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1.
Mar Pollut Bull ; 156: 111247, 2020 Jul.
Article in English | MEDLINE | ID: mdl-32510389

ABSTRACT

In six contiguous estuaries in Southwest Florida (USA) focused management actions over the past several decades have reduced watershed nutrient loads, resulting in an additional 11,672 ha of seagrass meadows between 1999 and 2016, an improvement of 32%. However, in September of 2017, Hurricane Irma made landfall in the state of Florida, affecting the open water and watersheds of each of these six estuaries. In response, seagrass coverage declined by 1203 ha between 2016 and 2018, a system-wide decrease of 3%. The range of decreases associated with Hurricane Irma varied from less than a 1% loss of seagrass coverage in St. Joseph Sound to declines of 7 and 11% in Clearwater Harbor and Lemon Bay, respectively. Areas with the largest losses between 2016 and 2018 were those systems where seagrass coverage had declined in prior years, indicating the effects of Hurricane Irma might have been intensified by prior impacts.


Subject(s)
Cyclonic Storms , Estuaries , Florida , Grassland
2.
Mar Pollut Bull ; 135: 1128-1137, 2018 Oct.
Article in English | MEDLINE | ID: mdl-30301011

ABSTRACT

In Southwest Florida, a variety of human impacts had caused widespread losses of seagrass coverage from historical conditions. St. Joseph Sound and Clearwater Harbor lost approximately 24 and 51%, respectively, of their seagrass coverage between 1950 and 1999, while Tampa Bay and Sarasota Bay had lost 46% and 15%, respectively, of their seagrass coverage between 1950 and the 1980s. However, over the period of 1999 to 2016, the largest of the six estuaries, Tampa Bay, added 408 ha of seagrass per year, while the remaining five estuaries examined in this paper added approximately 269 ha per year. In total, seagrass coverage in these six estuaries increased 12,171 ha between the 1980s and 2016. Focused resource management plans have held the line on nitrogen loads from non-point sources, allowing seagrass resources to expand in response to reductions in point source loads that have been implemented over the past few decades.


Subject(s)
Environmental Monitoring/methods , Plants , Aquatic Organisms , Conservation of Water Resources/methods , Ecosystem , Estuaries , Florida , Humans , Nitrogen , Spatio-Temporal Analysis , Water Pollution
3.
Mar Pollut Bull ; 50(8): 797-805, 2005 Aug.
Article in English | MEDLINE | ID: mdl-16115497

ABSTRACT

The estuaries of Tampa Bay, Sarasota Bay, Lemon Bay, and Upper Charlotte Harbor are contiguous waterbodies located within the subtropical environment of Southwest Florida. Based on an examination of rainfall data over the period of record (1916-2001) within the watersheds of these estuaries, there is no evidence for spatial differences (at the watershed level) or monotonic trends in annual rainfall. During the 1980s, nitrogen loads into Tampa Bay and Sarasota Bay (generated primarily by domestic wastewater treatment facilities) were reduced by 57% and 46%, respectively. In response, both Tampa Bay and Sarasota Bay have lower phytoplankton concentrations, greater water clarity and more extensive seagrass coverage in 2002 than in the early 1980s. As there is no evidence of a concurrent trend in rainfall during the period of 1982-2001, it is unlikely that variation in rainfall can account for the observed increase in seagrass coverage in these two bays. In contrast, seagrass coverage has remained relatively constant since the mid 1980s in Lemon Bay and Charlotte Harbor. Domestic wastewater treatment facilities are minor sources of nitrogen to Lemon Bay, and water clarity in Charlotte Harbor varies mostly as a function of dissolved organic matter and non-chlorophyll associated turbidity, not phytoplankton levels. Even in estuaries that share boundaries and are within 100 km of each other, varied responses to anthropogenic changes and natural phenomena were observed in water quality and associated seagrass extent. Resource management strategies must take into account system-specific factors-not all strategies will result in similar results in different systems.


Subject(s)
Environmental Monitoring/statistics & numerical data , Magnoliopsida/growth & development , Marine Biology , Models, Theoretical , Seawater/analysis , Analysis of Variance , Conservation of Natural Resources , Florida , Nitrogen/analysis , Oceans and Seas , Phytoplankton/growth & development , Rain , Water Pollutants, Chemical/analysis
4.
Chem Phys Lipids ; 107(2): 191-220, 2000 Oct.
Article in English | MEDLINE | ID: mdl-11090848

ABSTRACT

The phase behavior of Myverol 18-99K, a food emulsifier rich in monoacylglycerols, in combination with water has been determined. X-ray diffraction and polarized light microscopy (PLM) were used for phase identification and structure characterization. Phase behavior was established in the temperature range from -15 to 50 degrees C and in the composition range from dry to full hydration. Phases identified include the solid lamellar crystal (Lc) phase, the liquid fluid isotropic phase and three liquid crystal phases, the lamellar liquid crystal, the cubic-Ia3d and the cubic-Pn3m phase. Phase information is reported in the form of temperature-composition phase diagrams. It was collected under equilibrium conditions where measurements were made in the heating direction beginning with the Lc phase at -15 degrees C. Phase metastability was also examined in which the natural tendency of the liquid crystal phases to undercool was facilitated. Under this condition, both cubic phases were found to remain free of the solid Lc phase over a relatively wide range of hydration values down to 0 degrees C. The microstructure of the different phases and its dependence on temperature and hydration has been determined. Compositional analysis using thin layer chromatography and gas chromatography/mass spectrometry shows that Myverol 18-99K consists of 82% monoacylglycerols (86.6% monoolein, 7. 0% monostearin, 3.5% monopalmitin, 0.9% monoarachidin, 2.0% unidentified). The equilibrium and metastable phase diagrams of the Myverol 18-99K/water system show remarkable similarity to those reported for the monoolein/water system (Qiu, H., Caffrey, M., 2000. The phase diagram of the monoolein/water system: metastability and equilibrium aspects Biomaterials 21, 223-594.).


Subject(s)
Glycerides/chemistry , Water/chemistry , Chromatography, Thin Layer , Gas Chromatography-Mass Spectrometry , Temperature , X-Ray Diffraction
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