861 resultados para Environmental values in a globalising world


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By 1900 the Jewish community of Tunisia witnessed the emergence of new competing identities: “assimilationist” of the Alliance Israelite Universelle, termed “Alliancist,” and Zionist. Strikingly, two members of the same family in Tunis, Raymond Valensi, President of the AIU Regional Committee, and Alfred Valensi, President of the Zionist Federation, led the struggle for their separate causes. In his discussion of identity in the modern world, Homi Bhabha asks, "How do strategies of representation or empowerment come to be formulated in the competing claims of communities…where, despite shared histories of …discrimination, the exchange of values, meanings and priorities…may be profoundly antagonistic…?" It is in this context that the claims of the Alliance and Zionism will be examined prior to World War I, based on the Archives of the AIU and on such secondary sources as the indispensable work of Paul Sebag. The tensions between the Alliancists and Zionists continued until the outbreak of World War II, as the French-speaking Jews of Tunisia sought to define their individual and collective identities.

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Subpolar regions are key areas to study natural climate variability, due to their high sensitivity to rapid environmental changes, particularly through sea surface temperature (SST) variations. Here, we have tested three independent organic temperature proxies (UK'37, TEX86 and LDI) on their potential applicability for SST reconstruction in the subpolar region around Iceland. UK'37, TEX86 and TEXL86 temperature estimates from suspended particulate matter showed a substantial discrepancy with instrumental data, while long chain alkyl diols were below detection limit in most of the stations. In the northern Iceland Basin, sedimenting particles revealed a seasonality in lipid fluxes i.e. high fluxes of alkenones and GDGTs were measured during late spring-summer, and high fluxes of long chain alkyl diols during late summer. The flux-weighted average temperature estimates had a significant negative (ca. 2.3°C for UK'37) and positive (up to 5°C for TEX86) offset with satellite-derived SSTs and temperature estimates derived from the underlying surface sediment. UK'37 temperature estimates from surface sediments around Iceland correlate well with summer mean sea surface temperatures, while TEX86 derived temperatures correspond with both annual and winter mean 0-200 m temperatures, suggesting a subsurface temperature signal. Anomalous LDI-SST values in surface sediments, and low mass flux of 1,13- and 1,15-diols compared to 1,14-diols, suggest that Proboscia diatoms are the major sources of long chain alkyl diols in this area rather than eustigmatophyte algae, and therefore the LDI cannot be applied in this region.

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Coral reefs persist in an accretion-erosion balance and ocean acidification resulting from anthropogenic CO2 emissions threatens to shift this balance in favor of net reef erosion. Corals and calcifying algae, largely responsible for reef accretion, are vulnerable to environmental changes associated with ocean acidification, but the direct effects of lower pH on reef erosion has received less attention, particularly in the context of known drivers of bioerosion and natural variability. This study examines the balance between reef accretion and erosion along a well-characterized natural environmental gradient in Kane'ohe Bay, Hawai'i using experimental blocks of coral skeleton. Comparing before and after micro-computed tomography (µCT) scans to quantify net accretion and erosion, we show that, at the small spatial scale of this study (tens of meters), pH was a better predictor of the accretion-erosion balance than environmental drivers suggested by prior studies, including resource availability, temperature, distance from shore, or depth. In addition, this study highlights the fine-scale variation of pH in coastal systems and the importance of microhabitat variation for reef accretion and erosion processes. We demonstrate significant changes in both the mean and variance of pH on the order of meters, providing a local perspective on global increases in pCO2. Our findings suggest that increases in reef erosion, combined with expected decreases in calcification, will accelerate the shift of coral reefs to an erosion-dominated system in a high-CO2 world. This shift will make reefs increasingly susceptible to storm damage and sea-level rise, threatening the maintenance of the ecosystem services that coral reefs provide.

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This data set contains measurements of inorganic phosphorus in samples of soil solution collected in 2006 from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below) that have been aggregated to seasonal values. In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 µm (UMS GmbH, Munich, Germany) were installed in April 2002 in depths of 10, 20, 30 and 60 cm to collect soil solution. Manual soil matric potential measurements were used to regulate the vacuum system. Manual soil matric potential measurements were used to regulate the vacuum system. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved inorganic P (PO4P). Here volume-weighted mean values are provided as aggregated seasonal values (spring = March to May, summer = June to August, fall = September to November, winter = December to February) for 2006 in spring. To calculate these values, the sampled volume of soil solution is used as weight for P concentrations of the respective sampling date. Inorganic phosphorus concentrations in the soil solution were measured photometrically with a continuous flow analyzer (CFA Autoanalyzer [Bran&Luebbe, Norderstedt, Germany]). Ammonium molybdate catalyzed by antimony tartrate reacts in an acidic medium with phosphate and forms a phospho-molybdic acid complex. Ascorbic acid reduces this complex to an intensely blue-colored complex. As the molybdic complex forms under strongly acidic conditions, we could not exclude the hydrolysis of labile organic P compounds in our samples. Furthermore, the molybdate reaction is not sensitive for condensed phosphates. The detection limits of both TDP and PO4P were 0.04 mg P l-1 (Autoanalyzer, Bran&Luebbe).

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This data set contains measurements of inorganic phosphorus in samples of soil solution collected in 2004 from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below) that have been aggregated to seasonal values. In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 µm (UMS GmbH, Munich, Germany) were installed in April 2002 in depths of 10, 20, 30 and 60 cm to collect soil solution. Manual soil matric potential measurements were used to regulate the vacuum system. Manual soil matric potential measurements were used to regulate the vacuum system. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved inorganic P (PO4P). Here volume-weighted mean values are provided as aggregated seasonal values (spring = March to May, summer = June to August, fall = September to November, winter = December to February) for 2004 in spring, fall, and winter. To calculate these values, the sampled volume of soil solution is used as weight for P concentrations of the respective sampling date. Inorganic phosphorus concentrations in the soil solution were measured photometrically with a continuous flow analyzer (for samples collected until spring 2004: CFA SAN++, Skalar [Breda, The Netherlands]; for samples collected later: CFA Autoanalyzer [Bran&Luebbe, Norderstedt, Germany]). Ammonium molybdate catalyzed by antimony tartrate reacts in an acidic medium with phosphate and forms a phospho-molybdic acid complex. Ascorbic acid reduces this complex to an intensely blue-colored complex. As the molybdic complex forms under strongly acidic conditions, we could not exclude the hydrolysis of labile organic P compounds in our samples. Furthermore, the molybdate reaction is not sensitive for condensed phosphates. The detection limits of both TDP and PO4P were 0.02 mg P l-1 (CFA, Skalar) and 0.04 mg P l-1 (Autoanalyzer, Bran&Luebbe).

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This data set contains measurements of inorganic phosphorus in samples of soil solution collected in 2003 from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below) that have been aggregated to seasonal values. In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 µm (UMS GmbH, Munich, Germany) were installed in April 2002 in depths of 10, 20, 30 and 60 cm to collect soil solution. Manual soil matric potential measurements were used to regulate the vacuum system. Manual soil matric potential measurements were used to regulate the vacuum system. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved inorganic P (PO4P). Here volume-weighted mean values are provided as aggregated seasonal values (spring = March to May, summer = June to August, fall = September to November, winter = December to February) for 2003 in spring, fall, and winter. To calculate these values, the sampled volume of soil solution is used as weight for P concentrations of the respective sampling date. Inorganic phosphorus concentrations in the soil solution were measured photometrically with a continuous flow analyzer (CFA SAN++, Skalar [Breda, The Netherlands]). Ammonium molybdate catalyzed by antimony tartrate reacts in an acidic medium with phosphate and forms a phospho-molybdic acid complex. Ascorbic acid reduces this complex to an intensely blue-colored complex. As the molybdic complex forms under strongly acidic conditions, we could not exclude the hydrolysis of labile organic P compounds in our samples. Furthermore, the molybdate reaction is not sensitive for condensed phosphates. The detection limits of both TDP and PO4P were 0.02 mg P l-1 (CFA, Skalar).

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This data set contains measurements of inorganic phosphorus in samples of soil solution collected in 2005 from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below) that have been aggregated to seasonal values. In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 µm (UMS GmbH, Munich, Germany) were installed in April 2002 in depths of 10, 20, 30 and 60 cm to collect soil solution. Manual soil matric potential measurements were used to regulate the vacuum system. Manual soil matric potential measurements were used to regulate the vacuum system. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved inorganic P (PO4P). Here volume-weighted mean values are provided as aggregated seasonal values (spring = March to May, summer = June to August, fall = September to November, winter = December to February) for 2005 in spring, and winter. To calculate these values, the sampled volume of soil solution is used as weight for P concentrations of the respective sampling date. Inorganic phosphorus concentrations in the soil solution were measured photometrically with a continuous flow analyzer (CFA Autoanalyzer [Bran&Luebbe, Norderstedt, Germany]). Ammonium molybdate catalyzed by antimony tartrate reacts in an acidic medium with phosphate and forms a phospho-molybdic acid complex. Ascorbic acid reduces this complex to an intensely blue-colored complex. As the molybdic complex forms under strongly acidic conditions, we could not exclude the hydrolysis of labile organic P compounds in our samples. Furthermore, the molybdate reaction is not sensitive for condensed phosphates. The detection limits of both TDP and PO4P were 0.04 mg P l-1 (Autoanalyzer, Bran&Luebbe).

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Physiological responses (ingestion rate, absorption rate and efficiency, respiration, rate, excretion rate) and scope for growth of a subtidal scavenging gastropod Nassarius conoidalis under the combined effects of ocean acidification (pCO2 levels: 380, 950, 1250 µatm) and temperature (15, 30 °C) were investigated for 31 days. There was a significant reduction in all the physiological rates and scope for growth following short-term exposure (1-3 days) to elevated pCO2 except absorption efficiency at 15 °C and 30 °C, and respiration rate and excretion rate at 15 °C. The percentage change in the physiological rates ranged from 0% to 90% at 15 °C and from 0% to 73% at 30 °C when pCO2 was increased from 380 µatm to 1250 µatm. The effect of pCO2 on the physiological rates was enhanced at high temperature for ingestion, absorption, respiration and excretion. When the exposure period was extended to 31 days, the effect of pCO2 was significant on the ingestion rate only. All the physiological rates remained unchanged when temperature increased from 24 °C to 30 °C but the rates at 15 °C were significantly lower, irrespective of the duration of exposure. Our data suggested that a medium-term exposure to ocean acidification has no effect on the energetics of N. conoidalis. Nevertheless, the situation may be complicated by a longer term of exposure and/or a reduction in salinity in a warming world.

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All activities of an organization involve risks that should be managed. The risk management process aids decision making by taking account of uncertainty and the possibility of future events or circumstances (intended or unintended) and their effects on agreed objectives. With that idea, new ISO Standard has been drawn up. ISO 31010 has been recently issued which provides a structured process that identifies how objectives may be affected, and analyses the risk in term of consequences and their probabilities before deciding on whether further treatment is required. In this lecture, that ISO Standard has been adapted to Open Pit Blasting Operations, focusing in Environmental effects which can be managed properly. Technique used is Fault Tree Analysis (FTA), which is applied in all possible scenarios, providing to Blasting Professionals the tools to identify, analyze and manage environmental effects in blasting operations. Also this lecture can help to minimize each effect, studying each case. This paper also can be useful to Project Managers and Occupational Health and Safety Departments (OH&S) because blasting operations can be evaluated and compared one to each other to determine the risks that should be managed in different case studies. The environmental effects studied are: ground vibrations, flyrock and air overpressure (airblast). Sometimes, blasting operations are carried out near populated areas where environmental effects may impose several limitations on the use of explosives. In those cases, where these factors approach certain limits, National Standards and Regulations have to be applied.

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La gestión de los recursos hídricos se convierte en un reto del presente y del futuro frente a un panorama de continuo incremento de la demanda de agua debido al crecimiento de la población, el crecimiento del desarrollo económico y los posibles efectos del calentamiento global. La política hidráulica desde los años 60 en España se ha centrado en la construcción de infraestructuras que han producido graves alteraciones en el régimen natural de los ríos. Estas alteraciones han provocado y acrecentado los impactos sobre los ecosistemas fluviales y ribereños. Desde los años 90, sin embargo, ha aumentado el interés de la sociedad para conservar estos ecosistemas. El concepto de caudales ambientales consiste en un régimen de caudales que simula las características principales del régimen natural. Los caudales ambientales están diseñados para conservar la estructura y funcionalidad de los ecosistemas asociados al régimen fluvial, bajo la hipótesis de que los elementos que conforman estos ecosistemas están profundamente adaptados al régimen natural de caudales, y que cualquier alteración del régimen natural puede provocar graves daños a todo el sistema. El método ELOHA (Ecological Limits of Hydrological Alteration) tiene como finalidad identificar las componentes del régimen natural de caudales que son clave para mantener el equilibrio de los ecosistemas asociados, y estimar los límites máximos de alteración de estas componentes para garantizar su buen estado. Esta tesis presenta la aplicación del método ELOHA en la cuenca del Ebro. La cuenca del Ebro está profundamente regulada e intervenida por el hombre, y sólo las cabeceras de los principales afluentes del Ebro gozan todavía de un régimen total o cuasi natural. La tesis se estructura en seis capítulos que desarrollan las diferentes partes del método. El primer capítulo explica cómo se originó el concepto “caudales ambientales” y en qué consiste el método ELOHA. El segundo capítulo describe el área de estudio. El tercer capítulo realiza una clasificación de los regímenes naturales de la cuenca (RNC) del Ebro, basada en series de datos de caudal mínimamente alterado y usando exclusivamente parámetros hidrológicos. Se identificaron seis tipos diferentes de régimen natural: pluvial mediterráneo, nivo-pluvial, pluvial mediterréaneo con una fuerte componente del caudal base, pluvial oceánico, pluvio-nival oceánico y Mediterráneo. En el cuarto capítulo se realiza una regionalización a toda la cuenca del Ebro de los seis RNC encontrados en la cueca. Mediante parámetros climáticos y fisiográficos se extrapola la información del tipo de RNC a puntos donde no existen datos de caudal inalterado. El patrón geográfico de los tipos de régimen fluvial obtenido con la regionalización resultó ser coincidente con el patrón obtenido a través de la clasificación hidrológica. El quinto capítulo presenta la validación biológica de los procesos de clasificación anteriores: clasificación hidrológica y regionalización. La validación biológica de los tipos de regímenes fluviales es imprescindible, puesto que los diferentes tipos de régimen fluvial van a servir de unidades de gestión para favorecer el mantenimiento de los ecosistemas fluviales. Se encontraron diferencias significativas entre comunidades biológicas en cinco de los seis tipos de RNC encontrados en la cuenca. Finalmente, en el sexto capítulo se estudian las relaciones hidro-ecológicas existentes en tres de los seis tipos de régimen fluvial encontrados en la cuenca del Ebro. Mediante la construcción de curvas hidro-ecológicas a lo largo de un gradiente de alteración hidrológica, se pueden sugerir los límites de alteración hidrológica (ELOHAs) para garantizar el buen estado ecológico en cada uno de los tipos fluviales estudiados. Se establecieron ELOHAs en tres de los seis tipos de RNC de la cuenca del Ebro Esta tesis, además, pone en evidencia la falta de datos biológicos asociados a registros de caudal. Para llevar a cabo la implantación de un régimen de caudales ambientales en la cuenca, la ubicación de los puntos de muestreo biológico cercanos a estaciones de aforo es imprescindible para poder extraer relaciones causa-efecto de la gestión hidrológica sobre los ecosistemas dependientes. ABSTRACT In view of a growing freshwater demand because of population raising, improvement of economies and the potential effects of climate change, water resources management has become a challenge for present and future societies. Water policies in Spain have been focused from the 60’s on constructing hydraulic infrastructures, in order to dampen flow variability and granting water availability along the year. Consequently, natural flow regimes have been deeply altered and so the depending habitats and its ecosystems. However, an increasing acknowledgment of societies for preserving healthy freshwater ecosystems started in the 90’s and agreed that to maintain healthy freshwater ecosystems, it was necessary to set environmental flow regimes based on the natural flow variability. The Natural Flow Regime paradigm (Richter et al. 1996, Poff et al. 1997) bases on the hypothesis that freshwater ecosystems are made up by elements adapted to natural flow conditions, and any change on these conditions can provoke deep impacts on the whole system. Environmental flow regime concept consists in designing a flow regime that emulates natural flow characteristics, so that ecosystem structure, functions and services are maintained. ELOHA framework (Ecological Limits of Hydrological Alteration) aims to identify key features of the natural flow regime (NFR) that are needed to maintain and preserve healthy freshwater and riparian ecosystems. Moreover, ELOHA framework aims to quantify thresholds of alteration of these flow features according to ecological impacts. This thesis describes the application of the ELOHA framework in the Ebro River Basin. The Ebro River basin is the second largest basin in Spain and it is highly regulated for human demands. Only the Ebro headwaters tributaries still have completely unimpaired flow regime. The thesis has six chapters and the process is described step by step. The first chapter makes an introduction to the origin of the environmental flow concept and the necessity to come up. The second chapter shows a description of the study area. The third chapter develops a classification of NFRs in the basin based on natural flow data and using exclusively hydrological parameters. Six NFRs were found in the basin: continental Mediterranean-pluvial, nivo-pluvial, continental Mediterranean pluvial (with groundwater-dominated flow pattern), pluvio-oceanic, pluvio-nival-oceanic and Mediterranean. The fourth chapter develops a regionalization of the six NFR types across the basin by using climatic and physiographic variables. The geographical pattern obtained from the regionalization process was consistent with the pattern obtained with the hydrologic classification. The fifth chapter performs a biological validation of both classifications, obtained from the hydrologic classification and the posterior extrapolation. When the aim of flow classification is managing water resources according to ecosystem requirements, a validation based on biological data is compulsory. We found significant differences in reference macroinvertebrate communities between five over the six NFR types identified in the Ebro River basin. Finally, in the sixth chapter we explored the existence of significant and explicative flow alteration-ecological response relationships (FA-E curves) within NFR types in the Ebro River basin. The aim of these curves is to find out thresholds of hydrological alteration (ELOHAs), in order to preserve healthy freshwater ecosystem. We set ELOHA values in three NFR types identified in the Ebro River basin. During the development of this thesis, an inadequate biological monitoring in the Ebro River basin was identified. The design and establishment of appropriate monitoring arrangements is a critical final step in the assessment and implementation of environmental flows. Cause-effect relationships between hydrology and macroinvertebrate community condition are the principal data that sustain FA-E curves. Therefore, both data sites must be closely located, so that the effects of external factors are minimized. The scarce hydro-biological pairs of data available in the basin prevented us to apply the ELOHA method at all NFR types.

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In the EU context extraction of shale and oil gas by hydraulic fracturing (fracking) differs from country to country in terms of legislation and implementation. While fossil fuel extraction using this technology is currently taking place in the UK, Germany and France have adopted respective moratoria. In between is the Spanish case, where hydrocarbon extraction projects through fracking have to undergo mandatory and routine environmental assessment in accordance with the last changes to environmental regulations. Nowadays Spain is at the crossroad with respect to the future of this technology. We presume a social conflictt in our country since the position and strategy of the involved and confronted social actors -national, regional and local authorities, energy companies, scientists, NGO and other social organization- are going to play key and likely divergent roles in its industrial implementation and public acceptance. In order to improve knowledge on how to address these controverted situations from the own engineering context, the affiliated units from the Higher Technical School of Mines and Energy Engineering at UPM have been working on a transversal program to teach values and ethics. Over the past seven years, this pioneering experience has shown the usefulness of applying a consequentialist ethics, based on a case-by-case approach and costs-benefits analysis both for action and inaction. As a result of this initiative a theoretical concept has arisen and crystallized in this field: it is named Inter-ethics. This theoretical perspective can be very helpful in complex situations, with multi-stakeholders and plurality of interests, when ethical management requires the interaction between the respective ethics of each group; professional ethics of a single group is not enough. Under this inter-ethics theoretical framework and applying content analysis techniques, this paper explores the articulation of the discourse in favour and against fracking technology and its underlying values as manifested in the Spanish traditional mass media and emerging social media such as Youtube. Results show that Spanish public discourse on fracking technology includes the costs-benefits analysis to communicate how natural resources from local communities may be affected by these facilities due to environmental, health and economic consequences. Furthermore, this technology is represented as a solution to the "demand of energy" according to the optimistic discourse while, from a pessimistic view, fracking is often framed as a source "environmental problems" and even natural disasters as possible earthquakes. In this latter case, this negative representation could have been influenced by the closure of a macro project to store injected natural gas in the Mediterranean Sea using the old facilities of an oil exploitation in Amposta (Proyecto Cástor). The closure of this project was due to the occurrence of earthquakes whose intensity was higher than the originally expected by the experts in the assessment stage of the project.

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Riassunto La spettrometria di massa (MS) nata negli anni ’70 trova oggi, grazie alla tecnologia Matrix-Assisted Laser Desorption Ionization-Time of Flight (MALDI-TOF), importanti applicazioni in diversi settori: biotecnologico (per la caratterizzazione ed il controllo di qualità di proteine ricombinanti ed altre macromolecole), medico–clinico (per la diagnosi di laboratorio di malattie e per lo sviluppo di nuovi trattamenti terapeutici mirati), alimentare ed ambientale. Negli ultimi anni, questa tecnologia è diventata un potente strumento anche per la diagnosi di laboratorio in microbiologia clinica, rivoluzionando il flusso di lavoro per una rapida identificazione di batteri e funghi, sostituendo l’identificazione fenotipica convenzionale basata su saggi biochimici. Attualmente mediante MALDI-TOF MS sono possibili due diversi approcci per la caratterizzazione dei microrganismi: (1) confronto degli spettri (“mass spectra”) con banche dati contenenti profili di riferimento (“database fingerprints”) e (2) “matching” di bio-marcatori con banche dati proteomiche (“proteome database”). Recentemente, la tecnologia MALDI-TOF, oltre alla sua applicazione classica nell’identificazione di microrganismi, è stata utilizzata per individuare, indirettamente, meccanismi di resistenza agli antibiotici. Primo scopo di questo studio è stato verificare e dimostrare l’efficacia identificativa della metodica MALDI-TOF MS mediante approccio di comparazione degli spettri di differenti microrganismi di interesse medico per i quali l’identificazione risultava impossibile a causa della completa assenza o presenza limitata, di spettri di riferimento all’interno della banca dati commerciale associata allo strumento. In particolare, tale scopo è stato raggiunto per i batteri appartenenti a spirochete del genere Borrelia e Leptospira, a miceti filamentosi (dermatofiti) e protozoi (Trichomonas vaginalis). Secondo scopo di questo studio è stato valutare il secondo approccio identificativo basato sulla ricerca di specifici marcatori per differenziare parassiti intestinali di interesse medico per i quali non è disponibile una banca dati commerciale di riferimento e la sua creazione risulterebbe particolarmente difficile e complessa, a causa della complessità del materiale biologico di partenza analizzato e del terreno di coltura nei quali questi protozoi sono isolati. Terzo ed ultimo scopo di questo studio è stata la valutazione dell’applicabilità della spettrometria di massa con tecnologia MALDI-TOF per lo studio delle resistenze batteriche ai carbapenemi. In particolare, è stato messo a punto un saggio di idrolisi dei carbapenemi rilevata mediante MALDI-TOF MS in grado di determinare indirettamente la produzione di carbapenemasi in Enterobacteriaceae. L’efficacia identificativa della metodica MALDI-TOF mediante l’approccio di comparazione degli spettri è stata dimostrata in primo luogo per batteri appartenenti al genere Borrelia. La banca dati commerciale dello strumento MALDI-TOF MS in uso presso il nostro laboratorio includeva solo 3 spettri di riferimento appartenenti alle specie B. burgdorferi ss, B. spielmani e B. garinii. L’implementazione del “database” con specie diverse da quelle già presenti ha permesso di colmare le lacune identificative dovute alla mancanza di spettri di riferimento di alcune tra le specie di Borrelia più diffuse in Europa (B. afzelii) e nel mondo (come ad esempio B. hermsii, e B. japonica). Inoltre l’implementazione con spettri derivanti da ceppi di riferimento di specie già presenti nel “database” ha ulteriormente migliorato l’efficacia identificativa del sistema. Come atteso, il ceppo di isolamento clinico di B. lusitaniae (specie non presente nel “database”) è stato identificato solo a livello di genere corroborando, grazie all’assenza di mis-identificazione, la robustezza della “nuova” banca dati. I risultati ottenuti analizzando i profili proteici di ceppi di Borrelia spp. di isolamento clinico, dopo integrazione del “database” commerciale, indicano che la tecnologia MALDI-TOF potrebbe essere utilizzata come rapida, economica ed affidabile alternativa ai metodi attualmente utilizzati per identificare ceppi appartenenti a questo genere. Analogamente, per il genere Leptospira dopo la creazione ex-novo della banca dati “home-made”, costruita con i 20 spettri derivati dai 20 ceppi di riferimento utilizzati, è stata ottenuta una corretta identificazione a livello di specie degli stessi ceppi ri-analizzati in un esperimento indipendente condotto in doppio cieco. Il dendrogramma costruito con i 20 MSP-Spectra implementati nella banca dati è formato da due rami principali: il primo formato dalla specie non patogena L. biflexa e dalla specie a patogenicità intermedia L. fainei ed il secondo che raggruppa insieme le specie patogene L. interrogans, L. kirschneri, L. noguchii e L. borgpetersenii. Il secondo gruppo è ulteriormente suddiviso in due rami, contenenti rispettivamente L. borgpetersenii in uno e L. interrogans, L. kirschneri e L. noguchii nell’altro. Quest’ultimo, a sua volta, è suddiviso in due rami ulteriori: il primo comprendente la sola specie L. noguchii, il secondo le specie L. interrogans e L. kirshneri non separabili tra loro. Inoltre, il dendrogramma costruito con gli MSP-Spectra dei ceppi appartenenti ai generi Borrelia e Leptospira acquisiti in questo studio, e appartenenti al genere Brachyspira (implementati in un lavoro precedentemente condotto) mostra tre gruppi principali separati tra loro, uno per ogni genere, escludendo possibili mis-identificazioni tra i 3 differenti generi di spirochete. Un’analisi più approfondita dei profili proteici ottenuti dall’analisi ha mostrato piccole differenze per ceppi della stessa specie probabilmente dovute ai diversi pattern proteici dei distinti sierotipi, come confermato dalla successiva analisi statistica, che ha evidenziato picchi sierotipo-specifici. È stato, infatti, possibile mediante la creazione di un modello statistico dedicato ottenere un “pattern” di picchi discriminanti in grado di differenziare a livello di sierotipo sia i ceppi di L. interrogans sia i ceppi di L. borgpetersenii saggiati, rispettivamente. Tuttavia, non possiamo concludere che i picchi discriminanti da noi riportati siano universalmente in grado di identificare il sierotipo dei ceppi di L. interrogans ed L. borgpetersenii; i picchi trovati, infatti, sono il risultato di un’analisi condotta su uno specifico pannello di sierotipi. È stato quindi dimostrato che attuando piccoli cambiamenti nei parametri standardizzati come l’utilizzo di un modello statistico e di un programma dedicato applicato nella routine diagnostica è possibile utilizzare la spettrometria di massa MALDI-TOF per una rapida ed economica identificazione anche a livello di sierotipo. Questo può significativamente migliorare gli approcci correntemente utilizzati per monitorare l’insorgenza di focolai epidemici e per la sorveglianza degli agenti patogeni. Analogamente a quanto dimostrato per Borrelia e Leptospira, l’implementazione della banca dati dello spettrometro di massa con spettri di riferimento di miceti filamentosi (dermatofiti) si è rilevata di particolare importanza non solo per l’identificazione di tutte le specie circolanti nella nostra area ma anche per l’identificazione di specie la cui frequenza nel nostro Paese è in aumento a causa dei flussi migratori dalla zone endemiche (M. audouinii, T. violaceum e T. sudanense). Inoltre, l’aggiornamento del “database” ha consentito di superare la mis-identificazione dei ceppi appartenenti al complesso T. mentagrophytes (T. interdigitale e T. mentagrophytes) con T. tonsurans, riscontrata prima dell’implementazione della banca dati commerciale. Il dendrogramma ottenuto dai 24 spettri implementati appartenenti a 13 specie di dermatofiti ha rivelato raggruppamenti che riflettono quelli costruiti su base filogenetica. Sulla base dei risultati ottenuti mediante sequenziamento della porzione della regione ITS del genoma fungino non è stato possibile distinguere T. interdigitale e T. mentagrophytes, conseguentemente anche gli spettri di queste due specie presentavano picchi dello stesso peso molecoalre. Da sottolineare che il dendrogramma costruito con i 12 profili proteici già inclusi nel database commerciale e con i 24 inseriti nel nuovo database non riproduce l’albero filogenetico per alcune specie del genere Tricophyton: gli spettri MSP già presenti nel database e quelli aggiunti delle specie T. interdigitale e T. mentagrophytes raggruppano separatamente. Questo potrebbe spiegare le mis-identificazioni di T. interdigitale e T. mentagrophytes con T. tonsurans ottenute prima dell’implementazione del database. L’efficacia del sistema identificativo MALDI-TOF è stata anche dimostrata per microrganismi diversi da batteri e funghi per i quali la metodica originale è stata sviluppata. Sebbene tale sistema identificativo sia stato applicato con successo a Trichomonas vaginalis è stato necessario apportare modifiche nei parametri standard previsti per l’identificazione di batteri e funghi. Le interferenze riscontrate tra i profili proteici ottenuti per i due terreni utilizzati per la coltura di questo protozoo e per i ceppi di T. vaginalis hanno, infatti, reso necessario l’utilizzo di nuovi parametri per la creazione degli spettri di riferimento (MSP-Spectra). L’importanza dello sviluppo del nuovo metodo risiede nel fatto che è possibile identificare sulla base del profilo proteico (e non sulla base di singoli marcatori) microorganismi cresciuti su terreni complessi che potrebbero presentare picchi nell'intervallo di peso molecolare utilizzato a scopo identificativo: metaboliti, pigmenti e nutrienti presenti nel terreno possono interferire con il processo di cristallizzazione e portare ad un basso punteggio identificativo. Per T. vaginalis, in particolare, la “sottrazione” di picchi dovuti a molecole riconducibili al terreno di crescita utilizzato, è stata ottenuta escludendo dall'identificazione l'intervallo di peso molecolare compreso tra 3-6 kDa, permettendo la corretta identificazione di ceppi di isolamento clinico sulla base del profilo proteico. Tuttavia, l’elevata concentrazione di parassita richiesta (105 trofozoiti/ml) per una corretta identificazione, difficilmente ottenibile in vivo, ha impedito l’identificazione di ceppi di T. vaginalis direttamente in campioni clinici. L’approccio identificativo mediante individuazione di specifici marcatori proteici (secondo approccio identificativo) è stato provato ed adottato in questo studio per l’identificazione e la differenziazione di ceppi di Entamoeba histolytica (ameba patogena) ed Entamoeba dispar (ameba non patogena), specie morfologiacamente identiche e distinguibili solo mediante saggi molecolari (PCR) aventi come bersaglio il DNA-18S, che codifica per l’RNA della subunità ribosomiale minore. Lo sviluppo di tale applicazione ha consentito di superare l’impossibilità della creazione di una banca dati dedicata, a causa della complessità del materiale fecale di partenza e del terreno di coltura impiagato per l’isolamento, e di identificare 5 picchi proteici in grado di differenziare E. histolytica da E. dispar. In particolare, l’analisi statistica ha mostrato 2 picchi specifici per E. histolytica e 3 picchi specifici per E. dispar. L’assenza dei 5 picchi discriminanti trovati per E. histolytica e E. dispar nei profili dei 3 differenti terreni di coltura utilizzati in questo studio (terreno axenico LYI-S-2 e terreno di Robinson con e senza E. coli) permettono di considerare questi picchi buoni marcatori in grado di differenziare le due specie. La corrispondenza dei picchi con il PM di due specifiche proteine di E. histolytica depositate in letteratura (Amoebapore A e un “unknown putative protein” di E. histolytica ceppo di riferimento HM-1:IMSS-A) conferma la specificità dei picchi di E. histolytica identificati mediante analisi MALDI-TOF MS. Lo stesso riscontro non è stato possibile per i picchi di E. dispar in quanto nessuna proteina del PM di interesse è presente in GenBank. Tuttavia, va ricordato che non tutte le proteine E. dispar sono state ad oggi caratterizzate e depositate in letteratura. I 5 marcatori hanno permesso di differenziare 12 dei 13 ceppi isolati da campioni di feci e cresciuti in terreno di Robinson confermando i risultati ottenuti mediante saggio di Real-Time PCR. Per un solo ceppo di isolamento clinico di E. histolytica l’identificazione, confermata mediante sequenziamento della porzione 18S-rDNA, non è stata ottenuta mediante sistema MALDI-TOF MS in quanto non sono stati trovati né i picchi corrispondenti a E. histolytica né i picchi corrispondenti a E. dispar. Per questo ceppo è possibile ipotizzare la presenza di mutazioni geno/fenotipiche a livello delle proteine individuate come marcatori specifici per E. histolytica. Per confermare questa ipotesi sarebbe necessario analizzare un numero maggiore di ceppi di isolamento clinico con analogo profilo proteico. L’analisi condotta a diversi tempi di incubazione del campione di feci positivo per E. histolytica ed E. dipar ha mostrato il ritrovamento dei 5 picchi discriminanti solo dopo 12 ore dall’inoculo del campione nel terreno iniziale di Robinson. Questo risultato suggerisce la possibile applicazione del sistema MALDI-TOF MS per identificare ceppi di isolamento clinico di E. histolytica ed E. dipar nonostante la presenza di materiale fecale che materialmente può disturbare e rendere difficile l’interpretazione dello spettro ottenuto mediante analisi MALDI-TOF MS. Infine in questo studio è stata valutata l’applicabilità della tecnologia MALDI-TOF MS come saggio fenotipico rapido per la determinazione di ceppi produttori di carbapenemasi, verificando l'avvenuta idrolisi del meropenem (carbapeneme di riferimento utilizzato in questo studio) a contatto con i ceppi di riferimento e ceppi di isolamento clinico potenzialmente produttori di carbapenemasi dopo la messa a punto di un protocollo analitico dedicato. Il saggio di idrolisi del meropenem mediante MALDI-TOF MS ha dimostrato la presenza o l’assenza indiretta di carbapenemasi nei 3 ceppi di riferimento e nei 1219 (1185 Enterobacteriaceae e 34 non-Enterobacteriaceae) ceppi di isolamento clinico inclusi nello studio. Nessuna interferenza è stata riscontrata per i ceppi di Enterobacteriaceae variamente resistenti ai tre carbapenemi ma risultati non produttori di carbapenemasi mediante i saggi fenotipici comunemente impiegati nella diagnostica routinaria di laboratorio: nessuna idrolisi del farmaco è stata infatti osservata al saggio di idrolisi mediante MALDI-TOF MS. In un solo caso (ceppo di K. pneumoniae N°1135) è stato ottenuto un profilo anomalo in quanto presenti sia i picchi del farmaco intatto che quelli del farmaco idrolizzato. Per questo ceppo resistente ai tre carbapenemi saggiati, negativo ai saggi fenotipici per la presenza di carbapenemasi, è stata dimostrata la presenza del gene blaKPC mediante Real-Time PCR. Per questo ceppo si può ipotizzare la presenza di mutazioni a carico del gene blaKPC che sebbene non interferiscano con il suo rilevamento mediante PCR (Real-Time PCR positiva), potrebbero condizionare l’attività della proteina prodotta (Saggio di Hodge modificato e Test di Sinergia negativi) riducendone la funzionalità come dimostrato, mediante analisi MALDI-TOF MS, dalla presenza dei picchi relativi sia all’idrolisi del farmaco sia dei picchi relativi al farmaco intatto. Questa ipotesi dovrebbe essere confermata mediante sequenziamento del gene blaKPC e successiva analisi strutturale della sequenza amminoacidica deducibile. L’utilizzo della tecnologia MALDI-TOF MS per la verifica dell’avvenuta idrolisi del maropenem è risultato un saggio fenotipico indiretto in grado di distinguere, al pari del test di Hodge modificato impiegato comunemente nella routine diagnostica in microbiologia, un ceppo produttore di carbapenemasi da un ceppo non produttore sia per scopi diagnostici che per la sorveglianza epidemiologica. L’impiego del MALDI-TOF MS ha mostrato, infatti, diversi vantaggi rispetto ai metodi convenzionali (Saggio di Hodge modificato e Test di Sinergia) impiegati nella routine diagnostica di laboratorio i quali richiedono personale esperto per l’interpretazione del risultato e lunghi tempi di esecuzione e di conseguenza di refertazione. La semplicità e la facilità richieste per la preparazione dei campioni e l’immediata acquisizione dei dati rendono questa tecnica un metodo accurato e rapido. Inoltre, il metodo risulta conveniente dal punto di vista economico, con un costo totale stimato di 1,00 euro per ceppo analizzato. Tutte queste considerazioni pongono questa metodologia in posizione centrale in ambito microbiologico anche nel caso del rilevamento di ceppi produttori di carbapenemasi. Indipendentemente dall’approccio identificativo utilizzato, comparato con i metodi convenzionali il MALDI-TOF MS conferisce in molti casi un guadagno in termini di tempo di lavoro tecnico (procedura pre-analititca per la preparazione dei campioni) e di tempo di ottenimento dei risultati (procedura analitica automatizzata). Questo risparmio di tempo si accentua quando sono analizzati in contemporanea un maggior numero di isolati. Inoltre, la semplicità e la facilità richieste per la preparazione dei campioni e l’immediata acquisizione dei dati rendono questo un metodo di identificazione accurato e rapido risultando più conveniente anche dal punto di vista economico, con un costo totale di 0,50 euro (materiale consumabile) per ceppo analizzato. I risultati ottenuti dimostrano che la spettrometria di massa MALDI-TOF sta diventando uno strumento importante in microbiologia clinica e sperimentale, data l’elevata efficacia identificativa, grazie alla disponibilità sia di nuove banche dati commerciali sia di aggiornamenti delle stesse da parte di diversi utenti, e la possibilità di rilevare con successo anche se in modo indiretto le antibiotico-resistenze.

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Purpose: The purpose of this paper is to focus on investigating and benchmarking green operations initiatives in the automotive industry documented in the environmental reports of selected companies. The investigation roadmaps the main environmental initiatives taken by the world's three major car manufacturers and benchmarks them against each other. The categorisation of green operations initiatives that is provided in the paper can also help companies in other sectors to evaluate their green practices. Design/methodology/approach: The first part of the paper is based on existing literature on the topic of green and sustainable operations and the "unsustainable" context of automotive production. The second part relates to the roadmap and benchmarking of green operations initiatives based on an analysis of secondary data from the automotive industry. Findings: The findings show that the world's three major car manufacturers are pursuing various environmental initiatives involving the following green operations practices: green buildings, eco-design, green supply chains, green manufacturing, reverse logistics and innovation. Research limitations/implications: The limitations of this paper start from its selection of the companies, which was made using production volume and country of origin as the principal criteria. There is ample evidence that other, smaller, companies are pursuing more sophisticated and original environmental initiatives. Also, there might be a gap between what companies say they do in their environmental reports and what they actually do. Practical implications: This paper helps practitioners in the automotive industry to benchmark themselves against the major volume manufacturers in three different continents. Practitioners from other industries will also find it valuable to discover how the automotive industry is pursuing environmental initiatives beyond manufacturing, apart from the green operations practices covering broadly all the activities of operations function. Originality/value: The originality of the paper is in its up-to-date analysis of environmental reports of automotive companies. The paper offers value for researchers and practitioners due to its contribution to the green operations literature. For instance, the inclusion of green buildings as part of green operations practices has so far been neglected by most researchers and authors in the field of green and sustainable operations. © Emerald Group Publishing Limited.