Lawrence E. Battoe

NUTRIENT REMOVAL FROM EUTROPHIC LAKE WATER BY WETLAND FILTRATION

Abstract Lake Apopka is a large (125 km 2 ), shallow (mean depth 1.6 m) lake in Florida, USA. The lake was made hypereutrophic by phosphorus loading from floodplain farms and has high levels of nutrients, phytoplankton (Chl a 80 μg l −1 ), and suspended matter. The restoration plan developed by the St. Johns River Water Management District encompasses the biomanipulation concept in which the critical step for large shallow lakes is increasing the transparency of the water to allow the re-establishment of submerged macrophytes. Restoration includes operation of a treatment wetland, reduction in external P loading, harvest of fish, fluctuation of lake levels, and littoral planting. The District constructed a 2-km 2 pilot-scale treatment wetland to test nutrient-removal and hydraulic performance. Lake water was recirculated for 29 months, and the removal of suspended solids and particle-bound nutrients was assessed. Hydraulic loading rate varied from 6.5 to 65 m year −l with a mean hydraulic residence time of about 7 days. The inflow contained 40–180 mg l −l TSS, 80–380 μg l −l TP (mostly particulate organic), and 3–9 mg l −l TN (mostly dissolved and particulate organic). Overall, particulate matter was removed (> 90%) by the wetland, and soluble organic compounds were unaffected. Soluble inorganic compounds such as nitrate, ammonia, and soluble reactive phosphate (SRP) were low in the lake water but increased during passage through the wetland. Particulate matter at the outlet was enriched in both N (2-fold) and P (5-fold) compared to particles in the inflow. Mass removal efficiencies were 89–99 (TSS), 30–67 (TP), and 30–52% (TN), but efficiency fell when hydraulic short-circuiting occurred. First-order removal coefficients were 107 (TSS), 63 m year −1 (TP) and 98 m year −l (particulate N). Areal particulate removal rates were 5.4 g dry matter m −2 day −l , 0.18 g PON m −2 day −l , and 0.006 g POP m −2 day −l . The ratio of N:P removal was 28:1. Total sedimentation rate was 0.4 mm day −l of very light matter (4.4 g dw l −l ). About 40% of the dry matter and nitrogen removed and about 80% of the phosphorus was found in the new sediments. Relative to the inflow of lake water, evapotranspiration (4.3%), seepage (2.6%), and rainfall (2.8%) were low. Major problems were initial leaching of SRP, but not ammonia, from native organic soils and vegetation when this former farmland was flooded; hydraulic short-circuiting via former drainage ditches; and low inflows under drought conditions. After 6 months SRP release declined, and initial SRP leaching could be prevented with soil treatment. Hydraulic short-circuiting occurred only after modifications were made. Low gravity flows were augmented with pumped inflows. With these improvements P-removal should increase from the measured 0.48 to at least 3 g P m −2 year −l . Based on the pilot project results, the first phase of an improved 14-km 2 wetland filter has been constructed. This project should accelerate improvements in the water quality of Lake Apopka and, ultimately, create a new, large wildlife-rich marsh.

Abrupt Biological Response to Hydrologic and Land-use Changes in Lake Apopka, Florida, USA

Abstract Lake Apopka is a shallow, hypereutrophic lake in north-central Florida that experienced an abrupt shift in primary producer community structure (PPCS) in 1947. The PPCS shift was so abrupt anecdotal accounts report that dominant, submersed aquatic vegetation was uprooted by a hurricane in 1947 and replaced by phytoplankton within weeks. Here we propose two hypotheses to explain the sudden shift to phytoplankton. First, hydrologic modification of the drainage basin in the late 1800s lowered the lake level ca. 1.0 m, allowing the ecosystem to accommodate moderate, anthropogenic nutrient enrichment through enhanced production in the macrophyte community. Second, additional hydrologic changes and large-scale agricultural development of floodplain wetlands began in 1942 and altered the pattern and scale of phosphorus loading to the lake that triggered the rapid shift to phytoplankton dominance in 1947. Historic land-use changes and paleolimnological data on biological responses to nutrient loading support these hypotheses.

Setting Water Quality Goals for Restoration of Lake Apopka: Inferring Past Conditions

ABSTRACT Lake Apopka is a large (12,500 ha), hypertrophic lake in central Florida which is the subject of a state-sponsored restoration program. We used three quantitative methods in concert with an analysis of the history and general character of the lake and drainage basin to infer the past conditions. We specifically examined two past conditions: 1) pristine (before any major anthropogenic disturbance) and 2) antecedent (before a specific, major anthropogenic disturbance). For Lake Apopka the pristine condition ended in the 1890s when a canal was dug which lowered the elevation for surface water outflow. The antecedent condition ended in the late 1940s when most of the lakes 8,900 ha of floodplain marsh was drained for farming. History, general lake and basin characteristics, and the quantitative analysis indicate that Lake Apopka was mesotrophic; with clear-water and native, submersed macrophyte beds; in both the pristine and antecedent conditions. The three quantitative methods (reference lakes, emp...

Particulate phosphorus removal via wetland filtration: An examination of potential for hypertrophic lake restoration

Lake Apopka in Florida, USA, is a large (area=124 km2), hypertrophic (mean total phosphorus=0.220 g/m3; mean chlorophylla=60 mg/m3) lake, with a large sedimentary store of available P (1635 × 106 g P). Phosphorus loading from floodplain farms (132 × 106 g P/yr) has been the primary cause of eutrophication. Assuming elimination of farm P loading, the Vollenweider model predicts a decline in equilibrium P concentration from 0.270 to 0.024 g/m3, if the P sedimentation coefficient (σ) remains constant. It is likely, however, that the value for σ will fall with the elimination of farm loading due to unabated internal P loading from the sediments. Under a worst-case scenario (σ=0), the model predicts that exportation of P from the lake via wetland filtration will greatly accelerate the lakes recovery. Recirculation of lake water through a 21-km2, created wetland and elimination of farm P loading is projected to result in a negative P balance for the lake (−23 × 106 g P/yr) leading to depletion of P stores in the lake in about 60 yr. The estimated cost of the project,

The restoration of Lake Apopka in relation to alternative stable states: an alternative view to that of Bachmann et al. (1999)

20 million, is less than 3% of the estimated cost of dredging. A 3.65-km2 demonstration project is underway to test and refine the wetland filtration technique. We believe the technique could be cost-effective for other hypertrophic lakes.

Improvements in water quality following biomanipulation of gizzard shad (Dorosoma cepedianum) in Lake Denham, Florida

Bachmann et al. (1999) postulated that wind energy initiated, and has maintained, high turbidity in hypertrophic (mean chlorophyll a = 92 μg l−1) Lake Apopka, Florida (mean depth = 1.6 m; area = 12 500 ha). They asserted that the turbid condition was initiated by a hurricane in late 1947 that destroyed submersed plant beds and that high turbidity has since been maintained by wind-driven resuspension of fluid sediments. In their view, there has been sufficient light for re-establishment of submersed plants over about 38% of the lake bottom, but plant growth has been precluded by the fluid character of the sediments. They concluded that the restoration program of the St. Johns River Water Management District, which includes reduction of the phosphorus (P) loading rate, will not restore water clarity or submersed vegetation. An alternative explanation for Lake Apopkas turbid state is that it was initiated, and has been maintained, by excessive P loading that led to algal blooms and elimination of submersed vegetation through light limitation. The transition to the turbid state was contemporaneous with drainage of 7300 ha of the floodplain wetland to create polders for farming, beginning in the early 1940s. Lake P budgets indicate that drainage of the farms caused a seven-fold increase in the P loading rate (0.08 g TP m−2 yr−1 to 0.55 g TP m−2 yr−1). Paleolimnological analysis of lake sediments also indicates an increase in the P loading rate in mid-century, concomitant with the decline in submersed vegetation and the increase in phytoplankton abundance. After the increase in P loading, wind disturbance may have accelerated the transition to the turbid state; but, before the increase in P loading, wind disturbance was insufficient to elicit the turbid state, as evidenced by the stability of the clear-water state in the face of 14 hurricanes and 41 tropical storms from 1881 to 1946. Measurements of photosynthetically active radiation (PAR) indicate that light limitation has inhibited submersed plant growth except on the shallowest 5% of the lake bottom. Further, the correlation between the diffuse attentuation coefficient (KPAR) and chlorophyll a (CHLA) indicates that light limitation would be removed over about 82% of the lake bottom with a reduction in CHLA from 92 μg l−1 to 25 μg l−1. Recently, following a 40% reduction in the P loading rate, the mean total P (TP) concentration, mean CHLA, and total suspended solids fell by about 30% while mean Secchi depth increased by more than 20%. Submersed plant beds appeared in areas devoid of macrophytes for nearly 50 years. These improvements, during a period with no change in mean wind speeds measured at Lake Apopka, provide the strongest evidence that the turbid state has been maintained by excessive P loading and that the current restoration program, which combines P load reduction with planting and removal of planktivorous fish, will be effective.

First report about freshwater Bryozoa in Florida (Lake Apopka)

Abstract We removed gizzard shad (GS; Dorosoma cepedianum) from Lake Denham, a 104 ha hypereutrophic lake in the Ocklawaha chain of lakes in central Florida, to evaluate biomanipulation for restoration of shallow hypereutrophic Florida lakes. A commercial haul seine removed GS in winters 1990, 1991, and 1992. The 3-year total removal was 51,738 kg wet weight or 498 kg/ha, which reduced the stock of harvestable adult GS to less than 3% of the initial level. Water quality in Lake Denham improved progressively during the biomanipulation, and some improvements persisted through 2007 despite removal of a fish barrier in 1993. From 1989 until 1993, mean annual Secchi disk visibility in Lake Denham increased from 23 to 57 cm, mean annual chlorophyll a decreased from 143 to 40 ug/L, and mean annual total phosphorus declined from 194 to 93 ug/L. Neither land use nor rainfall changed significantly during the experiment, and similar improvements were not evident in other basin lakes during the same period. These findings and work elsewhere support our conclusion that removal of GS can be an effective component in the restoration of shallow hypereutrophic lakes. We postulate that the improvements were associated with reduced nutrient cycling and bioturbation rather than increased zooplankton predation on phytoplankton. Long-term improvements in water quality in Lake Denham indicate that effects of biomanipulation can persist when the benthivorous fish populations remain depressed.

The ecosystem niche as a framework for lake management

This study reports the first information on Phylactolaemata from Florida. Bryozoan floatoblasts were collected from Lake Apopka in February 2007 with a large mesh plankton net. Submerged surfaces of docks and buoys were inspected, as well as stems of Phragmites. The following bryozoan species were found: Urnatella gracilis Leidy 1851 (phylum Entoprocta) and Plumatella bushnelli Wood 2001, Plumatella vaihiriae (Hastings 1929), Plumatella casmiana (Oka 1907) and Plumatella sp. (phylum Ectoprocta, Phylactolaemata). Until now, U. gracilis is the only species already reported in Florida: it is widely distributed in eastern North America. Due to its presence in Europe, South America, Central Africa, India and Japan, it is considered cosmopolite. P. bushnelli is known just from one site in the USA and one site in New Zealand. Few data are available for P. vaihiriae, but where this species is present it is very abundant. P. casmiana is a common and widely distributed species and can be considered cosmopolite. Future research will address the distribution and role of Bryozoa in shallow subtropical systems in Florida.

Response of a eutrophic, shallow subtropical lake to reduced nutrient loading

Abstract We propose a framework for lake management that accounts for inherent variation in ecosystem state and extends the Hutchinsonian niche concept to the ecosystem level. Analogous to the n-dimensional species niche, the ecosystem state “niche” is enclosed by the range of variation in primary environmental drivers within which the target ecosystem state can be established and maintained. We applied this concept to Lake Apopka in central Florida using the 3 major drivers of trophic status: (1) concentration of total phosphorus ([P]); (2) concentration of chlorophyll a ([Chl-a]); and 3) transparency, as represented by Secchi disk transparency (SDT). We delineated 3 volumes or domains: regional, reference, and target domain, which is the ecosystem state niche for the desired condition. The regional domain includes the range of variation in trophic status drivers for the region. The reference domain lies within the regional domain and includes the ranges for trophic status variables for a set of lakes within the region that have conditions approximating the desired condition. The target domain is the ecosystem state niche, encompassed by the ranges of values required for establishment and persistence of the desired condition. The target domain, or ecosystem state niche, considers site-specific aspects such as the lakes bathymetry, water budget, and natural nutrient loadings. Further, we demonstrate that state diagrams of the temporal trajectory of lake trophic status, plotted over the suite of domains, effectively track progress toward the management goals embodied by the ecosystem state niche.