944 resultados para Algal Blooms


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L'objectiu general del projecte de tesi és el d'estudiar la resposta de les espècies algals a canvis en la disponibilitat de nutrients (i.e. NH4+/NO3-/PO43-). La hipòtesi de partida és que les alteracions en les concentracions absolutes i relatives de nutrients provoquen canvis en l'activitat de les espècies algals que seran més o menys intensos en funció de l’espècie i que són fruit de les característiques eco-evolutives intrínseques de cadascuna. Els objectius concrets es diferencien per l’escala temporal a la que s’observa la resposta, que va des de minuts fins a setmanes: Objectiu 1. Analitzar canvis a curt termini en l’activitat de les espècies degut a augments puntuals en la concentració absoluta i relativa de nutrients (NH4+/NO3-/ PO43-). S'ha vist que algunes espècies redueixen l’activitat fotosintètica a curt termini per destinar tots els recursos a l’assimilació de nutrients (Elrifi i Turpin 1986). S’estudiarà si aquesta pauta es troba de forma generalitzada i si respon a patrons evolutius, funcionals (mida, forma...) o ecològics (disponibilitat de nutrients). Objectiu 2. Analitzar, a mig termini, l’activitat de les espècies algals a diferents concentracions de NH4+/NO3-/ PO43-. Les respostes s’intentaran modelar, de manera que els paràmetres es puguin considerar trets funcionals característics de les espècies. S'estudiarà si la variabilitat en aquests trets respon a patrons evolutius o a d’altres trets funcionals com per exemple la mida. Objectiu 3. Analitzar com afecta, a llarg termini, la disponibilitat de nutrients en la composició d’espècies. Es detectarà quines espècies són més sensibles a les condicions de NH4+:NO3- i N:P del medi, i com es relaciona això amb les respostes específiques trobades en els objectius anteriors.

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This review paper reports the consensus of a technical workshop hosted by the European network, NanoImpactNet (NIN). The workshop aimed to review the collective experience of working at the bench with manufactured nanomaterials (MNMs), and to recommend modifications to existing experimental methods and OECD protocols. Current procedures for cleaning glassware are appropriate for most MNMs, although interference with electrodes may occur. Maintaining exposure is more difficult with MNMs compared to conventional chemicals. A metal salt control is recommended for experiments with metallic MNMs that may release free metal ions. Dispersing agents should be avoided, but if they must be used, then natural or synthetic dispersing agents are possible, and dispersion controls essential. Time constraints and technology gaps indicate that full characterisation of test media during ecotoxicity tests is currently not practical. Details of electron microscopy, dark-field microscopy, a range of spectroscopic methods (EDX, XRD, XANES, EXAFS), light scattering techniques (DLS, SLS) and chromatography are discussed. The development of user-friendly software to predict particle behaviour in test media according to DLVO theory is in progress, and simple optical methods are available to estimate the settling behaviour of suspensions during experiments. However, for soil matrices such simple approaches may not be applicable. Alternatively, a Critical Body Residue approach may be taken in which body concentrations in organisms are related to effects, and toxicity thresholds derived. For microbial assays, the cell wall is a formidable barrier to MNMs and end points that rely on the test substance penetrating the cell may be insensitive. Instead assays based on the cell envelope should be developed for MNMs. In algal growth tests, the abiotic factors that promote particle aggregation in the media (e.g. ionic strength) are also important in providing nutrients, and manipulation of the media to control the dispersion may also inhibit growth. Controls to quantify shading effects, and precise details of lighting regimes, shaking or mixing should be reported in algal tests. Photosynthesis may be more sensitive than traditional growth end points for algae and plants. Tests with invertebrates should consider non-chemical toxicity from particle adherence to the organisms. The use of semi-static exposure methods with fish can reduce the logistical issues of waste water disposal and facilitate aspects of animal husbandry relevant to MMNs. There are concerns that the existing bioaccumulation tests are conceptually flawed for MNMs and that new test(s) are required. In vitro testing strategies, as exemplified by genotoxicity assays, can be modified for MNMs, but the risk of false negatives in some assays is highlighted. In conclusion, most protocols will require some modifications and recommendations are made to aid the researcher at the bench. [Authors]

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While the quality of water in Brushy Creek Lake is currently adequate, a number of factors in the watershed (the surrounding area that drains into the lake) could put that water quality at risk. Sediment from the large watershed could fill in the lake and affect water clarity. Nutrients, like nitrogen and phosphorus, could cause algae blooms and other problems. Without preventative measures, potential manure and chemical spills could harm aquatic life in the lake. Using conservation farming practices and building structures like wetlands will work to maintain and even improve the lake’s water quality. Taking steps now to implement these critical practices will help prevent water quality problems, preserving water quality for future generations.

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Observa una generalizada proliferación de medusas, que llegan a formar “blooms” o poblaciones de alta densidad que podrían reemplazar organismos tradicionalmente dominantes en la cadena trófica.

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Para el estudio de la microalga Dunaliella salina Teodoresco, se colectaron muestras de 2 lagunas hipersalinas; las Salinas de Chimus y las Salinas de Chilca. La metodología usada fue la técnica de micropipeta, tratamiento con antibiótico y la técnica de sedimentación algal, obteniendo cultivos unialgales y axénicos. El medio usado fue medio Johnson modificado en agua de mar, utilizado concentraciones de NaCl (1 – 5M), éste permitió evaluar el crecimiento, densidad y velocidad algal a través de conteo en cámara de Newbahuer y lecturas de absorvancia en espectrofotómetro. La relación entre los métodos de conteo, se realizó con el análisis de regresión potencial. Las mejores densidades algales se observaron en cultivo de concentraciones 1M, 1,5M y 3,5M de NaCl, para las cepas de las salinas de Chimus y Chilca. La mayor densidad algal ( 4,603 x 106 cels. ml-1 equivalente al 56.4 % para la cepa de Chimus) se observó en el cultivo de 1,5M de NaCl. La velocidad de crecimiento durante la fase exponencial para ambas cepas, estuvieron entre 0,56-0,83 div. día-1, con un Td de 29-43 horas, en cámara de Newbahuer como en espectrofotómetro y a las mismas concentraciones de cultivo.

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El cultivo masivo de microalgas en biorreactores presenta una alta tasa de productividad frente a los cultivos abiertos, esta ventaja, aunada a determinados factores ambientales, se relaciona directamente con la cantidad y calidad de biomasa algal obtenida como producto final en el proceso de cultivo. El presente trabajo centró sus investigaciones en la evaluación de los parámetros físicos del ambiente (temperatura e intensidad lumínica), así como, físico-químicos (temperatura, pH y CO2) en la capacidad de carga de los cultivos. La investigación se desarrolló en el invernadero del Área de Biotecnología Acuática, del Instituto del Mar del Perú, dentro del marco del Proyecto IMARPE-EEP-FINCyT, denominado “Determinación de la Biomasa Microalgal potencialmente acumuladora de lípidos para la obtención de combustibles”, según contrato Nº025-FINCYT-PIBAP-2007. Los cultivos se realizaron empleando la cepa IMP-LBA-009, correspondiente a la microalga Nannochloropsis spp., con un flujo de producción semi-continuo por 48 horas, en un periodo de 6 meses, entre julio a diciembre, Bajo condiciones de iluminación (22,003.93 Lux.m-2.seg-1 ±10640.94), temperatura ambiental (31.7°C±2.8), temperatura de cultivo (25.7°C±1.2), CO2 (0.2 g.L-1) y pH (8.36 ±0.18); los resultados mostraron que la producción de biomasa húmeda fue 0.48g.L-1, equivalente a 0.13 g.L-1 de biomasa seca, durante los meses de octubre y noviembre, con una razón de conversión BS/BH del 28%. El impacto lumino-térmico, al interior del invernadero, favoreció el incremento progresivo de la concentración celular del cultivo en biorreactores, por ende, la producción de biomasa húmeda y seca, durante el periodo de trabajo.

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Durante el 2010, se capturó 55 ejemplares de tortuga verde Chelonia mydas en La Aguada (13°51’S y 76°15’W) al sureste de la bahía de Paracas; el número promedio de tortugas capturadas por kilómetro de red tendida fue 3,08±2,5; el tamaño promedio de la LCC fue 60,3±10,5cm; el 78% de los ejemplares presentaron el patrón 5c, 4d, 4i y 11d, 11i, para los escudos centrales, costales y marginales, respectivamente. La TSM donde se capturaron varió entre 15,2 y 20,9 °C, la mayor ocurrencia de tortugas se registró de 18,5 a 20 °C. Los epibiontes más representativos fueron Platylepas hexastylos (56,8%), Conchoderma virgatum (26,9%) y Chelonibia testudinaria (13,3%); la ocurrencia de los ítems alimenticios: Clorophyta (78%), Rhodophyta (30%), Cnidaria (43%), Crustacea (43%), Polichaeta (17%), Mollusca (17%), arena (26%) y plástico (17%); el 72% de las tortugas presentaron cobertura algal, de las cuales el 65% fue el alga verde Enteromorpha sp.

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At this time, about 3,000 different viruses are recognized, but metagenomic studies suggest that these viruses are a small fraction of the viruses that exist in nature. We have explored viral diversity by deep sequencing nucleic acids obtained from virion populations enriched from raw sewage. We identified 234 known viruses, including 17 that infect humans. Plant, insect, and algal viruses as well as bacteriophages were also present. These viruses represented 26 taxonomic families and included viruses with single-stranded DNA (ssDNA), double-stranded DNA (dsDNA), positive-sense ssRNA [ssRNA(¿)], and dsRNA genomes. Novel viruses that could be placed in specific taxa represented 51 different families, making untreated wastewater the most diverse viral metagenome (genetic material recovered directly from environmental samples) examined thus far. However, the vast majority of sequence reads bore little or no sequence relation to known viruses and thus could not be placed into specific taxa. These results show that the vast majority of the viruses on Earth have not yet been characterized. Untreated wastewater provides a rich matrix for identifying novel viruses and for studying virus diversity.

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Historical exploitation of the Mediterranean Sea and the absence of rigorous baselines makes it difficult to evaluate the current health of the marine ecosystems and the efficacy of conservation actions at the ecosystem level. Here we establish the first current baseline and gradient of ecosystem structure of nearshore rocky reefs at the Mediterranean scale. We conducted underwater surveys in 14 marine protected areas and 18 open access sites across the Mediterranean, and across a 31-fold range of fish biomass (from 3.8 to 118 g m22). Our data showed remarkable variation in the structure of rocky reef ecosystems. Multivariate analysis showed three alternative community states: (1) large fish biomass and reefs dominated by non-canopy algae, (2) lower fish biomass but abundant native algal canopies and suspension feeders, and (3) low fish biomass and extensive barrens, with areas covered by turf algae. Our results suggest that the healthiest shallow rocky reef ecosystems in the Mediterranean have both large fish and algal biomass. Protection level and primary production were the only variables significantly correlated to community biomass structure. Fish biomass was significantly larger in well-enforced no-take marine reserves, but there were no significant differences between multi-use marine protected areas (which allow some fishing) and open access areas at the regional scale. The gradients reported here represent a trajectory of degradation that can be used to assess the health of any similar habitat in the Mediterranean, and to evaluate the efficacy of marine protected areas.

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Halecium petrosum and Halecium pusillum on the alga Halimeda tuna from Tossa de Mar, northeastern Spain, were studied. Asexual reproduction of H. petrosum, by stolonisation, occurred throughout the year except for July and August. Asexual reproduction of H. pusillum, by planktonic propagules, occurred throughout the year. Sexual reproduction was limited to the autumn in H. petrosum and spring in H. pusillum. The growth rates of colonies of both species were rapid but declined with increased size. Mean colony size over two consecutive two week periods increased approximately five-fold and three-fold for H. petrosum, and six-fold and four-fold for H. pusillum. Mortality was estimated to be high for both species, especially in summer. The maximum life span of colonies (ramets) of both species was estimated to be only eight weeks. Consequently most colonies do not reproduce sexually. The absence of reproduction of H. petrosum in summer, when the turnover of algal thalli was greatest, probably contributed to the summer decline in its abundance. In both species the genet (clone) survives for unknown, possibly very long, periods by asexual reproduction which facilites colonisation of other substrata.

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Sacoglossan sea slugs (Mollusca: Opisthobranchia) are one of the few groups of specialist herbivores in the marine environment. Sacoglossans feed suctorially on the cell sap of macroalgae, from which they 'steal' chloroplasts (kleptoplasty) and deterrent substances (kleptochemistry), retaining intracellularly both host plastids and chemicals. The ingested chloroplasts continue to photosynthesize for periods ranging from a few hours or days up to 3 months in some species. Shelled, more primitive sacoglossans feed only on the siphonalean green algal genus Caulerpa, and they do not have functional kleptoplasty. The diet of sacoglossans has radiated out from this ancestral food. Among the shell-less Plakobranchidae (=Elysiidae), the more primitive species feed on other siphonales (families Derbesiaceae, Caulerpaceae, Bryopsidaceae and Codiaceae) and fix carbon, while the more 'advanced' species within the Plakobranchidae and Limapontioidae have a more broad dietary range. Most of these 'advanced' species are unable to fix carbon because the chloroplasts of their food algae are mechanically disrupted during ingestion. Mesoherbivores are likely to be eaten if they live on palatable seaweeds, their cryptic coloration and form not always keeping them safe from predators. Sacoglossans prefer to live on and eat chemically defended seaweeds, and they use ingested algal chemicals as deterrents of potential predators. The most ancestral shelled sacoglossans (Oxynoidae) and some Plakobranchidae such as Elysia translucens, Thuridilla hopei and Bosellia mimetica have developed a diet-derived chemical defense mechanism. Oxynoids and Thuridilla hopei are able to biomodify the algal metabolites. However, the Plakobranchidae Elysia timida and E. viridis, together with Limapontioidea species, are characterized by their ability to de novo synthesize polypropionate metabolites. A whole analysis of kleptoplasty and chemical defenses in sacoglossans may offer a better understanding of the ecology and evolution of these specialized opisthobranchs. In this paper we summarize some of the latest findings, related mainly to Mediterranean species, and offer a plausible evolutionary scenario based on the biological and chemical trends we can distinguish in them.

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We examined the effects of riparian vegetation removal on algal dynamics and stream nutrient retention efficiency by comparing NH4-N and PO4-P uptake lengths from a logged and an unlogged reach in Riera Major, a forested Mediterranean stream in northeastern Spain. From June to September 1995, we executed 6 short-term additions of N (as NH4Cl) and P (as Na2HPO4) in a 200-m section to measure nutrient uptake lengths. The study site included 2 clearly differentiated reaches in terms of canopy cover by riparian trees: the first 100 m were completely logged (i.e., the logged reach) and the remaining 100 m were left intact (i.e., the shaded reach). Trees were removed from the banks of the logged reach in the winter previous to our sampling. In the shaded reach, riparian vegetation was dominated by alders (Alnus glutinosa). The study was conducted during summer and fall months when differences in light availability between the 2 reaches were greatest because of forest canopy conditions. Algal biomass and % of stream surface covered by algae were higher in the logged than in the shaded reach, indicating that logging had a stimulatory effect on algae in the stream. Overall, nutrient retention efficiency was higher (i.e., shorter uptake lengths) in the logged than in the shaded reach, especially for PO4-P. Despite a greater increase in PO4-P retention efficiency relative to that of NH4-N following logging, retention efficiency for NH4-N was higher than for PO4-P in both study reaches. The PO4-P mass-transfer coefficient was correlated with primary production in both study reaches, indicating that algal activity plays an important role in controlling PO4-P dynamics in this stream. In contrast, the NH4-N mass-transfer coefficient showed a positive relation-ship only with % of algal coverage in the logged reach, and was not correlated with any algal-related parameter in the shaded reach. The lack of correlation with algal production suggests that mechanisms other than algal activity (i.e., microbial heterotrophic processes or abiotic mechanisms) may also influence NH4-N retention in this stream. Overall, this study shows that logging disturbances in small shaded streams may alter in-stream ecological features that lead to changes in stream nutrient retention efficiency. Moreover, it emphasizes that alteration of the tight linkage between the stream channel and the adjacent riparian zone may directly and indirectly impact biogeochemical processes with implications for stream ecosystem functioning.

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Se ha estudiado la flora algal del Canal de Piragüismo de Aguas Tranquilas durante un año. Se han identificado 90 taxa (20 Cyanophyta, 25 Chlorophyta , 1 Charophyta, 9 Euglenophyta, 31Chrysophyta, 2 Cryptophyta y 2 Pirrophyta). Se aportan datos morfométricos, descripciones y fotografías de microscopio óptico de algunas de las especies. También se incluyen fotografías de diatomeas realizadas al microscopio electrónico de barrido. Se comentan los cambios observados en la composición florística en relación con la mejora de la calidad del agua del canal. También se discute el efecto del progresivo incremento de salinidad del agua sobre las poblaciones de diatomeas.

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Se presentan los resultados de un estudio sobre la flora algal corticícola realizado en el nordeste y sudeste de España. Se citan treinta y siete táxones, dieciséis de los cuales constituyen nuevas citas para España. Se comentan los datos referentes a las principales características morfológicas y se ilustran las especies más relevantes.

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The first comprehensive study of the marine algal flora of Namibia including descriptions and illustrations of most species is presented. The main objective of this work is to report a flora that, until now, has scarcely been studied. The work compiles all the available information on the marine benthic flora of Namibia and provides new data about it composition and biogeography, as well as detailed descriptions and remarks of most of its species. The samples on which this study is based were collected between 1986 and 1989 in the eulittoral and the upper sublittoral zones of the north half of the Namibian coast. According to the present data, the marine benthic flora of Namibia comprises 196 taxa (147 Rhodophyceae, 20 Phaeophyceae, 15 Ulvophyceae, 6 Cladophorophyceae and 8 Bryopsidophyceae), 21 of which has not been recorded from this coasts. This temperate flora is mainly characterized by a low number of species, a low proportion of Phaeophyceae and a high degree of endemism. Concerning the species number, the flora is quite poor due to both the scarce availability of colonizable substratum and the low diversity of habitats. On the other hand, the low proportion of Phaeophyceae is the reason for which the R/P and (R+C)/P ratios take disproportionately high values and so they are not useful in this geographical area. As regards the degree of endemism, the marine benthic flora of Namibia includes quite a high number of taxa endemic to southern Africa (55 taxa; 28.1% of the flora); 25 of these 55 taxa (12.8% of the flora) are endemic to the biogeographic Benguela Marine Province and only Acrosorium cincinnatum is endemic to the Namibian coasts.