This study assessed the effects of a gizzard shad removal project
on redear sunfish populations.
In 1993, the St. John's Water Management District (SJWMD) began
a commercial shad gill netting program on Lake Apopka, which was
monitored by the Florida Fish and Wildlife Conservation Commission
(FWC). The SJWMD claimed that gizzard shad (Dorosoma
cepedianum) resuspend phosphorus from the lake bottom into the
water column. Resuspended phosphorus occurs when shad eat and
disrupt the bottom, which causes the sediment and the phosphorus
particles to suspend into the water column after they had
previously settled. The resuspended phosphorus is then used by
planktonic algae, resulting in excessive algal blooms.
The program later expanded to Lake Griffin near Fruitland Park
in February 2002. During the winter of 2003-2004,
approximately 20,000 redear sunfish (Lepomis microlophus)
eight-inches or larger in length were caught in gill nets deployed
for harvesting gizzard shad. Therefore, a study began in May 2004
to learn if commercial gill net harvest of gizzard shad could
impact redear sunfish populations on the Ocklawaha Chain of Lakes
(Lake County, Florida). Although the Lake Griffin redear sunfish
population was not examined prior to gill-net operations, current
studies would determine redear sunfish population parameters
following three years of gill netting. Gill-net use is scheduled to
be suspended on Lake Griffin for the next several years. After the
suspension of gill-net use, biologists will then analyze changes,
if any, to the redear sunfish population.
Before biologists can attempt to assess impacts on redear sunfish,
some preliminary data must be collected to learn more about the
fish population. Basic characteristics of interest are abundance
(index of how many fish are in the lake), growth (how fast the fish
are growing), and condition (how heavy they are for their
FWRI biologist Holly Alred sampling for
redear sunfish at Lake Eustis.
Electrofishing is a method often used to obtain this
information. This practice allows fish to be collected, measured,
and released unharmed. Redear sunfish were collected from
Lake Griffin between May 18 and July 1, 2004 by using a standard
electrofishing technique drafted by the FWC. All redear sunfish
were measured and weighed. A subsample was then collected to
determine age and gender.
Electrofishing catch rates for Lake Griffin were low, as 36.3
hours of sampling were needed to collect 471 redear sunfish. Redear
catch rates, which measure the number of fish collected per hour of
sampling, were 13 fish an hour for all fish and eight fish an hour
for fish at least six-inches in length. These values were low
compared to a recent University of Florida study of 60 lakes in
Florida, which reported an average catch rate of 49 fish an hour.
In a FWC statewide database of 35 lakes, the average catch rate was
56 fish an hour. Therefore, the Lake Griffin redear population in
the spring of 2004 was estimated to have relatively low abundance
compared to other systems in the state.
To assess the condition of fish in a population, we use a
measure called relative weight (Wr). Relative weight is the ratio
between the weight of a fish and a standard weight obtained from
many other populations. It is presented as a percentage, and the
higher the value, the better the fish's condition relative to other
populations. The average Wr for Lake Griffin redear sunfish
was 107 percent, which is average for similar systems in the FWC
database but slightly higher than the state mean of 92 percent. The
Wr values were particularly high for Lake Griffin redear sunfish
that were larger than six-inches in length, which indicates an
abundant food supply for adult sunfish. However, relatively lower
values were found for smaller individuals, which may indicate that
there is a food shortage problem for smaller fish.
Age and length information was used to calculate total annual
mortality (A), which is the combined number of fish lost annually
to fishing mortality (harvesting of fish) and/or natural mortality
(weather, disease, predators). Total annual mortality for redear
sunfish in Lake Griffin was 60 percent as compared to the statewide
average of 47 percent. The slightly higher than average total
annual mortality rate for the Lake Griffin redear sunfish
population may be the result of a variety of factors, including
increased fishing mortality (commercial and recreational) of older
fish and the lack of fish older than four-years in the
We also examined the growth of individuals in the population.
Redear sunfish grew rapidly at Lake Griffin, particularly for fish
at least two-years old. The mean size for fish ages 2- to 5- years
old was substantially higher than those of the FWC statewide redear
sunfish database and previous samples collected in 1997 from Lake
Griffin. Unlike 1997 when first-year growth was found to be
limited, recent data indicated the most growth generally occurred
during the fish's first year.
From the information we have gathered, we have determined that
there is a low abundance of redear sunfish in Lake Griffin, but the
growth and condition of these fish were generally good,
particularly for adult fish. Low condition values for smaller
individuals may indicate that there is a problem in the amount of
prey available for these fish.
Similar data were collected from other lakes in the Ocklawaha
Chain of Lakes, including Lakes Dora, Beauclair, and Eustis.
Additional sampling is scheduled for May 2007. Lakes Dora and
Beauclair were opened in March 2005 to commercial harvest of
gizzard shad, and Lake Eustis will serve as a control (no harvest)
lake. This information will allow biologists to examine redear
population dynamics prior to gill net fishing and help biologists
determine if and how the gill-net fishery for gizzard shad is
impacting the redear population in these lakes.