Long-term changes in the pelagos, benthos and fisheries of the North Sea

Pronounced changes have occurred in the fisheries, plankton and benthos of the North Sea over the last five decades. Attribution of the relative contribution of anthropogenic versus natural hydrometeorological modulation to these changes is still unclear. As a background a summary history of our understanding of the state of health of the North Sea is outlined. We then focus on two contrasting periods in the North Sea, one between 1978-82 (cold) and the other post 1987 (warm) when pronounced alterations in many ecosystem characteristics occurred. The scale of the changes in the second of these periods is sufficiently large and wide ranging for it to have been termed a regime shift. A combination of local, regional and far field hydrometeorological forcing, and in particular variability in oceanic inflow, is believed to be responsible for the observed changes. Finally attention is drawn to the poor status of North Sea fish stocks where 7 stocks are documented as being fished outside safe biological limits. This situation is primarily believed to be a consequence of overfishing, but may have been exacerbated by environmental change.

Assessing the sensitivity of seagrass bed biotopes to pressures associated with marine activities.

This project was commissioned to generate an improved understanding of the sensitivities of seagrass habitats to pressures associated with human activities in the marine environment - to provide an evidence base to facilitate and support management advice for Marine Protected Areas; development of UK marine monitoring and assessment, and conservation advice to offshore marine industries. Seagrass bed habitats are identified as a Priority Marine Feature (PMF) under the Marine (Scotland) Act 2010, they are also included on the OSPAR list of threatened and declining species and habitats, and are a Habitat of Principle Importance (HPI) under the Natural Environment and Rural Communities (NERC) Act 2006, in England and Wales. The purpose of this project was to produce sensitivity assessments with supporting evidence for the HPI, OSPAR and PMF seagrass/Zostera bed habitat definitions, clearly documenting the evidence behind the assessments and any differences between assessments. Nineteen pressures, falling in five categories - biological, hydrological, physical damage, physical loss, and pollution and other chemical changes - were assessed in this report. Assessments were based on the three British seagrasses Zostera marina, Z. noltei and Ruppia maritima. Z. marina var. angustifolia was considered to be a subspecies of Z. marina but it was specified where studies had considered it as a species in its own rights. Where possible other components of the community were investigated but the basis of the assessment focused on seagrass species. To develop each sensitivity assessment, the resistance and resilience of the key elements were assessed against the pressure benchmark using the available evidence. The benchmarks were designed to provide a ‘standard’ level of pressure against which to assess sensitivity. Overall, seagrass beds were highly sensitive to a number of human activities: • penetration or disturbance of the substratum below the surface; • habitat structure changes – removal of substratum; • physical change to another sediment type; • physical loss of habitat; • siltation rate changes including and smothering; and • changes in suspended solids. High sensitivity was recorded for pressures which directly impacted the factors that limit seagrass growth and health such as light availability. Physical pressures that caused mechanical modification of the sediment, and hence damage to roots and leaves, also resulted in high sensitivity. Seagrass beds were assessed as ‘not sensitive’ to microbial pathogens or ‘removal of target species’. These assessments were based on the benchmarks used. Z. marina is known to be sensitive to Labyrinthula zosterae but this was not included in the benchmark used. Similarly, ‘removal of target species’ addresses only the biological effects of removal and not the physical effects of the process used. For example, seagrass beds are probably not sensitive to the removal of scallops found within the bed but are highly sensitive to the effects of dredging for scallops, as assessed under the pressure penetration or disturbance of the substratum below the surface‘. This is also an example of a synergistic effect Assessing the sensitivity of seagrass bed biotopes to pressures associated with marine activities between pressures. Where possible, synergistic effects were highlighted but synergistic and cumulative effects are outside the scope off this study. The report found that no distinct differences in sensitivity exist between the HPI, PMF and OSPAR definitions. Individual biotopes do however have different sensitivities to pressures. These differences were determined by the species affected, the position of the habitat on the shore and the sediment type. For instance evidence showed that beds growing in soft and muddy sand were more vulnerable to physical damage than beds on harder, more compact substratum. Temporal effects can also influence the sensitivity of seagrass beds. On a seasonal time frame, physical damage to roots and leaves occurring in the reproductive season (summer months) will have a greater impact than damage in winter. On a daily basis, the tidal regime could accentuate or attenuate the effects of pressures depending on high and low tide. A variety of factors must therefore be taken into account in order to assess the sensitivity of a particular seagrass habitat at any location. No clear difference in resilience was established across the three seagrass definitions assessed in this report. The resilience of seagrass beds and the ability to recover from human induced pressures is a combination of the environmental conditions of the site, growth rates of the seagrass, the frequency and the intensity of the disturbance. This highlights the importance of considering the species affected as well as the ecology of the seagrass bed, the environmental conditions and the types and nature of activities giving rise to the pressure and the effects of that pressure. For example, pressures that result in sediment modification (e.g. pitting or erosion), sediment change or removal, prolong recovery. Therefore, the resilience of each biotope and habitat definitions is discussed for each pressure. Using a clearly documented, evidence based approach to create sensitivity assessments allows the assessment and any subsequent decision making or management plans to be readily communicated, transparent and justifiable. The assessments can be replicated and updated where new evidence becomes available ensuring the longevity of the sensitivity assessment tool. The evidence review has reduced the uncertainty around assessments previously undertaken in the MB0102 project (Tillin et al 2010) by assigning a single sensitivity score to the pressures as opposed to a range. Finally, as seagrass habitats may also contribute to ecosystem function and the delivery of ecosystem services, understanding the sensitivity of these biotopes may also support assessment and management in regard to these. Whatever objective measures are applied to data to assess sensitivity, the final sensitivity assessment is indicative. The evidence, the benchmarks, the confidence in the assessments and the limitations of the process, require a sense-check by experienced marine ecologists before the outcome is used in management decisions.

Influência da superfície sedimentar na dinâmica das macroalgas verdes e da sua macroepifauna associada na Ria Formosa

O sistema lagunar, conhecido vulgarmente por Ria Formosa, desenvolve-se na costa meridional Portuguesa, desde o Ancão a ocidente até Cacela a oriente. Com extensão, de aproximadamente 55 km, apresenta a sua maior largura, de 6 km, no sector Norte-Sul entre Faro e o Cabo de Santa Maria. Este sistema é um conjunto de ilhas-barreira que proteje a zona lagunar adjacente à plataforma litoral algarvia, da invasão marinha. A área total do Parque Natural da Ria Formosa é aproximadamente de 163 km2, sendo 48 km2 cobertos por sapal e 32 km2 ocupados por canais, esteiros e baixios (Teixeira & Alvim, 1978). Durante as marés vivas, as áreas intertidais expostas são de aproximadamente 50 km2. Estas áreas são predominantemente cobertas por plantas de sapal (Spartina maritima), angiospérmicas marinhas (Zostera e Cymodocea) e mantos de macroalgas (Entermorpha, Ulva e Fucus). 20 km2 do sistema são ocupados por salinas e aquaculturas (CCRA, 1984).

Comparing Zostera and Spartina environments in relation to carbon burial: a sedimentary and geochemical approach from Ria Formosa

Dissertação de mestrado, Biologia Marinha, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

Estudo de plantas silvestres comestíveis da região mediterrânica como fontes de compostos bioativos

Dissertação de mestrado, Engenharia Biológica, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

Contributo da geoquímica e da sedimentologia na caracterização de influências antropogénicas em ambientes estuarinos

Tese de doutoramento, Geologia (Geoquímica), Universidade de Lisboa, Faculdade de Ciências, 2016

Microbial community composition and mercury cycling in sediments of tagus estuary

Tese de doutoramento, Farmácia (Toxicologia), Universidade de Lisboa, Faculdade de Farmácia, 2016

Potencial de plantas estuarinas na remediação de produtos farmacêuticos e de cuidado pessoal

Dissertação para obtenção do Grau de Mestre em Engenharia do Ambiente, Perfil de Engenharia de Sistemas Ambientais

Âncoras ao largo: um contributo arqueológico para o estudo das actividades marítimas em Lagos na idade Moderna

No decurso de actividades marítimas na baía de Lagos, foram descobertas diversas âncoras ao longo dos anos. Um estudo aprofundado desses artefactos foi organizado para este ano, como parte do levantamento do património cultural subaquático da baía de Lagos, um projecto de investigação arqueológica em curso desde 2006, responsável pela descoberta de vários achados e estações arqueológicas. Sendo as âncoras um dos artefactos dissociáveis das embarcações eo primeiro artefacto a ser enquadrado no equipamento dos navios, estas tornaram-se um dos elementos-chave no estudo da navegação. Em Portugal há muitos exemplares destes objectos datados da Antiguidade, que atestam a presença imemorial de navios e embarcações no nosso litoral. Para aprofundar o nosso conhecimento da cidade de Lagos e o seu papel nacional e internacional, a nível marítimo torna-se necessário localizar, registrar e analisar esta tipologia existente na baía, na tentativa de compreender as diacronias espácias e temporais da actividade maritima. Este estudo visa apurar possíveis locais de ancoragem, pesca, estruturas de apoio à navegação e a localização de locais de pesca específicos datados da Idade Moderna. A descoberta de âncoras de pedra e ferro perto de Porto de Mós, uma das baías do conselho Lagos e onde se encontram a grande maioria dos objectos em estudo, foi um grande passo para a compreensão da história local. Este grande grupo de âncoras atesta uma prática de ancoragem previamente desconhecido nesta área de natureza diacrónica. As âncoras de pedra indicam um uso desta área possivelmente até tempos pré-clássicos, enquanto que, as âncoras de ferro, na sua maioria de Idade Moderna, falam da sua continuidade até ao século XIX.

La Anchoveta (Engraulis ringens J.): conocimiento actual sobre su biología ecología y pesquería

Describe la vida de la anchoveta que comprende reproducción, tasa de crecimiento, longevidad, nutrición y distribución de la especie en el tiempo. Fluctuaciones del stock, en base a las medidas de esfuerzo y captura.

La pesquería de la anchoveta

Presenta una evaluación del stock de anchovetas, basada en los resultados obtenidos por el Instituto del Mar del Perú, para ello efectúa un análisis de toda la información estadística sostenido en los datos biológicos obtenidos por medio de los muestreos, incluyendo los que se realizaron durante los tres meses de veda.

Informe complementario sobre la pesquería de la anchoveta

Desarrolla las consideraciones científicas sobre estimación del promedio de producción máxima sostenida de la anchoveta; la necesidad de establecer una corta temporada de veda como protección de la peladilla y la regulación del esfuerzo pesquero, todo lo cual condujo a las recomendaciones que el IMARPE presentó sobre las medidas que podrían adoptarse para la conservación del stock de anchoveta, en el año 1967.

La pesquería de la anchoveta y recomendaciones para la temporada 1967 - 68

Presenta recomendaciones para la regulación de la pesca de la anchoveta dentro de la temporada de 1967 y 1968.

Investigaciones adicionales de la pesquería de la anchoveta (Engraulis ringens) en el Perú

Examina las relaciones de los efectos de la población de aves guaneras y la pesquería comercial sobre la abundancia y cosecha total sostenible de la anchoveta. Ademas estudia las relaciones promedios entre esfuerzo pesquero, abundancia de la población y cosecha total aprovechando de un modelo generalizado de productividad de poblaciones de peces, afín de proporcionar algunas bases adicionales para decidir si algún otro modelo es más apropiado en este caso que la logística de Verhulst - Pearl.

Panel de expertos informe sobre los efectos económicos de diferentes medidas regulatorias dela pesquería de la anchoveta peruana

Presenta las regulaciones de la pesquería de la anchoveta para asegurar el mantenimiento de las capturas al/o cerca del nivel del rendimiento máximo sostenido y obtener la captura a un costo mínimo y utilizarla para obtener la máxima ganancia dentro de la estructura social, política y técnico económica de la industria.