Identification of Mn-oxide minerals in some soils from Devon,UK, and their varying capacity to adsorb Co and Cu

A number of Mn-oxide minerals in soils from a farm in North Devon have been tentatively identified using a combination of advanced analytical techniques: scanning electron microscopy (SEM), scanning electron microprobe (SEMP), X-ray diffraction (XRD) and bulk chemical analysis by wet digestion followed by inductively-coupled plasma spectrometry (ICP). The minerals lithiophorite and hollandite are thought to occur throughout the study area although there is considerable geographical variation in the proportions of minerals present. Bimessite, vernadite, romanechite, todorokite and cryptomelane may also be present, although in smaller amounts. The use of SEMP, together with a simple sorption experiment, has allowed a study of the extent of uptake of Co and Cu by different Mn-oxide minerals. Lithiophorite appears to take up Co and Cu more effectively than hollandite within a pH range of 4–6.     

PATTERNS OF ENERGY CONSUMPTION BY THE RURAL AND URBAN POOR IN DEVELOPING COUNTRIES

From the rudimentary data available on the domestic energy consumption of the urban and rural poor in developing countries it appears that consumption by the poor in much of the developing world is at bare subsistence levels. Despite generally higher incomes, the domestic energy consumption of the urban poor appears to be no higher in Btu terms than that of the rural poor due to the more thermally efficient fuel supplies used by the urban poor. A further tentative conclusion is that for similar reasons related to the changing efficiency of the fuel supply system, energy consumption measured in quantity terms rises within a given area by less than the rise in income at lower income levels. As incomes rise there is a tendency to switch to more efficient fuels in a manner analogous to the contrast in energy consumption patterns between urban and rural areas. Thus a rising demand for energy services can be accomodated by a less than proportionate gross input. En examinant les données rudimentaires dont on dispose sur la consommation domestique en énergie des classes urbaines et rurales défavorisées des pays en développement, il ressort que la consommation de ces classes dans la plupart de ces pays se situe à des niveaux de simple subsistence. Malgré des revenus généralement plus élevés, la consommation domestique en énergie des classes urbaines défavorisées ne semble pas étre supérieure en termes d'unités thermiques britanniques à celle des classes rurales défavorisées en raison d'approvisionnements en combustibles thermiques à meilleur rendement dans les villes. Une autre conclusion provisoire envisage que pour des raisons similaires ayant trait aux fluctuations de l'efficacité du système d'approvisionnement en combustibles, la consommation énergétique mesurée en termes quantitatifs augments dans une zone donnée moins rapidement que les revenus aux échelons inférieurs. Au fur et à mesure que les revenus progressent, la tendance à utiliser des combustibles a meilleur rendement reflète le même contraste existant dans les modes de consommation en énergie entre les zones urbaines et rurales. On peut donc satisfaire les besoins croissants en matière d'énergie par des coûts de production proportionnellement moins élevés. Por los datos rudimentarios disponibles sobre el consumo doméstico de energía de los estratos probres rural y urbano de los países en desarrollo, parece ser que dicho consumo está en los límites del nivel de subsistencia. A pesar del relativo mayor ingreso de los estratos pobres urbanos, el consumo de energía de éstos no parece ser, en términos fíisicos, mayor que la de los estratos pobres rurales debido a que aquellos emplean combustibles que pueden usarse con mayor eficiencia térmica. Otra conclusión tentativa es que debido a razones similares a esta disparidad de eficiencia, la cantidad de energía consumida en un sector pobre aumenta en una proporción menor que el aumento del ingreso. En forma análoga a la deferencia entre las tendencias de consumo entre grupos ru rales y urbanos, a mayores niveles de ingreso en una misma área hay una tendencia a usar combustibles más eficientes. Como resultado una demanda creciente de energía puede ser satisfecha con un amento proporcionalmente menor de suministrode combustible.     

The acetochlor registration partnership surface water monitoring program for four corn herbicides

A surface drinking water monitoring program for four corn (Zea mays L.) herbicides was conducted during 1995-2001. Stratified random sampling was used to select 175 community water systems (CWSs) within a 12-state area, with an emphasis on the most vulnerable sites, based on corn intensity and watershed size. Finished drinking water was monitored at all sites, and raw water was monitored at many sites using activated carbon, which was shown capable of removing herbicides and their degradates from drinking water. Samples were collected biweekly from mid-March through the end of August, and twice during the off-season. The analytical method had a detection limit of 0.05 microg L(-1) for alachlor [2-chloro-N-(2,6-diethylphenyl)-N-(methoxymethyl)-acetamide] and 0.03 microg L(-1) for acetochlor [2-chloro-N-(ethoxymethyl)-N-(2-ethyl-6-methylphenyl)-acetamide], atrazine [6-chloro-N-ethyl-N'-(1-methylethyl)-1,3,5-triazine-2,4-diamine], and metolachlor [2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl)-acetamide]. Of the 16528 drinking water samples analyzed, acetochlor, alachlor, atrazine, and metolachlor were detected in 19, 7, 87, and 53% of the samples, respectively. During 1999-2001, samples were also analyzed for the presence of six major degradates of the chloroacetanilide herbicides, which were detected more frequently than their parent compounds, despite having higher detection limits of 0.1 to 0.2 microg L(-1). Overall detection frequencies were correlated with product use and environmental fate characteristics. Reservoirs were particularly vulnerable to atrazine, which exceeded its 3 microg L(-1) maximum contaminant level at 25 such sites during 1995-1999. Acetochlor annualized mean concentrations (AMCs) did not exceed its mitigation trigger (2 microg L(-1)) at any site, and comparisons of observed levels with standard measures of human and ecological hazards indicate that it poses no significant risk to human health or the environment.     

When and how to use Q methodology to understand perspectives in conservation research

Understanding human perspectives is critical in a range of conservation contexts, for example, in overcoming conflicts or developing projects that are acceptable to relevant stakeholders. The Q methodology is a unique semiquantitative technique used to explore human perspectives. It has been applied for decades in other disciplines and recently gained traction in conservation. This paper helps researchers assess when Q is useful for a given conservation question and what its use involves. To do so, we explained the steps necessary to conduct a Q study, from the research design to the interpretation of results. We provided recommendations to minimize biases in conducting a Q study, which can affect mostly when designing the study and collecting the data. We conducted a structured literature review of 52 studies to examine in what empirical conservation contexts Q has been used. Most studies were subnational or national cases, but some also address multinational or global questions. We found that Q has been applied to 4 broad types of conservation goals: addressing conflict, devising management alternatives, understanding policy acceptability, and critically reflecting on the values that implicitly influence research and practice. Through these applications, researchers found hidden views, understood opinions in depth and discovered points of consensus that facilitated unlocking difficult disagreements. The Q methodology has a clear procedure but is also flexible, allowing researchers explore long‐term views, or views about items other than statements, such as landscape images. We also found some inconsistencies in applying and, mainly, in reporting Q studies, whereby it was not possible to fully understand how the research was conducted or why some atypical research decisions had been taken in some studies. Accordingly, we suggest a reporting checklist.     

Protection from metal toxicity by Hsp40-like protein isolated from contaminated soil using functional metagenomic approach

Environmental Science and Pollution Research - Pollution in the environment due to accumulation of potentially toxic metals results in deterioration of soil and water quality, thus impacting health...     

Biocatalyst physiology and interplay: a protagonist of MFC operation

Environmental Science and Pollution Research - Microbial fuel cells (MFC) have been foreseen as a sustainable renewable energy resource to meet future energy demand. In the past, several studies...     

Leachate injection using vertical wells in bioreactor landfills

Leachate recirculation or liquid injection in municipal solid waste landfills offers economic and environmental benefits. The key objective of this study was to carry out numerical evaluation of key design variables for leachate recirculation system consisting of vertical wells. In order to achieve the objective, numerical modeling was carried out using the finite-element model HYDRUS-2D. The following design parameters were evaluated by simulating liquid pressure head on the liner and the wetted width of the waste under steady-state flow conditions: (1) hydraulic conductivities of the waste and vertical well backfill; (2) liquid injection rate and dosing frequency; (3) well diameter, screen height and screen depth; and (4) hydraulic conductivity of the leachate collection system, slope of the leachate collection system and spacing of the leachate collection pipes. The key findings of this study are as follows. The well diameter, hydraulic conductivity of the well drainage pack, and screen height and screen depth of the well have very little effect on the wetted width for a given liquid flux. The wetted width and the injection pressure for a given liquid flux decrease with the increase in the hydraulic conductivity of the waste. The pressure head on the liner increases with the decrease in the vertical distance between the bottom of the well screen and the top of leachate collection system. The liquid injection flux increases with the decrease in hydraulic conductivity of the leachate collection system. Unlike sand (k approximately 10(-4)m/s), pea gravel (k approximately 0.01 m/s) resulted in less than 0.3m pressure head on the liner for all simulations carried out in this study.