capacity to assimilate nutrients and organic matter. Whe
n this capacity is exceeded, water and soil quality deteriorate. Sedim
ent removal and water exchange only transfer pollution problems from p
ond environments to surrounding environments.