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1 year ago

Theoretical models and empirical studies

Certain functions and structures of ecosystems are valued by people because they serve to regulate Cilengitide conditions and the related aspects mentioned above, provide material products and contribute nonmaterial human benefits. To safeguard the regulating, provisioning and cultural services of ecosystems, their structures and functions need to be monitored and protected. This is the aim of environmental directives and conventions such as the EU Biodiversity Strategy to 2020 and the UNECE Convention on Long-range Transboundary Air Pollution (Air Convention, UNECE, 2013). The framework of the Air Convention, and the activities therein nerve net refer to climate change and ecological structures and functions, comprises the Cooperative Programme for Monitoring and Evaluation of the Long-range Transmission of Air Pollutants in Europe (EMEP) and the Working Group on Effects, which manage six International Cooperative Programmes (ICP). The ICP Forests, ICP Vegetation and ICP Integrated Monitoring are of special relevance for assessing the impacts of climate change and air pollution on ecological structures and functions.

1 year ago

The implementation of the integrated approach to a

In comparison, Fig. 10b shows the ranking obtained applying only the EIRA method, as described in Barjoveanu et al. (2010). This method, based on the environmental risk as index (see Table 4 of Appendix B, Supplementary data), pointed out S24, S5 and S32 as the first three critical WWTPs. The EIRA method, on the basis of its logical approach, was led to highlight the WWTPs characterized by a bigger impact on water bodies (due to the presence of criticalities related to the N and P removal). The conditions and relative problems inherent to these WWTPs have been widely documented in technical literature as shown in Nardelli et al. (2008). The methodology here proposed, besides applying the EIRA approach by using the index of environmental risk, takes into account other relevant parameters by also considering the technical, environmental, economic and social aspects. Thus, it A 987306 generates a sort of “effect of mediation” minimizing the environmental risk index for the benefit of the other criteria. The WWTPs identified (S30, S31 and S20) have been those impacting on the receiving water bodies and, at the same time, on the anthropic environment. In the cases of the WWTPs S30 and S32, many cases of complaints by the population as well as by the media were reported, respectively due to the damage caused by the discharging of the treated wastewater in the lagoon of Venice (Zonta et al., 2007) and disorders related to bad odours perceived by people living near the plant (Hayes et al., 2014). Thus, the defined prioritization methodology has allowed integrating several inputs, further characterizing the plant contexts and main issues. Overall, the outcomes well fit with the ones achieved by applying the well-documented EIRA approach, as highlighted by the shape similarity between Fig. 10a and b, but the detailed results have shown different WWTPs as the most critical situations in which to prioritize interventions and allocate economic resources. Therefore, the proposed methodology permitted, synergistically with EIRA approach, a further in-depth analysis by complementing other aspects of ascertained priority for the decision-makers work, synergistically providing complementary information to decision-makers.

1 year ago

The alternate C hysteresis dynamics may only account for

In these usually disconnected depositional zones, sediment can be an important source of P (Quinton et al., 2010), which, when activated and connected to the wider catchment can result in the transfer of vast fluxes of P in surface water (cf. Haygarth et al., 1999). Upon rainfall subsiding, concentrations rapidly decline as surface runoff ceases (Siwek et al., 2013), with a secondary pulse being observed on the falling limb of the hydrograph as P enters the river via shallow through-flow pathways.

1 year ago

To improve the local knowledge on sediment dynamics

In this paper we present a major revision to the InVEST Vilanterol trifenatate model to address limitations in its application for ecosystem-based management. The main limitation was the poor representation of landscape connectivity, defined here as the internal linkages between runoff and sediment sources in upper parts of a watershed and the corresponding sinks (Borselli et al., 2008). In more details, the hydrologic routing in the previous version of the model imposed that sediment retention was provided exclusively by the riparian zone, irrespective of the topography, and resulting in a likely overestimation of the retention service. The new model theory relies on the more realistic concept of hydrologic connectivity (Fryirs, 2013), which is among the most promising approaches to representing sediment transfer across multiple scales (Bracken et al., 2015). The InVEST model is based on a framework developed by Borselli et al. (2008) and is described in detail in this paper to highlight the strength of this approach for ecosystem services projects.

1 year ago

The AFM surface morphology of BSO

Fig. 1. Working scheme of a roller coater.Figure optionsDownload full-size imageDownload as PowerPoint slide
In rotary printing processes, a very frequently arising printing artifact is the so-called “ribbing” [24]. Ribbing describes the occurrence of ribs in between the gap of two moving rolls as it BYK 191023 can be seen in Fig. 2 (left). These ribs are transferred to the substrate and lead to an inhomogeneous surface topography of the deposited and dried layer as shown in Fig. 2 (right).
Fig. 2. Development of ribs in between the gap of moving rolls (left); printed ribs on a substrate (right).Adapted from [24].Figure optionsDownload full-size imageDownload as PowerPoint slide
The appearance of this undesired printing artifact is caused by capillary effects between the two rolls and can be evaluated by the dimensionless capillary number Ca (see Eq. (1)) [25].equation(1)Ca=μU¯σ
The value of the capillary number Ca is dependent on the viscosity μ and on the surface tension σ   of the ink as well as on the applied printing speed U¯. The calculation of the capillary number Ca is strictly spoken only suitable for fluids which provide Newtonian flow behavior. Ca is a machine parameter and the calculated absolute values cannot be used for the adaption of an ink to an arbitrary rotary printer. Even if important parameters as the gap distance between the metering roll and the applicator roll or the surface energy of both rolls are not considered, Ca is a useful tool to develop suitable inks for rotary printing and roller coating. The complex flow behavior during the coating process was studied in the past by flow simulation experiments [26].

1 year ago

Virtual water transfer concurrent with trade

It should be noted that, when considering power loss, the volume of virtual water flux of a line is unique, while electricity flux has two different values in each line. That is to say, the virtual water loss concurrent with the power loss in one line is allocated to its input node.
The virtual water flux flowing into RN486 j via the line-in branch can be represented asequation(8)wnLinj=∑m→jwLm
In the same way, the virtual water flux out of node j through the line-out branch can be calculated asequation(9)wnLoutj=∑j→mwLm
2.1.3. Load branch
Loads represent the electricity consumers, the sum of which represents the total amount of electricity consumption in a region. The electricity flux into the p  th load (p=1,2,3…,Pp=1,2,3…,P) is equal to its electricity consumption, which is represented by eLoadpeLoadp.
The electricity flux out of node j through the load branch can be represented asequation(10)enLoadj=∑p=1PeLoadp
The consumption water intensity of the p  th load, DCpDCp, is defined as the ratio of virtual water flux to the electricity flux into the pth load. In this way, the virtual water flux into the pth load can be calculated fromequation(11)wLoadp=DCp·eLoadpwLoadp=DCp·eLoadp

1 year ago

Based on the above discussion it was revealed

The photocatalytic activity of ZnO and Ag-doped ZnO was evaluated by measuring photocatalytic degradation of BPA and NP in water under the illumination of UV light. In the presence of only UV, the AM 281 degradation is remained constant. For the degradation experiment certain dosage of the previously-prepared catalyst was dispersed in 100 mL aqueous solution. Then, the suspension was magnetically stirred in darkness for 30 min to establish the adsorption/desorption equilibrium between molecules and the surface of the photocatalyst. Subsequently, the suspension was subjected to UV irradiation and hydrogen peroxide. At a taxon given time intervals 5 mL aliquots were withdrawn from the above suspension and were centrifuged to completely remove the suspended catalyst particles. The concentration of the solutions during the irradiation was determined by UV–Visible spectrophotometer using a SHIMADZU UV-1800 apparatus. The mineralization degree was detected by a Shimadzu TOC-VCBH Total Organic Carbon (TOC) analyzer.