Before we all get busy touting the virtues and benefits of ZM, we may want to do a little more research.
Based on the benthic oxygen demand data and previous reports of low DO in rivers infested with zebra mussels, we believe the low DO in portions of the Mississippi River main channel during June and July was likely influenced by zebra mussel respiratory activity, decomposition of waste products and decaying zebra mussels. Reduced river flow and warm water conditions during mid- to late June would have contributed to a greater DO deficit during this time in reaches with high zebra mussel infestations.
Zebra mussel-induced water quality impacts were also believed to be responsible for unusually water quality conditions in the river during August and September of 1997. Unusually low chlorophyll concentrations and high light penetration was observed at LD 9 during this time. This was particularly apparent in early September when chlorophyll a concentrations were about 2 ug/L and light penetration (1% depth) was 3.5 m. In contrast, chlorophyll a was about ten fold greater upstream at LD 8 (Figure 2e) during this time and light penetration was substantially lower. Ratios of dissolved nutrients (soluble reactive phosphorus, ammonia nitrogen and silica) to chlorophyll a were also unusually high at LD 9 based on long term data for this site (Sullivan and Endris, 1998). Zebra mussel-induced nutrient conversions (particulate to dissolved forms) and phytoplankton consumption would be expected to contribute to high nutrient to chlorophyll ratios.
dnr.wi.gov/org/water/fhp/papers/p1/misszmdo.htm