Recent changes in submersed macrophytes and water quality variables have be
en offered as the strongest evidence that the current restoration program a
t Lake Apopka will be effective (Lowe et al., 2000); however, the new beds
of submersed plants in Lake Apopka are found only on hard substrates on the
fringes of the lake within 40 m of shore and are protected from waves by c
attails (Typha spp.). They occupy only 0.02% of the lake area, and there is
no indication that they can colonize the flocculent sediments that make up
90% of the lake area. There is no correlation between annual inputs of pho
sphorus and total phosphorus concentrations in the lake, and patterns of ch
ange in chlorophyll and other water quality variables do not follow changes
in phosphorus loads. Rather than reflecting decreases in phosphorus loadin
g, the recent changes could be related to the harvest of benthivorous fish
or are just the normal fluctuations found in lakes that have not been pertu
rbed. Regardless of the reason the macrophytes were lost in the 1940s, the
new analyses confirm our previous findings that the high turbidities in Lak
e Apopka are due to the resuspension of sediments, and that the fluid mud c
annot support the colonization of submersed aquatic macrophytes. Even witho
ut the fluid mud, the target phosphorus concentration of 55 mg m(-3) is too
high to bring about the restoration of the former macrophyte beds in the l
ake.