Interactions of bacteria and fungi on decomposing litter: differential extracellular enzyme activities

Fungi and bacteria are key agents in plant litter decomposition in freshwater ecosystems. However, the specific roles of these two groups and their interactions during the decomposition process are unclear. We compared the growth and patterns of degradativeenzymes expressed by communities of bacteria and fungi grown separately and in coexistence on Phragmites leaves. The two groups displayed both synergistic and antagonistic interactions. Bacteria grew better together with fungi than alone. In addition, there was a negative effect of bacteria on fungi, which appeared to be caused by suppression of fungal growth and biomass accrual rather than specifically affecting enzyme activity. Fungi growing alone had a high capacity for the decomposition of plant polymers such as lignin, cellulose, and hemicellulose. In contrast, enzyme activities were in general low when bacteria grew alone, and the activity of key enzymes in the degradation of lignin and cellulose (phenol oxidase and cellobiohydrolase) was undetectable in the bacteria-only treatment. Still, biomass-specific activities of most enzymes were higher in bacteria than in fungi. The low total activity and growth of bacteria in the absence of fungi in spite of apparent high enzymatic efficiency during the degradation of many substrates suggest that fungi provide the bacteria with resources that the bacteria were not able to acquire on their own, most probably intermediate decomposition products released by fungi that could be used by bacteria

Quantifying seasonality along a latitudinal gradient: from stream temperature to growth of invasive mosquitofish

Most ecosystems undergo substantial variation over the seasons, ranging from changes in abiotic features, such as temperature, light and precipitation, to changes in species abundance and composition. How seasonality varies along latitudinal gradients is not well known in freshwater ecosystems, despite being very important in predicting the effects of climate change and in helping to advance ecological understanding. Stream temperature is often well correlated with air temperature and influences many ecosystem features such as growth and metabolism of most aquatic organisms. We evaluated the degree of seasonality in ten river mouths along a latitudinal gradient for a set of variables, ranging from air and water temperatures, to physical and chemical properties of water and growth of an invasive fish species (eastern mosquitofish, Gambusia holbrooki ). Our results show that although most of the variation in air temperature was explained by latitude and season, this was not the case for water features, including temperature, in lowland Mediterranean streams, which depended less on season and much more on local factors. Similarly, although there was evidence of latitude-dependent seasonality in fish growth, the relationship was nonlinear and weak and the significant latitudinal differences in growth rates observed during winter were compensated later in the year and did not result in overall differences in size and growth. Our results suggest that although latitudinal differences in air temperature cascade through properties of freshwater ecosystems, local factors and complex interactions often override the water temperature variation with latitude and might therefore hinder projections of species distribution models and effects of climate change

How are riparian plants distributed along the riverbank topographic gradient in Mediterranean rivers? Application to minimally altered river stretches in Southern Spain.

Species structure and composition in Mediterranean riparian forests are determined by hydrological features, longitudinal zonation, and riverbank topography. This study assesses the distribution of four native riparian plants along the riverbank topographic gradient in three river stretches in southern Spain, with special emphasis on the occupation of adult and young feet of each species. The studied stretches suffered minimal human disturbances, displayed semi-arid conditions, and had wide riparian areas to allow the development of the target species: black alder (Alnus glutinosa), salvia leaf willow (Salix salviifolia), narrow-leafed ash (Fraxinus angustifolia), and oleander (Nerium oleander). Thalweg height was used to define the riverbank topographic gradient. The results showed a preferential zone for black alder and salvia leaf willow in the range of 0-150 cm from the channel thalweg, with adult alders and willows being more common between 51 and 150 cm and young alders being more common under 50 cm. Conversely, narrow-leafed ash and oleander were much more frequent, and showed greater development, in the ranges of 151-200 cm and 201-250 cm, respectively, whereas the young feet of both species covered the entire topographic range. Adult feet of the four species were spatially segregated along the riverbank topographic gradient, indicating their differential ability to cope with water stress from the non-tolerant alders and willows to more tolerant narrow-leafed ash trees and oleanders. Young feet, however, showed a strategy more closely linked to the initial availability of colonisation sites within riparian areas to the dispersion strategy of each species and to the distribution of adult feet. In Mediterranean areas, where riparian management has traditionally faced great challenges, the incorporation of species preferences along riverbank gradients could improve the performance of restoration projects.

Biomonitoreo de la calidad del agua en los ríos ibéricos: lecciones aprendidas.

Los autores resumen en un decálogo la experiencia de más de 30 años de estudio de los ríos españoles con dos focos principales: el uso de macroinvertebrados para la obtención de la calidad biológica y el diseño de sistemas de evaluación del estado ecológico de los ríos. Después de una introducción general y de un resumen de cómo se gestaron los estudios de biomonitoreo en España, los autores analizan los trabajos que se han publicado en la revista Limnetica sobre este tema. Se usan estos datos para ilustrar los puntos relevantes en el diseño y aplicación del biomonitoreo, que es posteriormente resumido en un decálogo. Este está pensado para contener todos los puntos necesarios para que el diseño de un sistema de biomonitoreo cumpla las especificaciones de la Directiva Marco del Agua (DMA). Los diez puntos analizados son: 1) establecimiento de la zona de estudio; 2) recursos humanos y materiales disponibles; 3) tipología de ríos; 4) establecimiento de las condiciones de referencia; 5) protocolos de muestreo; 6) métricas a utilizar; 7) establecimiento de los cortes de calidad y relación de las métricas con las presiones; 8) mapas de estado ecológico usando el valor relativo respecto a los valores de referencia (el EQR: Ecological Quality Ratio); 9) control de calidad; 10) uso de los datos para establecer los objetivos de calidad y el programa de medidas. En la revista Limnetica se han publicado desde su inicio en el año 1981 un total de 641 trabajos, de los cuales un 42% trataban de ríos y un 18% se centraban exclusivamente en el biomonitoreo. La mayor parte de los trabajos de biomonitoreo publicados utilizaron a los macroinvertebrados como elemento de calidad (88%), pero relativamente pocos (menos del 20%) usaron la tipología y las condiciones de referencia para establecer correctamente las clases de calidad. Se analiza por separado el período anterior al año 2002, y con un número similar de trabajos se advierte un mayor porcentaje de trabajos de biomonitoreo después de 2002. Sin embargo, y a pesar de la existencia de la DMA desde el año 2000, muchos trabajos publicados en Limnetica a partir de 2002 (cuando se hizo un número especial sobre biomonitoreo en ríos mediterráneos) no cumplen los requisitos que demanda esta Directiva. En este momento, después de la experiencia que se tiene por la implementación de la DMA, cualquier sistema de biomonitoreo desarrollado en Europa debe ser comparable a los que existen actualmente, especialmente a la métrica común de intercalibración (ICM).Este decálogo presenta los pasos necesarios para que cuando se diseñe un sistema de muestreo este cumpla los requisitos que demanda la DMA.

The Andean Biotic Index (ABI): revised tolerance to pollution values for macroinvertebrate families and index performance evaluation.

Score-based biotic indices are widely used to evaluate the water quality of streams and rivers. Few adaptations of these indices have been done for South America because there is a lack of knowledge on mac-roinvertebrate taxonomy, distribution and tolerance to pollution in the region. Several areas in the Andes are densely populated and there is need for methods to assess the impact of increasing human pressures on aquatic ecosystems. Considering the unique ecological and geographical features of the Andes, macroinvertebrate indices used in other regions must be adapted with caution. Here we present a review of the literature on mac-roinvertebrate distribution and tolerance to pollution in Andean areas above 2 000masl. Using these data, we propose an Andean Biotic Index (ABI), which is based on the BMWP index. In general, ABI includes fewer macroinvertebrate families than in other regions of the world where the BMWP index has been applied because altitude restricts the distribution of several families. Our review shows that in the high Andes, the tolerance of several macroinvertebrate families to pollution differs from those reported in other areas. We tested the ABI index in two basins in Ecuador and Peru, and compared it to other BMWP adaptations using the reference condi-tion approach. The ABI index is extremely useful for detecting the general impairment of rivers but class quality boundaries should be defined independently for each basin because reference conditions may be different. The ABI is widely used in Ecuador and Peru, with high correlations with land-use pressures in several studies. The ABI index is an integral part of the new multimetric index designed for high Andean streams (IMEERA). Rev. Biol. Trop. 62 (Suppl. 2): 249-273. Epub 2014 April 01.

Clave para la determinación de exuvias pupales de los quironómidos (Diptera: Chironomidae) de ríos altoandinos tropicales

The Chironomidae is a cosmopolitan family of Nematoceran flies with more than 20 000 species described. However the diversity of genera and species of the family in the Andean region beyond the 2 000m.a.s.l are scarcely known. We conducted faunal surveys and biomonitoring research in different streams of Colombia, Ecuador and Peru from May 2005 to October 2011. Based on specimens collections, and a taxonomic key was developed to identify pupae and pupal exuviae of 46 genera of midges (Diptera, Chironomidae) collected from streams at high altitude areas on the Andean tropical mountains. We included illustrations and brief taxonomic descriptions for all genera, of which several ones have not yet been formally described; in this latter case we used the nomenclature of Roback & Coffman (1983). For two genera, Cricotopus and Genus 1, keys to the most common morphospecies were provided. Results showed that in this area the chironomid assemblages are dominated by the members of the subfamily Orthocladiinae (22 genera) followed by the Chironominae (13). Six genera of Tanypodinae were identified, while only three and two genera were present from subfamilies Podonominae and Diamesinae. This key may be very useful for both studies about drift in streams, and for biomonitoring purposes.

Modelling nitrogen and phosphorus loads in a Mediterranean river catchment (La Tordera, NE Spain)

Human activities have resulted in increased nutrient levels in many rivers all over Europe. Sustainable management of river basins demands an assessment of the causes and consequences of human alteration of nutrient flows, together with an evaluation of management options. In the context of an integrated and interdisciplinary environmental assessment (IEA) of nutrient flows, we present and discuss the application of the nutrient emission model MONERIS (MOdelling Nutrient Emissions into River Systems) to the Catalan river basin, La Tordera (north-east Spain), for the period 1996–2002. After a successful calibration and verification process (Nash-Sutcliffe efficiencies E=0.85 for phosphorus and E=0.86 for nitrogen), the application of the model MONERIS proved to be useful in estimating nutrient loads. Crucial for model calibration, in-stream retention was estimated to be about 50 % of nutrient emissions on an annual basis. Through this process, we identified the importance of point sources for phosphorus emissions (about 94% for 1996–2002), and diffuse sources, especially inputs via groundwater, for nitrogen emissions (about 31% for 1996–2002). Despite hurdles related to model structure, observed loads, and input data encountered during the modelling process, MONERIS provided a good representation of the major interannual and spatial patterns in nutrient emissions. An analysis of the model uncertainty and sensitivity to input data indicates that the model MONERIS, even in data-starved Mediterranean catchments, may be profitably used by water managers for evaluating quantitative nutrient emission scenarios for the purpose of managing river basins. As an example of scenario modelling, an analysis of the changes in nutrient emissions through two different future scenarios allowed the identification of a set of relevant measures to reduce nutrient loads.

Per una comprensió històrica de les activitats aquàtiques : una mirada educativa

Una atenta observació de les activitats aquàtiques de caire educatiu mostra que aquestes pràctiques es fonamenten, principalment, en constructes que no són propis de la pedagogia, ans provenen de l’antropologia i/o de les cultures establertes a l’entorn de l’aigua. Així, el present article es pregunta pels sentits que acompanyen aquests imaginaris que sorgeixen de la relació que s’estableix entre l’home i el medi aquàtic. Per a fer-ho, s’utilitza el recurs hermenèutic de comprendre quines han estat les pràctiques aquàtiques que han anat sorgint al llarg de la història, ja que la idea principal del treball sosté que l’activitat educativa en el medi aquàtic s’ha construït a partir dels imaginaris culturals, sorgits de les mateixes pràctiques aquàtiques que l’han precedit.

La biota de los ríos : los peces

Capítol 15 del llibre 'Conceptos y técnicas en ecología fluvial' que es refereix als peixos dels sistemes fluvials

Presentación: importancia de los ríos

Capítol 1 del llibre 'Conceptos y técnicas en ecología fluvial' que es refereix a la importància dels rius per ser els que connecten les conques terrestres amb l'atmosfera i amb el mar; els que transporten a més a més d'aigua, sals, sediments i organismes i on es produeixen complexes reaccions químiques i biològiques, que són en part responsables, de les característiques químiques de l'aigua que es troba als llacs i als oceans

El río como ecosistema

Capítol 2 del llibre 'Conceptos y técnicas en ecología fluvial' que es refereix al riu com ecosistema

Otros factores físicos de importancia para los seres vivos : luz, temperatura, corriente

Capítol 9 del llibre 'Conceptos y técnicas en ecología fluvial' que es refereix a la influència de factors com la temperatura de l'aigua, la disponibilitat de llum i la velocitat de la corrent en els organismes que viuen en els sistemes fluvials

Anàlisi territorial de la vulnerabilitat dels recursos hídrics davant del canvi climàtic

En aquest capítol es descriuen els mecanismes que determinen la resposta dels sistemes hidrològics al canvi climàtic en el context de Catalunya i propostes per a determinar-ne la vulnerabilitat

The Problem of Invasive Species in River Ecosystems

Invasive nonnative species are a major problem in river ecosystems, and have large ecological and economic costs. Few ecosystems can resist invasions. The species that tend to invade most readily are those that humans. Introduce the most, and the ecosystems they invade are those with the most human activity. Most invasions are irreversible, and control is expensive, so efforts should be focused on prevention of future invasions

Concluding Remarks on River Conservation

We have pragmatic and ethical obligations to conserve rivers and their biodiversity. This chapter outlines how and why river conservation is important. To make a difference, we must act as individuals and groups, using water wisely and protecting vulnerable assets such as water quality, riparian zones and aquatic biodiversity