Harmful Algal Bloom Forecast ProjectApplication of Remote Sensing to Red Tide Forecasts in the Gulf of Mexico: Proceedings of a WorkshopWorkshop FindingsWith the eastern Gulf of Mexico as a model system, a variety of remote sensing platforms and instruments were evaluated to determine the advantages and disadvantages of each for use in an operational HAB forecast system. An operational system would require continuous coverage and would be developed to provide data to predict, verify, and improve the parameterization of the biological and physical processes in a forecast model. Remote Sensing PlatformsSatellite imagery provides spatial data at scales of hundreds to thousands of kilometers with resolution varying from meters to kilometers; a specific area will have repeat coverage that varies from less than one to greater than six days, depending on the satellite orbit. This spatial scale of information is warranted because oceanographic features that initiate G. breve blooms and the blooms themselves occur on kilometer scales. Satellite monitoring may be most useful to detect the conditions suitable for bloom development and to track the progress of a bloom as it moves in from offshore. This technique could allow prediction of when and where the coastal region would be affected by an HAB. Ocean Color: The Coastal Zone Color Scanner (CZCS), which was active from 1978 to 1986, proved that discoloration of the water caused by chlorophyll a present in phytoplankton is detectable by satellite. The substantial CZCS and Ocean Color and Temperature Scanner (OCTS: Sept. 1996 to June 1997) archives serve as data sources for historical information on the frequency, duration, and spatial extent of phytoplankton blooms on the Florida shelf. The ocean color satellite, Sea-viewing Wide Field-of-view Sensor (SeaWiFS), launched in August 1997, is essential for current and future forecasting capabilities. Satellite coverage would be vital as an early warning for bloom initiation and development in offshore areas. SeaWiFS provides normalized water-leaving radiance at five key wavelengths in the visible region of the spectrum. Derived products include chlorophyll a concentration, as a phytoplankton biomass parameter (Figure 3), and attenuation coefficients, as indicators of water clarity. Preparations are being made by the U.S. and foreign space agencies to launch additional ocean color sensors during the next several years.
Sea Surface Temperature: The Advanced Very High Resolution Radiometer (AVHRR) has been used to identify physical oceanographic features by detecting differences in surface water temperature (Figure 2). For example, northern intrusions of warm Loop Current water onto the Florida shelf and nearshore upwelling can be detected in AVHRR imagery. The ability to identify features that concentrate and transport phytoplankton can be used as an early warning of conditions conducive to bloom development. The mechanism of transport of HAB species to atypical regions has been traced using AVHRR imagery (Tester and others 1991; Keafer and Anderson 1993).
Sea Surface Height: Imagery from microwave altimeters aboard the TOPEX and European Remote Sensing (ERS 2) satellites can be used to identify physical oceanographic features by detecting differences in surface water height. The ability to identify features such as geostrophic currents that concentrate and transport phytoplankton can be used as an early warning of conditions conducive to bloom development.
Surface Waves and Fronts: Ocean currents and fronts can be identified by synthetic aperture radar (SAR) that detects surface roughness. This imagery would allow identification of physical oceanographic features that concentrate and transport phytoplankton and could aid in detection of bloom initiation and transport. This type of satellite could identify the Loop Current in summer months when the temperature signal is obscured by surrounding warm waters. These microwave sensors are available on ERS 1 and 2 and the Canadian RADARSAT satellite.
Wind Fields: Wind fields may be most useful in determining the direction and velocity of bloom transport. Large-scale wind patterns can provide information critical to determining the movements of surface ocean features. Winds are suspected to be a major factor in the demise of blooms by mixing the water column, thereby disrupting the physical environment. Data are available from the Advanced Microwave Instrument (AMI) aboard ERS 1 and 2 and from the Special Sensor Microwave/Imager (SSM/I).
Aircraft instruments provide spatial data at the meter to kilometer scale with resolution on the scale of a meter or less; temporal resolution is variable depending on flight schedules. Aircraft monitoring may be most useful to detect large-scale features nearshore where satellite data are often invalid because of interference by continental aerosols and terrestrial features. Because they are flown at low altitude, aircraft-based instruments are relatively unaffected by cloud cover; although some atmospheric correction would be required. Aircraft can be equipped with several instruments for simultaneous measurement of several variables. If the systems are automated and user friendly, they could be mounted to aircraft-of-opportunity such as the Coast Guard helicopters that routinely fly over coastal regions of the Gulf of Mexico. Targeted, local areas could be monitored routinely using instruments mounted on aircraft. Ocean Color: Ocean color can be measured using passive optical systems such as the Ocean Data Acquisition System (ODAS) and SeaWiFS Aircraft Simulator (SAS) that measure radiance at selected visible wavelengths. These systems have been used previously in nearshore areas such as the Chesapeake Bay (Harding and Itsweire 1990). Imaging instruments are available that collect swath data and have been used in, for example, Barkley Sound (Gower and others 1988). Examples are the Airborne Visible Infra-Red Imaging Spectrometer (AVIRIS) and the Compact Airborne Spectrographic Imager (CASI).
Laser Fluorosensing: An alternative to passive ocean color measurements, active laser fluorescence (Light Detection and Ranging [LIDAR]) has been used to detect phytoplankton by measuring chlorophyll pigment fluorescence (Hoge and Swift 1981). LIDAR can be modified to detect fluorescence of colored dissolved organic material (Vodacek and others 1995) and phycoerythrin-containing plankton such as cyanobacteria (Sathyendranath and others 1994), which could prove useful in the detection of Trichodesmium spp. Some reports indicate that toxic dinoflagellate blooms are often preceded by or occur with blooms of cyanobacteria (Steidinger and Baden 1984; Paerl and Bebout 1988) Laser fluorosensing also has been used to measure the beam attenuation coefficient (Bristow and others 1981; Hoge and Swift 1981). This method has been used successfully by the remote sensing group at NASA, Wallops Island.
Salinity: The Scanning Low Frequency Microwave Radiometer is a remote sensing system (Gooberlet and others 1997) that measures salinity to within 1 ppt and sea surface temperature to within 0.5 ºC. Temperature is required to correct microwave measurements and obtain accurate salinity data; Spatial resolution depends on aircraft altitude and is typically on the order of 100 m. A salinity map could address bloom demise due to freshwater influx.
Mooring, Buoy and Ground Platforms: Instruments on moorings and buoys provide spatial data at the meter to kilometer scale with resolution on the scale of 1 m or less; temporal data can be obtained on scales that can vary from hours to months with resolution of seconds or less. Moored instruments can provide vertical profile data; these data are not available readily from any other remote sensing platform. Moorings have the potential of being equipped with several instruments for simultaneous measurement of several variables. Instruments mounted on drifters are essential for the development and verification of area circulation models. Forecast models will require continuous monitoring for timely data acquisition. Data collection is relatively impervious to weather conditions, in particular to cloud cover. Moorings may be the most efficient means for continuous data collection from targeted local areas. The National Data Buoy Center (NDBC) maintains a system of buoys that monitor wind speed and direction, air temperature, and atmospheric pressure above the surface and water temperature at the surface for locations along the coast and at selected offshore sites. The University of South Florida also maintains buoys in the area. The NOAA Coastal Ocean Programs Ecology and Oceanography of Harmful Algal Blooms (ECOHAB) project has plans to establish 12 moorings in strategic locations in the Gulf of Mexico. Ocean Color: (see summary by Cullen and others 1997) Instruments moored at depth can provide information on the sub-surface distribution of phytoplankton populations by measuring irradiance and absorption coefficients. A chain of irradiance sensors allows calculation of spectral diffuse attenuation coefficients. Information on irradiance propagation below surface and on spectral absorption and beam attenuation coefficients is useful for the interpretation of surface signals that are measured by aircraft and satellites.
Winds, Temperature, Salinity, and Currents: Conductivity, temperature, and depth sensors provide information allowing the detection of water masses. Depth profiles provide information on the depth of the mixed layer and allow detection of subsurface water masses. Current meters provide information on the speed and direction of water mass movement. This information is necessary for validation and refinement of circulation models.
Waves, Fronts, and Currents: The Ocean Surface Current Radar (OSCR) system is a series of high frequency (25.4 MHz) radar stations that has been developed by the Rosenstiel School of Marine and Atmospheric Science to resolve surface current fields (Shay and others 1995; 1998). Spatial coverage is approximately 45 km with a resolution of 1 km for the High Frequency (HF) mode of OSCR (Figure 4). Temporal scale is variable; surface currents can be mapped approximately every 20 min for use in understanding particle accumulation and dispersal in surface current convergent and divergent regimes. The measurements also can be used to analyze the importance of tidal and subinertial flows in the transport of blooms. This instrument may be most useful in monitoring the currents transporting blooms along shore.
Point-and-profile data are of limited spatial and temporal coverage; however, these data are critical for the validation of remote sensing algorithms. Ships are essential for rapid response to an HAB event and can be directed to an area of interest indicated by other remote sensing data. Historical data primarily are point-and-profile data. Attempts to statistically analyze remote sensing data in combination with historical data to determine long-term changes in bloom frequency and intensity will require that remote sensing data be validated by methods comparable to those used for historical data collection. Access to a ship and water samples allows for the development of techniques that are considered to be in the research phase. These techniques often require a discrete water sample and intensive analysis, but may prove useful to an automated remote sensing-based forecast program in the future. Many of these techniques involve the identification and enumeration of G. breve cells as a constituent of the phytoplankton population (Van Dolah and others 1994). Research has begun on the discrimination of the optical signature of G. breve from the optical signature of a mixed phytoplankton assemblage (Millie and others 1997). Additionally, the carotenoid pigment gyroxanthin-diester is being investigated as a quantitative indicator of G. breve. This pigment is consistent within G. breve and has not been detected in other species in the eastern Gulf of Mexico (Millie and others 1995). Absorption in the ultraviolet region of the spectrum also may be useful as an identifying feature for toxic dinoflagellates (Kahru and Mitchell submitted). Shipboard measurements also would be required to measure carbon and oxygen production by G. breve. Productivity analyses require discrete water samples; however research using active (e.g., Falkowski, Greene, and Kolber 1994) and passive (Kiefer, Chamberlin, and Booth 1989; Chamberlin and others 1990) fluorescence measurements may prove useful to a remote sensing program in the future. Other studies that would benefit from access to a ship platform are those that investigate the nutrient dynamics of G. breve blooms (e.g., Vargo and Howard-Shamblott 1990).
Data Integration and Modeling TechniquesThe "Marine Biotoxins and Harmful Algae: A National Plan" (Anderson, Galloway, and Joseph 1993) states as a weakness that there are no predictive models for population development, transport, and toxin accumulation for any of the major harmful algal species in the US. Predictive models, which would be necessary to implement a forecasting capability, require integration of basic research and long-term monitoring measurements to validate parameterization. A method for data storage and integration suggested in the National Plan is a geographic information system (GIS). This type of system links spatially-related oceanographic data collected by remote sensing methods with in-situ measurements and with other spatial data including geology, municipal land-use patterns, and plant and animal habitat classifications. This type of data storage and analysis system will be useful for both research purposes and for management purposes such as prioritizing mitigation and control responses to predicted HAB events. Numerical models are one mechanism to integrate data for physical and biological components for the purposes of prediction. Numerical models have been designed to describe oceanic circulation in limited spatial areas and have been used in the prediction of oil spill trajectories (Galt 1994). These models would be used based on the premise that tracking and predicting the movements of the water mass would track and predict the movements of an HAB. They are complex models in nearshore areas that must account for variation in wind, tides, temperature and salinity and topography. |
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