845 research outputs found

    Structure of the vacuum states in the presence of isovector and isoscalar pairing correlations

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    The long standing problem of proton-neutron pairing and, in particular, the limitations imposed on the solutions by the available symmetries, is revisited. We look for solutions with non-vanishing expectation values of the proton, the neutron and the isoscalar gaps. For an equal number of protons and neutrons we find two solutions where the absolute values of proton and neutrons gaps are equal but have the same or opposite sign. The behavior and structure of these solutions differ for spin saturated (single l-shell) and spin unsaturared systems (single j-shell). In the former case the BCS results are checked against an exact calculation.Comment: 19 pages, 5 postscript figure

    Study of Giant Pairing Vibrations with neutron-rich nuclei

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    We investigate the possible signature of the presence of giant pairing states at excitation energy of about 10 MeV via two-particle transfer reactions induced by neutron-rich weakly-bound projectiles. Performing particle-particle RPA calculations on 208^{208}Pb and BCS+RPA calculations on 116^{116}Sn, we obtain the pairing strength distribution for two particles addition and removal modes. Estimates of two-particle transfer cross sections can be obtained in the framework of the 'macroscopic model'. The weak-binding nature of the projectile kinematically favours transitions to high-lying states. In the case of (~^6He, \~^4He) reaction we predict a population of the Giant Pairing Vibration with cross sections of the order of a millibarn, dominating over the mismatched transition to the ground state.Comment: Talk presented in occasion of the VII School-Semina r on Heavy Ion Physics hosted by the Flerov Laboratory (FLNR/JINR) Dubna, Russia from May 27 to June 2, 200

    Wastewater treatment plant as microplastics release source - Quantification and identification techniques

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    [EN] The high presence of microplastics (MPs) in different sizes, materials and concentrations in the aquatic environment is a global concern due to their potential physically and chemically harm to aquatic organisms including mammals. Furthermore, the bioaccumulation of these compounds is leading to their ingestion by humans through the consumption of sea food and even through the terrestrial food chain. Even though conventional wastewater treatment plants are capable of eliminating more than 90% of the influent MPs, these systems are still the main source of MPs introduction in the environment due to the high volumes of effluents generated and returned to the environment. The amount of MPs dumped by WWTP is influenced by the configuration of the WWTP, population served and influent flow. Thus, the average of MP/L disposed vary widely depending on the region. In addition to MPs disposed in water bodies, more than 80% of these emerging contaminants, which enter the WWTP, are retained in biosolids that can be applied as fertilizers, representing a potential source of soil contamination. Due to the continuous disposal of MPs in the environment by effluent treatment systems and their polluting potential, separation and identification techniques have been assessed by several researchers, but unfortunately, there are no standard protocols for them. Aiming to provide insight about the relevance of studying the WWTP as source of MPs, this review summarizes the currently methodologies used to classify and identify them.Bretas Alvim, C.; Mendoza Roca, JA.; Bes-Piá, M. (2020). Wastewater treatment plant as microplastics release source - Quantification and identification techniques. Journal of Environmental Management. 255:1-11. https://doi.org/10.1016/j.jenvman.2019.109739S111255Araujo, C. F., Nolasco, M. M., Ribeiro, A. M. P., & Ribeiro-Claro, P. J. 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Microplastic Ingestion by Zooplankton. Environmental Science & Technology, 47(12), 6646-6655. doi:10.1021/es400663fCourtene-Jones, W., Quinn, B., Murphy, F., Gary, S. F., & Narayanaswamy, B. E. (2017). Optimisation of enzymatic digestion and validation of specimen preservation methods for the analysis of ingested microplastics. Analytical Methods, 9(9), 1437-1445. doi:10.1039/c6ay02343fDevi, P., Das, U., & Dalai, A. K. (2016). In-situ chemical oxidation: Principle and applications of peroxide and persulfate treatments in wastewater systems. Science of The Total Environment, 571, 643-657. doi:10.1016/j.scitotenv.2016.07.032Duemichen, E., Braun, U., Senz, R., Fabian, G., & Sturm, H. (2014). Assessment of a new method for the analysis of decomposition gases of polymers by a combining thermogravimetric solid-phase extraction and thermal desorption gas chromatography mass spectrometry. Journal of Chromatography A, 1354, 117-128. doi:10.1016/j.chroma.2014.05.057Dümichen, E., Eisentraut, P., Bannick, C. G., Barthel, A.-K., Senz, R., & Braun, U. (2017). Fast identification of microplastics in complex environmental samples by a thermal degradation method. Chemosphere, 174, 572-584. doi:10.1016/j.chemosphere.2017.02.010Dyachenko, A., Mitchell, J., & Arsem, N. (2017). Extraction and identification of microplastic particles from secondary wastewater treatment plant (WWTP) effluent. Analytical Methods, 9(9), 1412-1418. doi:10.1039/c6ay02397eElert, A. M., Becker, R., Duemichen, E., Eisentraut, P., Falkenhagen, J., Sturm, H., & Braun, U. (2017). Comparison of different methods for MP detection: What can we learn from them, and why asking the right question before measurements matters? Environmental Pollution, 231, 1256-1264. doi:10.1016/j.envpol.2017.08.074Enders, K., Lenz, R., Beer, S., & Stedmon, C. A. (2016). 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Environmental Science & Technology, 46(6), 3060-3075. doi:10.1021/es2031505Hidayaturrahman, H., & Lee, T.-G. (2019). A study on characteristics of microplastic in wastewater of South Korea: Identification, quantification, and fate of microplastics during treatment process. Marine Pollution Bulletin, 146, 696-702. doi:10.1016/j.marpolbul.2019.06.071Huerta Lwanga, E., Mendoza Vega, J., Ku Quej, V., Chi, J. de los A., Sanchez del Cid, L., Chi, C., … Geissen, V. (2017). Field evidence for transfer of plastic debris along a terrestrial food chain. Scientific Reports, 7(1). doi:10.1038/s41598-017-14588-2Hurley, R. R., Lusher, A. L., Olsen, M., & Nizzetto, L. (2018). Validation of a Method for Extracting Microplastics from Complex, Organic-Rich, Environmental Matrices. Environmental Science & Technology, 52(13), 7409-7417. doi:10.1021/acs.est.8b01517Jochem, G., & Lehnert, R. J. (2002). On the potential of Raman microscopy for the forensic analysis of coloured textile fibres. Science & Justice, 42(4), 215-221. doi:10.1016/s1355-0306(02)71831-5Kalčíková, G., Alič, B., Skalar, T., Bundschuh, M., & Gotvajn, A. Ž. (2017). Wastewater treatment plant effluents as source of cosmetic polyethylene microbeads to freshwater. Chemosphere, 188, 25-31. doi:10.1016/j.chemosphere.2017.08.131Käppler, A., Fischer, D., Oberbeckmann, S., Schernewski, G., Labrenz, M., Eichhorn, K.-J., & Voit, B. (2016). Analysis of environmental microplastics by vibrational microspectroscopy: FTIR, Raman or both? Analytical and Bioanalytical Chemistry, 408(29), 8377-8391. doi:10.1007/s00216-016-9956-3Käppler, A., Fischer, M., Scholz-Böttcher, B. M., Oberbeckmann, S., Labrenz, M., Fischer, D., … Voit, B. (2018). Comparison of μ-ATR-FTIR spectroscopy and py-GCMS as identification tools for microplastic particles and fibers isolated from river sediments. Analytical and Bioanalytical Chemistry, 410(21), 5313-5327. doi:10.1007/s00216-018-1185-5Lares, M., Ncibi, M. C., Sillanpää, M., & Sillanpää, M. (2018). Occurrence, identification and removal of microplastic particles and fibers in conventional activated sludge process and advanced MBR technology. Water Research, 133, 236-246. doi:10.1016/j.watres.2018.01.049Lei, K., Qiao, F., Liu, Q., Wei, Z., Qi, H., Cui, S., … An, L. (2017). Microplastics releasing from personal care and cosmetic products in China. Marine Pollution Bulletin, 123(1-2), 122-126. doi:10.1016/j.marpolbul.2017.09.016Lenz, R., Enders, K., Stedmon, C. A., Mackenzie, D. M. A., & Nielsen, T. G. (2015). A critical assessment of visual identification of marine microplastic using Raman spectroscopy for analysis improvement. Marine Pollution Bulletin, 100(1), 82-91. doi:10.1016/j.marpolbul.2015.09.026Leslie, H. A., Brandsma, S. H., van Velzen, M. J. M., & Vethaak, A. D. (2017). Microplastics en route: Field measurements in the Dutch river delta and Amsterdam canals, wastewater treatment plants, North Sea sediments and biota. Environment International, 101, 133-142. doi:10.1016/j.envint.2017.01.018Li, J., Liu, H., & Paul Chen, J. (2018). Microplastics in freshwater systems: A review on occurrence, environmental effects, and methods for microplastics detection. Water Research, 137, 362-374. doi:10.1016/j.watres.2017.12.056Li, X., Chen, L., Mei, Q., Dong, B., Dai, X., Ding, G., & Zeng, E. Y. (2018). Microplastics in sewage sludge from the wastewater treatment plants in China. Water Research, 142, 75-85. doi:10.1016/j.watres.2018.05.034Liu, X., Yuan, W., Di, M., Li, Z., & Wang, J. (2019). Transfer and fate of microplastics during the conventional activated sludge process in one wastewater treatment plant of China. Chemical Engineering Journal, 362, 176-182. doi:10.1016/j.cej.2019.01.033Löder, M. G. J., Imhof, H. K., Ladehoff, M., Löschel, L. A., Lorenz, C., Mintenig, S., … Gerdts, G. (2017). Enzymatic Purification of Microplastics in Environmental Samples. Environmental Science & Technology, 51(24), 14283-14292. doi:10.1021/acs.est.7b03055Long, Z., Pan, Z., Wang, W., Ren, J., Yu, X., Lin, L., … Jin, X. (2019). Microplastic abundance, characteristics, and removal in wastewater treatment plants in a coastal city of China. Water Research, 155, 255-265. doi:10.1016/j.watres.2019.02.028Maes, T., Jessop, R., Wellner, N., Haupt, K., & Mayes, A. G. (2017). A rapid-screening approach to detect and quantify microplastics based on fluorescent tagging with Nile Red. Scientific Reports, 7(1). doi:10.1038/srep44501Magni, S., Binelli, A., Pittura, L., Avio, C. G., Della Torre, C., Parenti, C. C., … Regoli, F. (2019). The fate of microplastics in an Italian Wastewater Treatment Plant. Science of The Total Environment, 652, 602-610. doi:10.1016/j.scitotenv.2018.10.269Mahon, A. M., O’Connell, B., Healy, M. G., O’Connor, I., Officer, R., Nash, R., & Morrison, L. (2016). Microplastics in Sewage Sludge: Effects of Treatment. 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Are Nitric Acid (HNO3) Digestions Efficient in Isolating Microplastics from Juvenile Fish? Water, Air, & Soil Pollution, 228(12). doi:10.1007/s11270-017-3654-4Napper, I. E., Bakir, A., Rowland, S. J., & Thompson, R. C. (2015). Characterisation, quantity and sorptive properties of microplastics extracted from cosmetics. Marine Pollution Bulletin, 99(1-2), 178-185. doi:10.1016/j.marpolbul.2015.07.029Ng, E.-L., Huerta Lwanga, E., Eldridge, S. M., Johnston, P., Hu, H.-W., Geissen, V., & Chen, D. (2018). An overview of microplastic and nanoplastic pollution in agroecosystems. Science of The Total Environment, 627, 1377-1388. doi:10.1016/j.scitotenv.2018.01.341Nizzetto, L., Futter, M., & Langaas, S. (2016). Are Agricultural Soils Dumps for Microplastics of Urban Origin? Environmental Science & Technology, 50(20), 10777-10779. doi:10.1021/acs.est.6b04140Nuelle, M.-T., Dekiff, J. H., Remy, D., & Fries, E. (2014). A new analytical approach for monitoring microplastics in marine sediments. 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    Pairing in 4-component fermion systems: the bulk limit of SU(4)-symmetric Hamiltonians

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    Fermion systems with more than two components can exhibit pairing condensates of much more complex structure than the well-known single BCS condensate of spin-up and spin-down fermions. In the framework of the exactly solvable SO(8) Richardson-Gaudin model with SU(4)-symmetric Hamiltonians, we show that the BCS approximation remains valid in the thermodynamic limit of large systems for describing the ground state energy and the canonical and quasiparticle excitation gaps. Correlations beyond BCS pairing give rise to a spectrum of collective excitations, but these do not affect the bulk energy and quasiparticle gaps.Comment: 13 pages; 2 figures; 1 tabl

    Towards the decays of NˉX(1625)\bar{N}_X(1625) in the molecular picture

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    In this talk, we firstly overview the experimental status of NˉX(1625)\bar{N}_X(1625), which is an enhancement structure observed in KΛˉK^{-}\bar{\Lambda} invariant mass spectrum of J/ψpKΛˉJ/\psi\to pK^{-}\bar{\Lambda} process. Then we present the result of the decay of NˉX(1625)\bar{N}_X(1625) under the two molecular assumptions, i.e. S-wave ΛˉK\bar\Lambda K^- and S-wave Σˉ0K\bar{\Sigma}^0K^- molecular states. Several experimental suggestions for NˉX(1625)\bar{N}_X(1625) are proposed.Comment: 5 pages, 6 figures, 2 tables. Contribution to the Workshop on the Physics of Excited Nucleon-NSTAR2009, Beijing April 19-22, 200

    Generalized Pseudo-SU(3) Model and Pairing

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    The pseudo-SU(3) model is extended to explicitly include the spin and proton-neutron degrees of freedom. A general formalism for evaluating matrix elements of one-body and two-body tensor operators within this framework is presented. The pairing interaction, which couples different irreducible representations of SU(3), is expressed in terms of pseudo-space tensors and a general result is given for calculating its matrix elements. The importance of pairing correlations in pseudo-SU(3) model calculations is demonstrated by examining the dependence of wavefunctions, low-energy collective excitation spectra, and moments of inertia on the strength of the pairing interaction.Comment: 21 Pages, 7 Figures (available upon request), Nucl. Phys. A in pres

    Anharmonic properties of double giant dipole resonance

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    A systematic microscopic study of the anharmonic properties of the double giant dipole resonance (DGDR) has been carried out, for the first time, for nuclei with mass number AA spanning the whole mass table. It is concluded that the corrections of the energy centroid of the Jπ=0+J^{\pi} = 0^+ and 2+2^+ components of the DGDR from its harmonic limit are negative, have a value of the order of few hundred keV and follow an A1A^{-1} dependence.Comment: 4 pages, 2 figure
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