Terrestrial Reserve Networks Do Not Adequately Represent Aquatic Ecosystems

Las áreas protegidas son una piedra angular de la conservación y han sido diseñadas principalmente alrededor de atributos terrestres. Las especies y ecosistemas dulceacuícolas se encuentran en peligro, pero la efectividad de las áreas protegidas existentes para representar las características dulceacuícolas es poco conocida. Utilizando las aguas interiores de Michigan como un caso de prueba, cuantificamos la cobertura de cuatro atributos dulceacuícolas clave (humedales, zonas ribereñas, recarga de agua subterránea y especies raras) en las tierras conservadas y las comparamos con la representación de los atributos terrestres. Los humedales estaban incluidos en las áreas protegidas más a menudo que lo esperado por azar, pero las zonas ribereñas estuvieron insuficientemente representadas en todas las tierras protegidas (GAP1–3), particularmente en manantiales y ríos grandes. Sin embargo, las zonas ribereñas estuvieron bien representadas en las tierras con protección estricta (GAP 1–2) debido a la contribución del Programa Nacional de Ríos Silvestres y Escénicos. La representación de áreas de recarga de aguas subterráneas generalmente fue proporcional al área de la red de reservas dentro de cuencas hidrológicas, aunque un sitio importante de recarga asociado con algunos de los ríos más valiosos en Michigan estaba casi totalmente desprotegido. La representación de especies en áreas protegidas difirió significativamente entre las especies acuáticas obligadas, de humedales y terrestres, con una representación generalmente mayor para las especies terrestres y menor para las acuáticas. Nuestros resultados ilustran la necesidad de evaluar y atender la representación de los atributos dulceacuícolas dentro de las áreas protegidas y el valor de ampliar el análisis de brechas y otras evaluaciones de áreas protegidas para incluir los procesos ecosistémicos claves que son requisito para la conservación a largo plazo de especies y ecosistemas. Concluimos que las redes de áreas protegidas orientadas al medio terrestre proporcionan una red de seguridad débil para los atributos acuáticos, lo que significa que se requiere planeación y manejo complementario tanto para objetivos de conservación dulceacuícolas como terrestres.Peer Reviewedhttp://deepblue.lib.umich.edu/bitstream/2027.42/79138/1/COBI_1460_sm_AppendixS3.pdfhttp://deepblue.lib.umich.edu/bitstream/2027.42/79138/2/COBI_1460_sm_AppendixS1.pdfhttp://deepblue.lib.umich.edu/bitstream/2027.42/79138/3/j.1523-1739.2010.01460.x.pd

The role of river morphodynamic disturbance and groundwater hydrology as driving factors of riparian landscape patterns in mediterranean rivers

Original ResearchFluvial disturbances, especially floods and droughts, are the main drivers of the successional patterns of riparian vegetation. Those disturbances control the riparian landscape dynamics through the direct interaction between flow and vegetation. The main aim of this work is to investigate the specific paths by which fluvial disturbances, distributed by its components of groundwater hydrology (grndh) and morphodynamic disturbance (mrphd), drive riparian landscape patterns as characterized by the location (position in the river corridor) and shape (physical form of the patch) of vegetation patches in Mediterranean rivers. Specifically, this work assesses how the different components of fluvial disturbances affect these features in general and particularly in each succession phase of riparian vegetation. grndh and mrphd were defined by time and intensity weighted indexes calculated, respectively, from the mean annual water table elevations and the annual maximum instantaneous discharge shear stresses of the previous decade. The interactions between riparian landscape features and fluvial disturbances were assessed by confirmatory factor analysis using structural equation modeling. Two hypothetical models for patch location and shape were conceptualized and tested against empirical data collected from 220 patches at four different study sites. Both models were successfully fitted, meaning that they adequately depicted the relationships between the variables. Furthermore, the models achieved a good adjustment for the observed data, based on the evaluation of several approximate fit indexes. The patch location model explained approximately 80% of the patch location variability, demonstrating that the location of the riparian patches is primarily driven by grndh, while the mrphd had very little effect on this feature. In a multigroup analysis regarding the succession phases of riparian vegetation, the fitted model explained more than 68% of the variance of the data, confirming the results of the general model. The patch shape model explained nearly 13% of the patch shape variability, in which the disturbances came to have less influence on driving this feature. However, grndh continues to be the primary driver of riparian vegetation between the two disturbance factors, despite the proportional increase of the mrphd effect to approximately a third of the grndh effectinfo:eu-repo/semantics/publishedVersio

The natural wood regime in rivers

International audienc

Adaptive Management of Riverine Socio-ecological Systems

If ongoing change in ecosystems and society can render inflexible policies obsolete, then management must dynamically adapt as a counter to perennial uncertainty. This chapter describes a general synthesis of how to make decision-making more adaptive and then explores the barriers to learning in management. We then describe how one such process, known as adaptive management (AM), has been applied in different river basins, on which basis we discuss AM’s strengths and limitations in various resource management contexts

Characterizing geomorphological change to support sustainable river restoration and management

The hydrology and geomorphology of most rivers has been fundamentally altered through a long history of human interventions including modification of river channels, floodplains, and wider changes in the landscape that affect water and sediment delivery to the river. Resultant alterations in fluvial forms and processes have negatively impacted river ecology via the loss of physical habitat, disruption to the longitudinal continuity of the river, and lateral disconnection between aquatic, wetland, and terrestrial ecosystems. Through a characterization of geomorphological change, it is possible to peel back the layers of time to investigate how and why a river has changed. Process rates can be assessed, the historical condition of rivers can be determined, the trajectories of past changes can be reconstructed, and the role of specific human interventions in these geomorphological changes can be assessed. To achieve this, hydrological, geomorphological, and riparian vegetation characteristics are investigated within a hierarchy of spatial scales using a range of data sources. A temporal analysis of fluvial geomorphology supports process-based management that targets underlying problems. In this way, effective, sustainable management and restoration solutions can be developed that recognize the underlying drivers of geomorphological change, the constraints imposed on current fluvial processes, and the possible evolutionary trajectories and timelines of change under different future management scenarios. Catchment/river basin planning, natural flood risk management, the identification and appraisal of pressures, and the assessment of restoration needs and objectives would all benefit from a thorough temporal analysis of fluvial geomorphology

How Do They Do It? – Understanding the Success of Marine Invasive Species

From the depths of the oceans to the shallow estuaries and wetlands of our coasts, organisms of the marine environment are teeming with unique adaptations to cope with a multitude of varying environmental conditions. With millions of years and a vast volume of water to call their home, they have become quite adept at developing specialized and unique techniques for survival and – given increasing human mediated transport – biological invasions. A growing world human population and a global economy drives the transportation of goods across the oceans and with them invasive species via ballast water and attached to ship hulls. In any given 24-hour period, there are about 10,000 species being transported across different biogeographic regions. If any of them manage to take hold and establish a range in an exotic habitat, the implications for local ecosystems can be costly. This review on marine invasions highlights trends among successful non-indigenous species (NIS), from vectors of transport to ecological and physiological plasticity. Apart from summarizing patterns of successful invasions, it discusses the implications of how successfully established NIS impact the local environment, economy and human health. Finally, it looks to the future and discusses what questions need to be addressed and what models can tell us about what the outlook on future marine invasions is

The Remediation of Abandoned Iron Ore Mine Subsidence in Rockaway Township, New Jersey

This report represents the twenty-seventh and Final Technical Progress Report issued in connection with the subsidence remediation projects undertaken by Rockaway Township in Morris County, New Jersey. This report provides a summary of the major project work accomplished during this last reporting period ending June 30, 2010 and a summary of the work accomplished since the agreement inception in 1997. This report is issued as part of the project reporting provisions set forth in the Cooperatorâs Agreement between the United States Government - Department of Energy, and Rockaway Township. The purpose of the Cooperatorâs Agreement is for the Department of Energy to provide technical and financial assistance in a coordinated effort with Rockaway Township to develop and implement a multi-phased plan to remediate ground stability problems associated with abandoned mining activity. Primarily during the 1800âs, extensive iron ore mining and prospecting was undertaken in Rockaway Township, part of the Dover District Mining region in Morris County. The abandoned mining activity has resulted in public safety hazards associated with ground collapse and surface subsidence features evolving in both developed and undeveloped areas within Rockaway Township. At the Green Pond Mine site at the Townshipâs Jacobs Road Compost Storage Facility, surface monitoring continued after completion of construction in September 2003. Surface monitoring was conducted periodically at the Mt. Hope Road subsidence work area and adjacent areas after the January 2000 construction effort. In March 2007, a seventh collapse occurred over a portion of the White Meadow Mine in a public roadway at the intersection of Iowa and Erie Avenues in Rockaway Township. After test drilling, this portion of the mine was remediated by drilling and grouting the stopes