An Assessment of U.S. Stream Compensatory Mitigation Policy: Necessary Changes to Protect Ecosystem Functions and Services

Compensatory mitigation of impacted streams and wetlands has increased over the past two decades, with the associated industry spending over US$2.9 billion in aquatic restoration annually. Despite these expenditures, evaluations by the National Research Council and U.S. Government Accountability Office have provided evidence that compensatory mitigation practices are failing to protect aquatic resource functions and services, and vague federal policy and inadequate evaluation of compensatory mitigation projects are to blame. To address these weaknesses, an update to federal regulations on compensatory mitigation was released in 2008. Additionally, the 2012 Reissuance of Nationwide Permits, some of which affects compensatory stream mitigation, was recently published. Current policy, as reflected in these documents, still uses nonspecific language to direct compensatory stream mitigation leaving most implementation decisions to the local U.S. Army Corps of Engineers district. The majority of federal mitigation policy has focused on wetland compensation, with other aquatic resources receiving less attention (e.g., streams). In this article, weaknesses of current policy are discussed, as are suggested policy changes to minimize the loss of stream ecosystem functions and services. Compensatory mitigation policy should clearly define key terms, incorporate adaptive management procedures, and provide guidelines for determining mitigation costs and compensation ratio requirements.     

Partikelentfernung in der Trinkwasseraufbereitung: Problematiken und Lösungsansätze

The drinking water treatment plant (WTP) in Irsch-Treves is one of the WTPs operated by the Public Utility Company of Treves (SWT) responsible for supplying the city of Treves with drinking water. This treatment plant has been responsible for the treatment of raw, soft water from the oligotrophic reservoir Riveris since 1958. The main functions of the WTP are the removal of particulate matter, manganese, iron, aluminium and organic material, especially humic substances. The removal of particulate matter such as bacteria, other microorganisms and plankton is very important to ensure a microbiologically and hygienically stable drinking water. Insufficient removal of particulate manganese may lead to manganese scaling in the supply system and, in extreme conditions, may lead to a brown-coloured drinking water. The so called Multi-Barrier-System is being used in the entire water treatment process. Under this system, great importance is given to the monitoring of the catchment area, the inflows, and the reservoirs. After a preliminary and subsequent sedimentation and biological treatment in the preliminary and in the main reservoirs respectively, the raw water is finally treated through flocculation filtration over the rapid multi-layer sand filters in the WTP Irsch. With this approach, only a rigid application of the above mentioned steps and the application of the latest recognized technology to maintain the supply system can best guarantee a constant supply of clean drinking water. Online particle count in raw water and in drinking water is one of the main quality control measures applied in the WTP Irsch. The conventional flocculation filtration is not always able to fulfil the increasing quality demands for drinking water, especially during adverse raw water quality conditions. This is the reason why more and more membrane filtration units are currently being installed in completely new plants, as substitutes in conventional plants, or for upgrade purposes. The SWT is currently planning an enlargement and upgrade of the WTP Irsch, integrating ultrafiltration, which was successfully tested in a pilot study. The upgrade of the elimination of particulate matter is one of the most important targets, after the enlargement and upgrade of the plant.     

Neue Aspekte in der Behandlung von Siedlungsabflüssen

The surface runoff from urban areas is one of the most important sources of pollutants emitted into surface waters. Suspended solids which act as a transport vehicle for many anthropogenic pollutants (e.?g. heavy metals, PAH) are a key factor in this regard. The development of efficient measures of storm water runoff treatment thus requires a further differentiation of suspended solids in a fine (clay and silt) and coarse (sand and gravel) fraction. Both fractions show distinctly different characteristics in pollutant loading, transport and retention on urban surfaces and sewer systems. The primary aim of storm water runoff treatment is the reduction of the fine particles which are always highly loaded with anthropogenic pollutants. In contrast the coarse particles are almost unpolluted especially if they have a low organic share. The widespread sedimentation tanks with surface loadings between 10 and 2?m/h are very inefficient. A significant, save and lasting reduction of the emitted load of fine particles requires a considerable reduction of the surface loads. That can be achieved with the installation of lamellar settler or the utilization of the very large volumes of flood management tanks frequently present in urban areas. Filtration plants are highly efficient but there application in urban areas is limited due to their high space demands.     

A nutrient-transfer model to explain the fate of phosphorus and sulphur in a Grazed Hill-Country pasture

A nutrient-transfer model was developed using a mass balance approach to explain the variations in the amounts of soil phosphorus (P) and sulphur (S) found across a range of slopes and aspects in four 10-ha farmlets located in summer-moist hill-country pastures in the southern North Island of New Zealand. The farmlets were continuously grazed by sheep for a period of 12 years, during which time they received a total of 115, 187, 387, 603 and 126, 201, 405, 630 kg ha⁻¹ of P and S, respectively, as single superphosphate (SSP). The model takes account of the effect of topography and local climate on stock behaviour, herbage accumulation and its nutrient content, pasture utilization and the uneven nutrient return through excreta.The developed P model was reliable. The predictions of the transfer model explained 95% of variation in soil P amounts (0–150 mm depth) between farmlets (n=4), 89% of variation between slope units (n=12) and 79% between slope-aspect units (n=36) across all farmlets. When S input parameters were substituted for P parameters, the model was unable to predict the measured soil S levels in any of the four farmlets. Unlike P, S is subject to losses by leaching from these soils. The differences between predicted and measured soil S amounts were used to estimate S leaching losses and pinpoint areas from where they occurred.The concept of modelling the fate of P in P and S fertilized systems and then using the calculated nutrient-transfer functions of the model to evaluate the fate of S provides invaluable information for developing strategies for improving the efficiency of S fertilizer use.     

Evidence for a water-borne cue inducing metamorphosis in the dorid nudibranch mollusc Adalaria proxima (Gastropoda: Nudibranchia)

The dorid nudibranch Adalaria proxima (Alder & Hancock) is a specialist predator of the cheilostome bryozoan Electra pilosa (L.). Natural induction of metamorphosis of the pelagic lecithotrophic larva of A. proxima was assessed in response to solutions from sonicated prey tissue and (live) E. pilosa-conditioned seawater (Electra-CSW). We exploited the tendency of larvae to become entrapped (rafted) at the air-water interface in cultures to examine whether larvae require direct contact with the live prey for metamorphosis to proceed. Larvae metamorphosed when rafted above colonies of live E. pilosa, above plankton mesh bags isolating live E. pilosa, and in choline chloride controls; there was no metamorphosis of larvae that were rafted in filtered seawater controls. Entrapped veliger shells remained rafted throughout the experimental period in all cases. No metamorphosis occurred in treatments containing either the supernatants or pelleted particulates obtained from sonicated colonies of E. pilosa. Both one-colony and three-colony Electra-CSW induced metamorphosis of larvae. These data are at variance with previous results in showing that direct contact with the live prey is not necessary for metamorphosis to proceed. Furthermore, the fact that competent larvae metamorphosed in response to Electra-CSW in the absence of any other cue strongly suggests that the inductive cue is water-borne.     

Potential effects of climate change on birds of the Northeast

We used three approaches to assess potential effects of climate change on birds of the Northeast. First, we created distribution and abundance models for common bird species using climate, elevation, and tree species variables and modeled how bird distributions might change as habitats shift. Second, we assessed potential effects on high-elevation birds, especially Bicknell’s thrush (Catharus bicknelli), that may be particularly vulnerable to climate change, by using statistical associations between climate, spruce-fir forest vegetation and bird survey data. Last, we complemented these projections with an assessment of how habitat quality of a migratory songbird, the black-throated blue warbler (Dendroica caerulescens) might be affected by climate change. Large changes in bird communities of the Northeast are likely to result from climate change, and these changes will be most dramatic under a scenario of continued high emissions. Indeed, high-elevation bird species may currently be at the threshold of critical change with as little as 1°C warming reducing suitable habitat by more than half. Species at mid elevations are likely to experience declines in habitat quality that could affect demography. Although not all species will be affected adversely, some of the Northeast’s iconic species, such as common loon and black-capped chickadee, and some of its most abundant species, including several neotropical migrants, are projected to decline significantly in abundance under all climate change scenarios. No clear mitigation strategies are apparent, as shifts in species’ abundances and ranges will occur across all habitat types and for species with widely differing ecologies.