Micro-economic drivers of profitability in an ITQ-managed fishery: An analysis of the Queensland Coral Reef Fin-Fish Fishery

An economic survey of the commercial operators currently active in the Queensland Coral Reef Fin-Fish Fishery has been carried out, as part of a research project aimed at evaluating alternative management options for this fishery. This paper presents the background analysis used as a basis to develop the sampling design for this survey. The background analysis focuses on activity patterns of the fleet based on effort and catch information, as well as patterns of quota ownership. Based on this information, a fishing business profile describing the micro-economic structure of fishing operations is developed. This profile, in conjunction with the qualitative information gained in undertaking the economic surveys, allows preliminary understanding of the key drivers of profitability in the CRFFF, and possible impacts of external factors on fishing operations.

Stock assessment of the Queensland east coast common coral trout (Plectropomus leopardus) fishery

Common coral trout Plectropomus leopardus is an iconic fish of the Great Barrier Reef (GBR) and is the most important fish for the commercial fishery there. Most of the catch is exported live to Asia. This stock assessment was undertaken in response to falls in catch sizes and catch rates in recent years, in order to gauge the status of the stock. It is the first stock assessment ever conducted of coral trout on the GBR, and brings together a multitude of different data sources for the first time. The GBR is very large and was divided into a regional structure based on the Bioregions defined by expert committees appointed by the Great Barrier Reef Marine Park Authority (GBRMPA) as part of the 2004 rezoning of the GBR. The regional structure consists of six Regions, from the Far Northern Region in the north to the Swains and Capricorn–Bunker Regions in the south. Regions also closely follow the boundaries between Bioregions. Two of the northern Regions are split into Subregions on the basis of potential changes in fishing intensity between the Subregions; there are nine Subregions altogether, which include four Regions that are not split. Bioregions are split into Subbioregions along the Subregion boundaries. Finally, each Subbioregion is split into a “blue” population which is open to fishing and a “green” population which is closed to fishing. The fishery is unusual in that catch rates as an indicator of abundance of coral trout are heavily influenced by tropical cyclones. After a major cyclone, catch rates fall for two to three years, and rebound after that. This effect is well correlated with the times of occurrence of cyclones, and usually occurs in the same month that the cyclone strikes. However, statistical analyses correlating catch rates with cyclone wind energy did not provide significantly different catch rate trends. Alternative indicators of cyclone strength may explain more of the catch rate decline, and future work should investigate this. Another feature of catch rates is the phenomenon of social learning in coral trout populations, whereby when a population of coral trout is fished, individuals quickly learn not to take bait. Then the catch rate falls sharply even when the population size is still high. The social learning may take place by fish directly observing their fellows being hooked, or perhaps heeding a chemo-sensory cue emitted by fish that are hooked. As part of the assessment, analysis of data from replenishment closures of Boult Reef in the Capricorn–Bunker Region (closed 1983–86) and Bramble Reef in the Townsville Subregion (closed 1992–95) estimated a strong social learning effect. A major data source for the stock assessment was the large collection of underwater visual survey (UVS) data collected by divers who counted the coral trout that they sighted. This allowed estimation of the density of coral trout in the different Bioregions (expressed as a number of fish per hectare). Combined with mapping data of all the 3000 or so reefs making up the GBR, the UVS results provided direct estimates of the population size in each Subbioregion. A regional population dynamic model was developed to account for the intricacies of coral trout population dynamics and catch rates. Because the statistical analysis of catch rates did not attribute much of the decline to tropical cyclones, (and thereby implied “real” declines in biomass), and because in contrast the UVS data indicate relatively stable population sizes, model outputs were unduly influenced by the unlikely hypothesis that falling catch rates are real. The alternative hypothesis that UVS data are closer to the mark and declining catch rates are an artefact of spurious (e.g., cyclone impact) effects is much more probable. Judging by the population size estimates provided by the UVS data, there is no biological problem with the status of coral trout stocks. The estimate of the total number of Plectropomus leopardus on blue zones on the GBR in the mid-1980s (the time of the major UVS series) was 5.34 million legal-sized fish, or about 8400 t exploitable biomass, with an 2 additional 3350 t in green zones (using the current zoning which was introduced on 1 July 2004). For the offshore regions favoured by commercial fishers, the figure was about 4.90 million legal-sized fish in blue zones, or about 7700 t exploitable biomass. There is, however, an economic problem, as indicated by relatively low catch rates and anecdotal information provided by commercial fishers. The costs of fishing the GBR by hook and line (the only method compatible with the GBR’s high conservation status) are high, and commercial fishers are unable to operate profitably when catch rates are depressed (e.g., from a tropical cyclone). The economic problem is compounded by the effect of social learning in coral trout, whereby catch rates fall rapidly if fishers keep returning to the same fishing locations. In response, commercial fishers tend to spread out over the GBR, including the Far Northern and Swains Regions which are far from port and incur higher travel costs. The economic problem provides some logic to a reduction in the TACC. Such a reduction during good times, such as when the fishery is rebounding after a major tropical cyclone, could provide a net benefit to the fishery, as it would provide a margin of stock safety and make the fishery more economically robust by providing higher catch rates during subsequent periods of depressed catches. During hard times when catch rates are low (e.g., shortly after a major tropical cyclone), a change to the TACC would have little effect as even a reduced TACC would not come close to being filled. Quota adjustments based on catch rates should take account of long-term trends in order to mitigate variability and cyclone effects in data.

Dimethyl sulfide and other biogenic volatile organic compound emissions from branching coral and reef seawater: Potential sources of secondary aerosol over the Great Barrier Reef

Volatile organic compounds (VOCs) in the headspace of bubble chambers containing branches of live coral in filtered reef seawater were analysed using gas chromatography with mass spectrometry (GC-MS). When the coral released mucus it was a source of dimethyl sulfide (DMS) and isoprene; however, these VOCs were not emitted to the chamber headspace from mucus-free coral. This finding, which suggests that coral is an intermittent source of DMS and isoprene, was supported by the observation of occasional large pulses of atmospheric DMS (DMSa) over Heron Island reef on the southern Great Barrier Reef (GBR), Australia, in the austral winter. The highest DMSa pulse (320 ppt) was three orders of magnitude less than the DMS mixing ratio (460 ppb) measured in the headspace of a dynamically purged bubble chamber containing a mucus-coated branch of Acropora aspera indicating that coral reefs can be strong point sources of DMSa. Static headspace GC-MS analysis of coral fragments identified mainly DMS and seven other minor reduced sulfur compounds including dimethyl disulfide, methyl mercaptan, and carbon disulfide, while coral reef seawater was an indicated source of methylene chloride, acetone, and methyl ethyl ketone. The VOCs emitted by coral and reef seawater are capable of producing new atmospheric particles < 15 nm diameter as observed at Heron Island reef. DMS and isoprene are known to play a role in low-level cloud formation, so aerosol precursors such as these could influence regional climate through a sea surface temperature regulation mechanism hypothesized to operate over the GBR.

Crystal and Molecular Structure of Sclerophytin F Methyl Ether from the Soft Coral Cladiella krempfi

new cembranoid diterpene was isolated from the soft coral Ckdiella h p f ifrom Minicoy Island (India), and its structure was established by X-ray crystallography to be sclerophytin F methyl ether (21 with the R absolute configuration at all six epimeric centers,assuming a configuration similar to that of sclerophytin C. Compound 2 may be an artifact of the isolation process.

Coral diseases are major contributors to coral mortality in Shingle Island, Gulf of Mannar, southeastern India

The present study reports coral mortality, driven primarily by coral diseases, around Shingle Island, Gulf of Mannar (GOM), Indian Ocean. In total, 2910 colonies were permanently monitored to assess the incidence of coral diseases and consequent mortality for 2 yr. Four types of lesions consistent with white band disease (WBD), black disease (BD), white plaque disease (WPD), and pink spot disease (PSD) were recorded from 4 coral genera: Montipora, Pocillopora, Acropora, and Porites. Porites were affected by 2 disease types, while the other 3 genera were affected by only 1 disease type. Overall disease prevalence increased from 8% (n = 233 colonies) to 41.9% (n = 1219) over the 2 yr study period. BD caused an unprecedented 100% mortality in Pocillopora, followed by 20.4 and 13.1% mortality from WBD in Montipora and Acropora, respectively. Mean disease progression rates of 0.8 +/- 1.0 and 0.6 +/- 0.5 cm mo(-1) over live coral colonies were observed for BD and WBD. Significant correlations between temperature and disease progression were observed for BD (r = 0.86, R-2 = 0.75, p < 0.001) and WBD (R-2 = 0.76, p < 0.001). This study revealed the increasing trend of disease prevalence and progression of disease over live coral in a relatively limited study area; further study should investigate the status of the entire coral reef in the GOM and the role of diseases in reef dynamics.

Determinación de la implementación de buenas prácticas pecuarias, para el proceso de rastreabilidad de carne en fincas ganaderas de "El Coral", Chontales

Este trabajo se llevó a cabo en el Municipio de “El Coral”, localizado al sureste de la ciudad de Managua. Los objetivos del presente estudio fueron: a) Elaborar el Protocolo de Buenas Prácticas Pecuarias; b) Determinar el grado de cumplimento de BPP en fincas ganaderas del municipio de “El Coral”; y c) Elaborar una estrategia para la implementación del programa de rastreabilidad de carne bovina. La metodología utilizada para el primer objetivo consistió en una revisión de fuentes secundarias y una encuesta a personal clave en tres aspectos de los ítems del Manual de BPP y se abordó tres aspectos: si están de acuerdo con cada ítem, si es exigible y si tienen otro ítem que agregar al protocolo; en el caso del segundo objetivo consistió en un diagnóstico modificado de PROGANIC, con preguntas cerradas aplicado a 70 fincas y su procesamiento en un programa de cómputo Excel; y en el caso del tercer objetivo se aplico una matriz de estrategia para la determinación del rol y proceso de implementación. Se obtuvo como resultado de 29 personas claves que fueron encuestadas, 55 (98%) de los 56 (100%) ítems en total del protocolo propuesto obtuvieron un consenso positivo de parte de los encuestados, para que estos ítem fueran aplicados en el diagnóstico de finca y se resulto un “Protocolo de BPP” de 50 ítem en total, de un total de 72 ítem que tenia el “Manual de BPP de la producción primaria” de la resolución 117-2004 de la Asamblea Nacional. El diagnóstico practicado a 70 fincas ganaderas que representan el 21% del municipio, mostró que el 100% de las fincas ganaderas no cumplen con las BPP definidas en el protocolo de BPP, siendo 9 ítems sobre manejo los que más afectan el no cumplimiento de las BPP. El resultado de la matriz de estrategia muestra que se debe organizar, definir el rol y establecer un mecanismo para la implementación del sistema de rastreabilidad de carne bovina en “El Coral”. Se concluye: a) El “Protocolo de Buenas Prácticas Pecuarias” aplicado en este estudio es apropiado y valido para fincas ganaderas; b) Ninguna de las fincas ganaderas cumple con las BPP para fincas ganaderas; d) Las principales causas de la no aplicación de las BPP son: el desconocimiento de las mismas; la falta de asistencia técnica directa y el bajo incentivo de la producción y e) la principal estrategia para la implementación del programa de rastreabilidad en el municipio, es la sensibilización a todos los actores locales que participaran en el programa.

Evaluacion de regencia en farmacias veterinarias de distritos I, II y III de Managua

En vista que en Nicaragua y principalmente en la capital Managua, existe una problemática en los establecimientos que se dedican a la venta de productos veterinarios y que brindan servicios directos a la ciudadanía para sus animales se propuso este estudio de tesis; que lleva por título: Evaluación de regencia en farmacias veterinarias de distritos I, II y III de Managua. Para lo cual se procedió a establecer objetivos tales como: Evaluar los tipos de farmacias veterinarias (Agroveterinarias, Farmacias Veterinarias, Farmacias Veterinarias con clínica Integrada y Farmacias Veterinarias Puras) de los distritos I, II, y III de Managua, para esto se efectuó dicho estudio en un periodo de 3 meses mediante visitas y recopilación de la información del 100% de los establecimientos encontrados en la guía telefónica del año 2007, por medio de información obtenida del Ministerio Agropecuario y Forestal (MAGFOR) y finalmente se tomaron en cuenta los establecimientos populares comprobados in situ, en total se evaluaron 20 establecimientos, en los cuales se aplicó una misma encuesta para la recolección de datos.. Los resultados obtenidos, demuestran que el alto porcentaje de las empresas que brindan servicio relacionado con la salud animal no esta siendo atendida por personal especializado, así el 80% de las Agroveterinarias equivalente a 4 establecimientos, actualmente son administradas 3 por comerciantes y una está a cargo de un Zootecnista. El 50% de las farmacias veterinarias son atendidas por Médicos Veterinarios y otro 50% por Comerciantes y Zootecnistas, no obstante aun en las farmacias veterinarias con clínica se encuentran regenciadas por Zootecnistas (9%) y el 91%(9), por Médicos Veterinarios. Se encontró que los 5 establecimientos agroveterinarios no están legalizados por las autoridades competentes del Ministerio Agropecuario y Forestal, 3 de las farmacias veterinarias (75%), laboran ilegalmente y 4 farmacias veterinarias con clínica (36%), brindan servicios a la población ilícitamente. Única y exclusivamente presentan permiso de la alcaldía de Managua. Concluyendo que la mayoría de los establecimientos son atendidos por no profesionales y /o profesionales que no son Médicos Veterinarios, no obstante se encontraron establecimientos atendidos por Médicos Veterinarios, por lo cual se recomienda que todo establecimiento de servicio Veterinario deben ser regenciados por un Médico Veterinario titulado, según citan los incisos 6.1.1 y 6.5.1 de la Norma Técnica Obligatoria Nicaragüense (NTON-20001-03.MAGFOR,2003).

Evaluacion de regencia en farmacias veterinarias de los distritos IV, V y VI de Managua

En vista que en Nicaragua y principalmente en la capital Managua, existe una problemática en los establecimientos que se dedican a la venta de productos veterinarios y que brindan servicios directos a la población para sus mascotas se propuso este estudio de tesis; que lleva por título: Evaluación de Regencia en Farmacias Veterinarias de los distritos IV, V y VI de Managua. Para lo cual se establecieron los objetivos siguientes: Evaluar los tipos de farmacias veterinarias (Agroveterinarias, Farmacias Veterinarias con clínica Integrada y Farmacias Veterinarias Puras, farmacias veterinarias y sala de estilismo) de los distritos IV , V, y VI de Managua, dicho estudio se efectuó en un periodo de 4 meses mediante visitas y recopilación del 100% de la información de los establecimientos encontrados en la guía telefónica del año 2007, así como información obtenida por el Ministerio Agropecuario y Forestal (MAGFOR) y finalmente se tomaron en cuenta los establecimientos populares comprobados in situ, en total se evaluaron 45 establecimientos clasificados en: 30 Farmacias veterinarias con clínica, 4 Agroveterinar ias, 10 Farmacias veterinarias y 1 Peluquería Canina, las cuales fueron visitadas y se recopiló información de cada uno de los establecimientos a través de una misma encuesta se recogieron datos como:nombre del establecimiento,dirección, teléfono, nivel profesional del administrador, uso de libro de bitácora , licencia de funcionamiento, uso de receta médica, superficie, precio oscilante de consultas y de cirugías en caninos y felinos, manejo de inventario de productos químicos y uso de expediente de casos clínicos. Los resulta dos obtenidos, demuestran que un alto porcentaje de los establecimientos que brindan servicio relacionado con la salud animal no esta siendo atendida por personal especializado, así el de las Agroveterinarias equivalente a 4 establecimientos, actualmente son administradas por zootecnista con un 22.2% y un 33.3% por agrónomos. El 50% de las farmacias veterinarias son atendidas por Médicos Veterinarios y otro 30% por Comerciantes y 20% por Zootecnista, no obstante aun en las farmacias veterinarias con clínic a se encuentran un 14.29% por Zootecnista y un 11.43% por Ing. agrónomos y prevaleciendo en dicho establecimiento los médicos veterinarios con un 74.29% pero no en su totalidad. Durante la etapa de investigación constatamos que un alto porcentaje de clínicas veterinarias no llevan un historial clínico de sus pacientes, solo entregan una tarjeta de vacunación y desparasitaciones, así como un alto porcentaje de estos establecimientos dicen tener licencia para funcionar no obstante el Ministerio Agropecuario y Forestal en su lista no lo reporta. Se recomienda establecer mediante comisiones de trabajo de diferentes organizaciones un modelo descriptivo de cómo tiene que ser la infraestructura de las instalaciones así como instituciones gubernamentales como: MAGFOR, MINSA, UNA y otras asociaciones de profesionales como el COMVEN formen una comisión de trabajo para asegurar que en los establecimientos se garanticen el uso, manejo y almacenaje adecuado de dichos productos ya que pueden poner en peligro la salud animal, medio ambiente y salud humana causados por residuos de los medicamentos.

Evaluacion del efecto de anabolicos de crecimiento (Zeranol over, Overmax L.A. Premium y Zeranol implante) en novillos de engorde en un periodo de cien dias en la finca El Rastro, El Coral, Chontales

Para el estudio se utilizaron 68 novillos producto del cruce de la raza Pardo Suizo x Brahman con un peso inicial de 230 ± 33 kg, con el objetivo de evaluar el efecto de tres tratamientos anabólicos sobre la ganancia de peso total en pastoreo libre durante un periodo de 100 días, siendo los tratamientos los siguientes: T 1 (Zeranol implante: Zeranol Over®), T2 (Zeranol Over® formulación tixotrópico), T3. (Overmax® LA Premium: Zeranol + ivermectina 3.15%), comparado con el T4 Testigo o Control (Sin implante). A los animales pesados y organizados en tres grupos con características semejantes, se les aplicó los tratamientos y cada grupo estuvo conformado por 17 novillos; de igual manera, fueron desparasitados con Vermectina La Premium 3. 15 %, a razón de 1ml por cada 50 kg de peso vivo (kg p.v), antes de aplicar los agentes anabólicos. Se determinó el incremento en peso a partir del peso final e inicial, y se calculó la Ganancia Media Diaria (GMD) en cada uno de los tratamientos. Para el diseño de dos vías se utilizó el test de Fisher (Análisis de Varianza) y el Test de Friedman, y categorización estadística mediante la Mínima Diferencia Significativa (DMS, P=O.OS). El análisis estadístico determinó efecto altamente significativo (P=O.OOl) en la GMD, en donde la GMD fue de 739, 624, 590 y de 536 gramos para los tratamientos T3 (Overeas® LA Premium: Zeranol + ívermectina), TI (Zeranol implante: Zeranol Over®), T2 (Zeranol Over'l formulación tixotrópica) y el Control, respectivamente. El implante Overmax® LA Premium (Zeranol+ivermectina3.15%) superó en más de 27 % al tratamiento sin implante, siendo este el tratamiento de mayor rentabilidad, con 83.43 dólares en ganancia de peso por animal, y una relación Beneficio/Costo de 1.27 por cada unidad monetaria invertida.

Fish Habitat Utilization Patterns and Evaluation of the Efficacy of Marine Protected Areas in Hawaii: Integration of NOAA Digital Benthic Habitat Mapping and Coral Reef Ecological Studies

Over the past four decades, the state of Hawaii has developed a system of eleven Marine Life Conservation Districts (MLCDs) to conserve and replenish marine resources around the state. Initially established to provide opportunities for public interaction with the marine environment, these MLCDs vary in size, habitat quality, and management regimes, providing an excellent opportunity to test hypotheses concerning marine protected area (MPA) design and function using multiple discreet sampling units. NOAA/NOS/NCCOS/Center for Coastal Monitoring and Assessment’s Biogeography Team developed digital benthic habitat maps for all MLCD and adjacent habitats. These maps were used to evaluate the efficacy of existing MLCDs for biodiversity conservation and fisheries replenishment, using a spatially explicit stratified random sampling design. Coupling the distribution of habitats and species habitat affinities using GIS technology elucidates species habitat utilization patterns at scales that are commensurate with ecosystem processes and is useful in defining essential fish habitat and biologically relevant boundaries for MPAs. Analysis of benthic cover validated the a priori classification of habitat types and provided justification for using these habitat strata to conduct stratified random sampling and analyses of fish habitat utilization patterns. Results showed that the abundance and distribution of species and assemblages exhibited strong correlations with habitat types. Fish assemblages in the colonized and uncolonized hardbottom habitats were found to be most similar among all of the habitat types. Much of the macroalgae habitat sampled was macroalgae growing on hard substrate, and as a result showed similarities with the other hardbottom assemblages. The fish assemblages in the sand habitats were highly variable but distinct from the other habitat types. Management regime also played an important role in the abundance and distribution of fish assemblages. MLCDs had higher values for most fish assemblage characteristics (e.g. biomass, size, diversity) compared with adjacent fished areas and Fisheries Management Areas (FMAs) across all habitat types. In addition, apex predators and other targeted resources species were more abundant and larger in the MLCDs, illustrating the effectiveness of these closures in conserving fish populations. Habitat complexity, quality, size and level of protection from fishing were important determinates of MLCD effectiveness with respect to their associated fish assemblages. (PDF contains 217 pages)

Cruise Report NOAA Ship McARTHUR II Cruise AR-04-04: Leg 2 (June 1-12, 2004): A pilot survey of deepwater coral/sponge assemblages and their susceptibility to fishing/harvest impacts at the Olympic Coast National Marine Sanctuary (OCNMS)

Summary: The offshore shelf and canyon habitats of the OCNMS (Fig. 1) are areas of high primary productivity and biodiversity that support extensive groundfish fisheries. Recent acoustic surveys conducted in these waters have indicated the presence of hard-bottom substrates believed to harbor unique deep-sea coral and sponge assemblages. Such fauna are often associated with shallow tropical waters, however an increasing number of studies around the world have recorded them in deeper, cold-water habitats in both northern and southern latitudes. These habitats are of tremendous value as sites of recruitment for commercially important fishes. Yet, ironically, studies have shown how the gear used in offshore demersal fishing, as well as other commercial operations on the seafloor, can cause severe physical disturbances to resident benthic fauna. Due to their exposed structure, slow growth and recruitment rates, and long life spans, deep-sea corals and sponges may be especially vulnerable to such disturbances, requiring very long periods to recover. Potential effects of fishing and other commercial operations in such critical habitats, and the need to define appropriate strategies for the protection of these resources, have been identified as a high-priority management issue for the sanctuary. To begin addressing this issue, an initial pilot survey was conducted June 1-12, 2004 at six sites in offshore waters of the OCNMS (Fig. 2, average depths of 147-265 m) to explore for the presence of deep-sea coral/sponge assemblages and to look for evidence of potential anthropogenic impacts in these critical habitats. The survey was conducted on the NOAA Ship McARTHUR-II using the Navy’s Phantom DHD2+2 remotely operated vehicle (ROV), which was equipped with a video camera, lasers, and a manipulator arm for the collection of voucher specimens. At each site, a 0.1-m2 grab sampler also was used to collect samples of sediments for the analysis of macroinfauna (> 1.0 mm), total organic carbon (TOC), grain size, and chemical contaminants. Vertical profiles of salinity, dissolved oxygen (DO), temperature, and pressure were recorded at each site with a small SeaCat conductivity-temperature-depth (CTD) profiler. Niskin bottles attached to the CTD also obtained near-bottom water samples in support of a companion study of microbial indicators of coral health and general ecological condition across these sites. All samples except the sediment-contaminant samples are being analyzed with present project funds. Original cruise plans included a total of 12 candidate stations to investigate (Fig. 3). However, inclement weather and equipment failures restricted the sampling to half of these sites. In spite of the limited sampling, the work completed was sufficient to address key project objectives and included several significant scientific observations. Foremost, the cruise was successful in demonstrating the presence of target deepwater coral species in these waters. Patches of the rare stony coral Lophelia pertusa, more characteristic of deepwater coral/sponge assemblages in the North Atlantic, were observed for the first time in OCNMS at a site in 271 meters of water. A large proportion of these corals consisted of dead and broken skeletal remains, and a broken gorgonian (soft coral) also was observed nearby. The source of these disturbances is not known. However, observations from several sites included evidence of bottom trawl marks in the sediment and derelict fishing gear (long lines). Preliminary results also support the view that these areas are important reservoirs of marine biodiversity and of value as habitat for demersal fishes. For example, onboard examination of 18 bottom-sediment grabs revealed benthic infaunal species representative of 14 different invertebrate phyla. Twenty-eight species of fishes from 11 families, including 11 (possibly 12) species of ommercially important rockfishes, also were identified from ROV video footage. These initial discoveries have sparked considerable interests in follow-up studies to learn more about the spatial extent of these assemblages and magnitude of potential impacts from commercial-fishing and other anthropogenic activities in the area. It is essential to expand our knowledge of these deep-sea communities and their vulnerability to potential environmental risks in order to determine the most appropriate management strategies. The survey was conducted under a partnership between NOAA’s National Centers for Coastal Ocean Science (NCCOS) and National Marine Sanctuary Program (NMSP) and included scientists from NCCOS, OCNMS, and several other west-coast State, academic, private, and tribal research institutions (see Section 4 for a complete listing of participating scientists). (PDF contains 20 pages)

An environmental assessment of the John Pennekamp Coral Reef State Park and the Key Largo Coral Reef Marine Sanctuary (Unpublished 1983 Report)

The Pennekamp Coral Reef State Park was established in 1960 and the Key Largo National Marine Sanctuary in 1975. Field studies, funded by NOAA, were conducted in 1980 - 1981 to determine the state of the coral reefs and surrounding areas in relation to changing environmental conditions and resource management that had occurred over the intervening years. Ten reef sites within the Sanctuary and seven shallow grass and hardbottom sites within the Park were chosen for qualitative and quantitative studies. At each site, three parallel transects not less than 400 m long were run perpendicular to the reef or shore, each 300 m apart. Observations, data collecting and sampling were done by two teams of divers. Approximately 75 percent of the bottom within the 18-m isobath was covered by marine grasses, predominantly turtle grass. The general health of the seagrasses appeared good but a few areas showed signs of stress. The inner hardbottom of the Park was studied at the two entrances to Largo Sound. Though at the time of the study the North Channel hardbottom was subjected to only moderate boat traffic, marked changes had taken place over the past years, the most obvious of which was the loss of the extensive beds of Sargassum weed, one of the most extensive beds of this alga in the Keys. Only at this site was the green alga Enteromorpha encountered. This alga, often considered a pollution indicator, may denote the effects of shore run off. The hardbottom at South Channel and the surrounding grass beds showed signs of stress. This area bears the heaviest boat traffic within the Park waters causing continuous turbidity from boat wakes with resulting siltation. The offshore hardbottom and rubble areas in the Sanctuary appeared to be in good health and showed no visible indications of deterioration. Damage by boat groundings and anchors was negligible in the areas surveyed. The outer reefs in general appear to be healthy. Corals have a surprising resiliency to detrimental factors and, when conditions again become favorable, recover quickly from even severe damage. It is, therefore, a cause for concern that Grecian Rocks, which sits somewhat inshore of the outer reef line, has yet to recover from die-off in 1978. The slow recovery, if occurring, may be due to the lower quality of the inshore waters. The patch reefs, more adapted to inshore waters, do not show obvious stress signs, at least those surveyed in this study. It is apparent that water quality was changing in the keys. Water clarity over much of the reef tract was observed to be much reduced from former years and undoubtedly plays an important part in the stresses seen today over the Sanctuary and Park. (PDF contains 119 pages)

Coral Remote Sensing Workshop: Proceedings and Recommendations, 17-18 September, Sheraton, Brickell Ave, Miami FL

Coral reefs exist in warm, clear, and relatively shallow marine waters worldwide. These complex assemblages of marine organisms are unique, in that they support highly diverse, luxuriant, and essentially self-sustaining ecosystems in otherwise nutrient-poor and unproductive waters. Coral reefs are highly valued for their great beauty and for their contribution to marine productivity. Coral reefs are favorite destinations for recreational diving and snorkeling, as well as commercial and recreational fishing activities. The Florida Keys reef tract draws an estimated 2 million tourists each year, contributing nearly $800 million to the economy. However, these reef systems represent a very delicate ecological balance, and can be easily damaged and degraded by direct or indirect human contact. Indirect impacts from human activity occurs in a number of different forms, including runoff of sediments, nutrients, and other pollutants associated with forest harvesting, agricultural practices, urbanization, coastal construction, and industrial activities. Direct impacts occur through overfishing and other destructive fishing practices, mining of corals, and overuse of many reef areas, including damage from souvenir collection, boat anchoring, and diver contact. In order to protect and manage coral reefs within U.S. territorial waters, the National Oceanic and Atmospheric Administration (NOAA) of the U.S. Department of Commerce has been directed to establish and maintain a system of national marine sanctuaries and reserves, and to monitor the condition of corals and other marine organisms within these areas. To help carry out this mandate the NOAA Coastal Services Center convened a workshop in September, 1996, to identify current and emerging sensor technologies, including satellite, airborne, and underwater systems with potential application for detecting and monitoring corals. For reef systems occurring within depths of 10 meters or less (Figure 1), mapping location and monitoring the condition of corals can be accomplished through use of aerial photography combined with diver surveys. However, corals can exist in depths greater than 90 meters (Figure 2), well below the limits of traditional optical imaging systems such as aerial or surface photography or videography. Although specialized scuba systems can allow diving to these depths, the thousands of square kilometers included within these management areas make diver surveys for deeper coral monitoring impractical. For these reasons, NOAA is investigating satellite and airborne sensor systems, as well as technologies which can facilitate the location, mapping, and monitoring of corals in deeper waters. The following systems were discussed as having potential application for detecting, mapping, and assessing the condition of corals. However, no single system is capable of accomplishing all three of these objectives under all depths and conditions within which corals exist. Systems were evaluated for their capabilities, including advantages and disadvantages, relative to their ability to detect and discriminate corals under a variety of conditions. (PDF contains 55 pages)