
Section 2 Existing Conditions/Affected Environment
EAA Storage Reservoirs Revised Draft PIR and EIS February 2006
2-34
Within its range, Johnson’s seagrass critical habitat designations have been
designated for 10 areas: a portion of the Indian River Lagoon, north of the
Sebastian Inlet Channel; a portion of the Indian River Lagoon, south of the
Sebastian Inlet Channel; a portion of the Indian River Lagoon near the Fort
Pierce Inlet; a portion of the Indian River Lagoon, north of the St. Lucie Inlet; a
portion of Hobe Sound; a site on the south side of Jupiter Inlet; a site in central
Lake Worth Lagoon; a site in Lake Worth Lagoon, Boynton Beach; a site in Lake
Wyman, Boca Raton; and a portion of Biscayne Bay.
The essential features of habitat appear to be adequate water quality, salinity,
water clarity and stable sediments free from physical disturbance. Important
habitat characteristics include shallow intertidal as well as deeper subtidal
zones (2-5 m). Water transparency appears to be critical for Johnson’s seagrass,
limiting its distribution at depth to areas of suitable optical water quality
(Kenworthy 1997). In areas in which long-term poor water and sediment quality
have existed until recently, such as Lake Worth Lagoon, H. johnsonii appears to
occur in relatively higher abundance perhaps due to the previous inability of the
larger species to thrive. These studies support unconfirmed previous
observations that suspended solids and tannin, which reduce light penetration
and water clarity, may be important factors limiting seagrass distribution. Good
water clarity is essential for Halophila johnsonii growth in deeper waters.
Johnson’s seagrass occurs over varied depths, environmental conditions,
salinities, and water quality. In tidal channels H. johnsonii is found in coarse
sand substrates, although it has been found growing on sandy shoals, in soft
mud near canals and rivers where salinity many fluctuate widely (Virnstein et
al. 1997). Virnstein has called Johnson’s seagrass a “perennial opportunistic
species.” Within study areas in the Indian River Lagoon, H. johnsonii was found
by itself, with other seagrass species, in the intertidal, and (more commonly) at
the deep edge of some transects in water depths of up to 180 cm. H. johnsonii
was found shallowly rooted on sandy shoals, in soft mud, near the mouths of
canals, rivers and in shallow and deep water (Virnstein et al. 1997).
Additionally, recent studies have documented large patches of Johnson’s
seagrass on flood deltas just inside Sebastian Inlet, as well as far from the
influence of inlets (reported at the workshop discussed in Kenworthy, 1997).
These sites encompass a wide variety of salinities, water quality, and substrates.
Areas of concern include seagrass beds located in proximity to rivers and canal
mouths where low salinity, highly colored water is discharged. Freshwater
discharge into areas adjacent to seagrass beds may provoke physiological stress
upon the plants by reducing the salinity levels. Additionally, colored waters
released into these areas reduce the amount of sunlight available for
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