Analysis of spatial and temporal patterns in a large reservoir using water quality and hydrodynamic modeling

Effective management of reservoir water resources demands a good command of ecological processes in the waterbody. In this work the three-dimensional finite element hydrodynamic model RMA10 was coupled to an eutrophication model. The models were used together with a methodology for loads estimation to foster the understanding of such processes in the largest reservoir in Western Europe—the Alqueva. Nutrient enrichment and eutrophication are water quality concerns in this man-made impoundment. A total phosphorus and nitrogen loads quantification methodology was developed to estimate the inputs in the reservoir, using point and non-point source data.Field data (including water temperature, wind, water elevation, chlorophyll-a, nutrient concentration and dissolved oxygen) and estimated loads were used as forcing for simulations.The analysis of the modeling results shows that spatial and temporal distributions for water temperature, chlorophyll-a, dissolved oxygen and nutrients are consistent with measured in situ data.Modeling results allowed the identification of likely key impact factors on the water quality of the Alqueva reservoir. It is shown that the particular geomorphological and hydrological characteristics of the reservoir together with local climate features are responsible for the existence of distinct ecological regions within the reservoir.     

Biosorption of uranium from aqueous solutions by Azolla sp. and Limnobium laevigatum

Environmental Science and Pollution Research - The main goal of this study was to assess alternatives to the current challenges on environmental quality and circular economy. The former is here...     

“Return” and Extension Actions After Ethnobotanical Research: The Perceptions and Expectations of a Rural Community in Semi-arid Northeastern Brazil

The scientific community has debated the importance of “return” activities after ethnobiological studies. This issue has provoked debate because it touches on the ethics of research and the relationships with the people involved in these studies. This case study aimed to investigate community perception of an ethnobotany research project that was carried out in the semi-arid region of northeastern Brazil. Furthermore, we reported how the residents of this rural community felt about participating in the activities of “return” that arose from the projects. Our findings demonstrate that “return” activities should be planned from the design phase of the research until its closure as a lifelong process that allows the communities involved to gradually take ownership of the information and actions that are being generated. Similarly, we argue that such activities must be negotiated with the people of the community so that they have decision-making power and autonomy to decide what is most relevant to their lives.     

The Impact of the Extreme Amazonian Flood Season on the Incidence of Viral Gastroenteritis Cases

During the Amazonian flood season in 2012, the Negro River reached its highest level in 110 years, submerging residential and commercial areas which appeared associated with an elevation in the observed gastroenteritis cases in the city of Manaus. The aim of this study was to evaluate the microbiological water quality of the Negro River basin during this extreme flood to investigate this apparent association between the illness cases and the population exposed to the contaminated waters. Forty water samples were collected and analysed for classic and emerging enteric viruses. Human adenoviruses, group A rotaviruses and genogroup II noroviruses were detected in 100, 77.5 and 27.5% of the samples, respectively, in concentrations of 10³–10⁶ GC/L. All samples were compliant with local bacteriological standards. HAdV2 and 41 and RVA G2, P[6], and P[8] were characterised. Astroviruses, sapoviruses, genogroup IV noroviruses, klasseviruses, bocaviruses and aichiviruses were not detected. Statistical analyses showed correlations between river stage level and reported gastroenteritis cases and, also, significant differences between virus concentrations during this extreme event when compared with normal dry seasons and previous flood seasons of the Negro River. These findings suggest an association between the extreme flood experienced and gastrointestinal cases in the affected areas providing circumstantial evidence of causality between the elevations in enteric viruses in surface waters and reported illness.     

Removal of emerging contaminants from wastewater using advanced treatments. A review

Environmental Chemistry Letters - The rise of emerging contaminants in waters challenges the scientific community and water treatment stakeholders to design remediation techniques that are simple,...     

Investigation of two new low-cost adsorbents functionalized with magnetic nanoparticles for the efficient removal of triclosan and a synthetic mixture

Environmental Science and Pollution Research - Triclosan (TCS) is widely used in the production of antibacterial products, being often found in wastewater. Therefore, this study developed new...     

Influence of temperature on muscle-fibre development in larvae of the herringClupea harengus

The development of swimming (myotomal) muscles was studied in herring larvae (Clupea harengus L.) caught in the Firth of Clyde, Scotland, in spring 1990 and reared at either 5, 10 or 15°C. Two muscle-fibre types can be distinguished in the myotomes of herring larvae using ultrastructural criteria. A single layer of small-diameter muscle fibres, packed with mitochondria, is present beneath the entire surface of the skin (superficial muscle fibres). The remaining bulk of the muscle is composed of larger diameter fibres (inner muscle fibres) containing significantly more myofibrils than the superficial fibres. In 1 d-old larvae, the number of inner muscle fibres in myotomes immediately posterior to the yolk-sac was 311±41 at 15°C, 257±22 at 10°C and 187±22 at 5°C (mean±SD,n=6). The average diameter of inner muscle fibres increased with decreasing temperature, so that the total cross-sectional area of muscle was similar at each temperature. After 6 to 7 d, the number of muscle fibres had significantly increased at 15°C (383±25), but not at 10°C (281±32) or 5°C (192±17). In contrast, the average cross-sectional area of inner muscle fibres had increased by 19% at 15°C, 34% at 10°C, and 26% at 5°C. Temperature also influenced the relative proportions and spatial distributions of muscle-fibre organelles. For example, in 1 d-old larvae, the fraction of muscle-fibre volume (volume density) occupied by mitochondria in the superficial fibres was significantly higher at 15°C (46.0%) than at either 5°C (37.6%) or 10°C (38.8%). In the inner muscle fibres, the volume density of mitochondria was 26.1% at 15°C, 20.5% at 10°C and 15.9% at 5°C, whereas the volume density of myofibrils was similar at the three temperatures (33 to 38%). Typically, inner muscle fibres from 10°C larvae, but not from 5 or 15°C larvae contained a large central mitochondrion.     

Residual and cumulative effects of soil application of sewage sludge on corn productivity

The objective of this study was to evaluate the effect of frequent and periodic applications of sewage sludge to the soil, on corn productivity. The experiment was carried out as part of an experiment that has been underway since 1999, using two types of sludge. One came from the Barueri Sewage Treatment Station (BS, which receives both household and industrial sludge) and the other came from the Franca Sewage Treatment Station (FS, which receives only household sludge). The Barueri sludge was applied from 1999 up to the agricultural year of 2003/2004. With the exception of the agricultural years of 2004/2005 and 2005/2006, the Franca sludge was applied up to 2008/2009. All the applications were made in November, with the exception of the first one which was made in April 1999. After harvesting the corn, the soil remained fallow until the next cultivation. The experiment was set up as a completely randomized block design with three replications and the following treatments: control without chemical fertilization or sludge application, mineral fertilization, and dose 1 and dose 2 of sludge (Franca and Barueri). The sludges were applied individually. Dose 1 was calculated by considering the recommended N application for corn. Dose 2 was twice dose 1. It was evident from this work that the successive application of sludge to the soil in doses sufficient to reach the productivity desired with the use of nitrogen fertilizers could cause environmental problems due to N losses to the environment and that the residual and cumulative effects should be considered when calculating the application of sludge to soil.