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Abstract

The article presents the current state of the CNG market used as an alternative fuel for car engines. Attention was paid to European Union directives requirements and the current state of the directives’ fulfillment. The economic aspect of CNG usage was analyzed and the approximate costs of driving 10,000 km on different fuels in the last four years were presented. The PtG process which uses electric energy (hydrogen production) and carbon dioxide captured from the flue gas for the production of synthetic methane were discussed. The scheme of the SNG plant with the indication of its most important components was presented, and attention was paid to the mutual complementation of PtG technologies with carbon dioxide capture technology. The benefits of synthetic methane production are presented and the use of compressed natural gas to power engines in vehicles has been described. First, the focus was on the single-fuel use of CNG in bus and truck engines, paying particular attention to the ecological aspect of the implemented solutions. It has been shown that the use of compressed natural gas will reduce almost 100% of the particulates emission from the combustion process. The advantages and disadvantages of the alternative fuel supply are given. Next, the aspect of dual-fuel use in diesel engines was analyzed on the example of a smaller engine. The degree of reduction of harmful compounds emission from the combustion process is shown. Finally, attention was paid to the possible scale effect, referring to the number of motor vehicles in Poland.

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Authors and Affiliations

Szymon Dobras
Lucyna Więcław-Solny
Andrzej Wilk
Adam Tatarczuk
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Abstract

Environmental applications of carbon nanotubes (CNTs) have recently attracted worldwide attentiondue to their excellent adsorption capacities and promising physical, chemical and mechanical properties, as well asthe preparation of novel membranes with attractive features for water purification. This paper critically reviews therecent progress on the preparation and applications of CNT based membranes in water and wastewater treatment. Various synthesis techniques for the preparation of CNT based membranes are discussed. The functionalization ofCNTs, which involves chemical/physical modification of pristine CNTs with different types of functional groups,improves the capabilities of CNT for water and wastewater treatment and/or removal of waterborne contaminants.The CNT-based membrane applications are found to possess a variety of advantages, including improving waterpermeability, high selectivity and antifouling capability. However, their applications at full scale are still limitedby their high cost. Finally, we highlight that CNT membranes with promising removal efficiencies for respectivecontaminants can be considered for commercialization and to achieve holistic performance for the purpose ofwater treatment and desalination. This paper may provide an insight for the development of CNT based membranesfor water purification in the future. With their tremendous separation performance, low biofouling potential andultra-high water flux, CNT membranes have the potential to be a leading technology in water treatment, especiallydesalination.
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Bibliography

  1. Adamczak, M., Kaminska, G. & Bohdziewicz, J. (2019). Preparation of polymer membranes by in situ interfacial polymerization. International Journal of Polymer Science, vol. 219, Article ID 6217924, 13 pages, DOI: 10.1155/2019/6217924
  2. Ahmad, A., El-Nour, K.A., Ammar, R.A.A. & Al-Warthan, A., (2012). Carbon nanotubes, science and technology part (I) structure, synthesis and characterization., Arabian Journal of Chemistry, 5, pp. 1–23, DOI: 10.1016/j.arabjc.2010
  3. Ahmed, F., Santos, C.M., Mangadlao, J., Advincula, R. & Rodrigues, D.F. (2013). Antimicrobial PVK: SWNT nanocomposite coated membrane for water purification: performance and toxicity testing, Water Res., 47, 12, pp. 3966–3975, DOI: 10.1016/j.watres.2012.10.055
  4. Ahn, C.H, Baek, Y., Lee, C., Kim, S.O., Kim, S., Lee, S., Kim, S.H. Bae, S.S., Park, J. & Yoon, J. (2012). Carbon nanotube-based membranes: fabrication and application to desalination. J. Ind. Eng. Chem.,18, pp. 1551–1559, DOI: 10.1016/j.jiec.2012.04.005.
  5. Ajmani, G.S., Goodwin, D., Marsh, K., Fairbrother, D.H., Schwab, K.J., Jacangelo, J.G. & Huang, H. (2012). Modification of low pressure membranes with carbon nanotube layers for fouling control, Water Res., 46, 17, pp. 5645–5654, DOI:10.1016/j.watres.2012.07.059.
  6. Ali, S., Ur Rehman, S.A., Luan, H.Y., Usman Farid, M. & Huang, H. (2019). Challenges and opportunities in functional carbon nanotubes for membrane-based water treatment and desalination. Science of the Total Environment, 646, pp.1126–1139, DOI: 10.1016/j.scitotenv.2018.07.348.
  7. Al-Hakami, S.M., Khalil, A.B., Laoui, T. & Atieh, M.A. (2013). Fast disinfection of Escherichia coli bacteria using carbon nanotubes interaction with microwave radiation. Bioinorg. Chem. Appl.,458943, DOI: 10.1155/2013/458943.
  8. Al-Khaldi, F.A., Abu-Sharkh, B., Abulkibash, A.M. & Atieh, M.A. (2013). Cadmium removal by activated carbon, carbon nanotubes, carbon nanofibers, and carbon fly ash: a comparative study. Desalin. Water Treat., 53, pp. 1–13, DOI: 10.1080/19443994.2013.847805.
  9. Ansari, R. & Kazemi, E. (2012). Detailed investigation on single water molecule entering carbon nanotubes. App. Math. Mech., 33, pp.1287–1300, DOI: 10.1007/s10483-012-1622-8.
  10. Atieh, M.A., Bakather, O.Y., Tawabini, B.S., Bukhari, A.A., Khaled, M., Alharthi, M., Fettouhi, M. & Abuilaiwi, F.A. (2010). Removal of chromium (III) from water by using modified and nonmodified carbon nanotubes, J. Nanomater., Article ID 232378, pp.1-9, DOI: 10.1155/2010/232378.
  11. Baek, Y., Kim, C., Kyun, D., Kim, T., Seok, J., Hyup, Y., Hyun, K., Seek, S., Cheol, S., Lim, J., Lee, K. & Yoon, J. (2014), High performance and antifouling vertically aligned carbon nanotube membrane for water purification. J. Membr. Sci., 460, 171–177, DOI: 10.1016/j.memsci.2014.02.042.
  12. Bahgat, M., Farghali, A.A., El Rouby, W.M.A. & Khedr, M.H. (2011). Synthesis and modification of multi-walled carbon nano-tubes (MWCNTs) for water treatment applications, J. Anal. Appl. Pyrolysis, 92, 2, pp. 307–313, DOI: 10.1016/j.jaap.2011.07.002.
  13. Bai, L., Liang, H., Crittenden, J., Qu, F., Ding, A., Ma, J., Du, X., Guo, S. & Li, G. (2015), Surface modification of UF membranes with functionalized MWCNTs to control membrane fouling by nom fractions. J. Membr. Sci., 492, 400–411, DOI: 10.1016/j.memsci.2015.06.006.
  14. Balasubramanian, K. & Burghard, M. (2005). Chemically functionalized carbon nanotubes, Small, 1, pp. 180–192, DOI: 10.1002/smll.200400118.
  15. Bhadra, M., Roy, S. & Mitra, S. (2013). Enhanced desalination using carboxylated carbon nanotube immobilized membranes. Sep. Purif. Technol., 120, pp. 373–377, DOI: 10.1016/j.seppur.2013.10.020.
  16. Bodzek, M. & Konieczny, K. (2017). Membrane techniques in the treatment of geothermal water for fresh and potable water production. [In:] Geothermal Water Management, Bundschuh, J. & Tomaszewska, B. (Eds.). CRC Press/Balkema, Taylor and Francis Group, Ch. 8, pp. 157–231, DOI: 10.1201/9781315734972.
  17. Bodzek, M. (2019). Membrane separation techniques – removal of inorganic and organic admixtures and impurities from water environment – review, Archives of Environmental Protection, 45, 4, pp. 4-19. DOI: 10.24425/aep.2019.130237.
  18. Bodzek, M., Konieczny, K. & Rajca, M. (2019). Membranes in water and wastewater disinfection – review. Archives of Environmental Protection, 45 (1), pp. 3-18, DOI: 10.24425/aep.2019.126419.
  19. Bodzek, M., Konieczny, K. & Kwiecińska-Mydlak, A. (2020a). Nanotechnology in water and wastewater treatment. Graphene – the nanomaterial for next generation of semipermeable membranes. Critical Reviews in Environmental Science and Technology, 50, 15, pp. 1515-1579, DOI: 10.1080/10643389.2019.1664258.
  20. Bodzek, M., Konieczny, K. & Kwiecińska-Mydlak, A. (2020b). The application of nanomaterial adsorbents for the removal of impurities from water and wastewaters: a review, Desalination and Water Treatment, 185, pp. 1-26, DOI: 10.5004/dwt.2020.25454
  21. Bodzek, M., Konieczny, K. & Kwiecińska-Mydlak, A. (2020c). The application for nanotechnology and nanomaterials in water and wastewater treatment. Membranes, photocatalysis and disinfection, Desalination and Water Treatment, 186, pp. 88–106, DOI:10.5004/dwt.2020.25231
  22. Brady-Estévez, A.S., Kang, S. & Elimelech, M. (2008). A single‐walled‐carbon‐nanotube filter for removal of viral and bacterial pathogens, Small, 4, 4, pp. 481–484. DOI: 10.1002/smll.200700863.
  23. Brady-Estévez, A.S., Schnoor, M.H., Kang, S. & Elimelech, M. (2010). SWNT–MWNT hybrid filter attains high viral removal and bacterial inactivation, Langmuir, 26, pp. 19153–19158. DOI: 10.1021/la103776y.
  24. Brunet, L., Lyon, D., Zodrow, K., Rouch, J.-C., Caussat, B., Serp, P., Remigy, J.-C., Wiesner, M. & Alvarez, P.J. (2008). Properties of membranes containing semi- dispersed carbon nanotubes, Environ. Eng. Sci., 25, pp. 565–575. DOI: 10.1089/ees.2007.0076.
  25. Celik, E., Park, H., Choi, H. & Choi, H. (2011). Carbon nanotube blended polyethersulfone membranes for fouling control in water treatment, Water Res., 45, pp. 274–282. DOI: 10.1016/j.watres.2010.07.060.
  26. Chan, Y. & Hill, J.M. (2012). Modeling on ion rejection using membranes comprising ultrasmall radii carbon nanotubes, Eur. Phys. J. B, 85, pp. 56. DOI: 10.1140/epjb/e2012-21029-0.
  27. Chan, Y. & Hill, J.M. (2013). Ion selectivity using membranes comprising functionalized carbon nanotubes, J. Math. Chem., 53, pp. 1258–1273. DOI: 10.1007/s10910-013-0142-y.
  28. Chan ,W.-F., Chen, H.-Y., Surapathi, A., Taylor, M.G., Shao, X., Marand, E. & Johnson, J.K. (2013). Zwitterion functionalized carbon nanotube/polyamide nanocomposite membranes for water desalination, ACS Nano, 7, pp. 5308–5319.; DOI: 10.1021/nn4011494.
  29. Chen, H., Li, J., Shao, D., Ren, X. & Wang, X. (2012). Poly(acrylic acid) grafted multiwall carbon nanotubes by plasma techniques for Co(II) removal from aqueous solution, Chem. Eng. J., 210, pp. 475–481. DOI: 10.1016/j.cej.2012.08.082.
  30. Chen, X., Qiu, M., Ding, H., Fu, K. & Fan, Y. (2016). A reduced graphene oxide nanofiltration membrane intercalated by well-dispersed carbon nanotubes for drinking water purification, Nanoscale, 8, pp. 5696–5705./ DOI: 10.1039/c5nr08697c.
  31. Chi, M.F., Wu,W.L., Du,Y., Chin,C.J. & Lin, C.C. (2016). Inactivation of Escherichia coli planktonic cells by multi-walled carbon nanotubes in suspensions: Effect of surface function-nalization coupled with medium nutrition level, J Hazard. Mater., 318, pp. 507-514. DOI: 10.1016/j.jhazmat.2016.07.013.
  32. Choi, J., Jegal, J. & Kim, W. (2006). Fabrication and characterization of multi-walled carbon nanotubes/polymer blend membranes, J. Membr. Sci., 284, pp. 406–415. DOI: 10.1016/j.memsci.2006.08.013.
  33. Chung, Y.T., Mahmoudi, E., Mohammad, A.W., Benamor, A., Johnson, D. & Hilal, N. (2017). Development of polysulfone-nanohybrid membranes using ZnO-GO composite for enhanced antifouling and antibacterial control, Desalination, 402, pp. 123–132. DOI: 10.1016/j.desal.2016.09.030.
  34. Corry, B. (2008). Designing carbon nanotube membranes for efficient water desalination, J.Phys. Chem. B, 112, pp. 1427–1434. DOI: 10.1021/jp709845u.
  35. Corry, B. (2011). Water and ion transport through functionalised carbon nanotubes: implications for desalination technology, Energy Environ Sci., 4, pp. 751-759. DOI: 10.1039/C0EE00481B.
  36. Dalmas F., Chazeau, L., Gauthier, C., Masenelli-Varlot, K., Dendievel, R., Cavaillé, J.Y. & Forró, L. (2005). Multiwalled carbon nanotube/polymer nanocomposites: processing and properties, J. Polym. Sci. B Polym. Phys., 43, pp.1186–1197. DOI: 10.1002/polb.20409.
  37. Das, R., Abd Hamid, S.B., Ali, M.E., Ismail, A.F., Annuar, M.S.M. & Ramakrishna, S. (2014a). Multifunctional carbon nanotubes in water treatment: the present, past and future, Desalination, 354, pp. 160–179. DOI: 10.1016/j.desal.2014.09.032.
  38. Das, R., Ali, M.E., Hamid, S.B.A., Ramakrishna, S. & Chowdhury, Z.Z. (2014b). Carbon nanotube membranes for water purification: a bright future in water desalination, Desalination, 336, pp. 97–109. DOI: 10.1016/j.desal.2013.12.026.
  39. Daer, S., Kharraz, J., Giwa, A. & Hasan, S.W. (2015). Recent applications of nanomaterials in water desalination: a critical review and future opportunities, Desalination, 367, pp. 37–48. DOI: 10.1016/j.desal.2015.03.030.
  40. de Lannoy, C.-F., Soyer, E. & Wiesner, M.R. (2013). Optimizing carbon nanotube-reinforced polysulfone ultrafiltration membranes through carboxylic acid functionalization, J. Membr. Sci.,447, pp. 395–402. DOI: 10.1016/j.memsci.2013.07.023.
  41. Dobrzańska-Danikiewicz, A.D., Łukowiec, D., Cichocki, D. & Wolany, W. (2015). Nanokompozyty złożone z nanorurek węglowych pokrytych nanokryształami metali szlachetnych, Open Access Library, Annal V Issue 2, International OCSCO World Press. (in Polish). http://www.openaccesslibrary.com/vol22015/cover.pdf.
  42. Dufresne, A., Paillet, M., Putaux, J.L., Canet, R., Carmona, F., Delhaes, P. & Cui, S. (2002). Processing and characterization of carbon nanotube/poly(styrene-co-butyl acrylate) nanocomposites, J. Mater. Sci., 37, pp. 3915–3923. DOI: 10.1023/A:1019659624567.
  43. Dumée, L., Campbell, J.L., Sears, K., Schutz, J., Finn, N., Duke, M. & Gray, S. (2011). The Impact of hydrophobic coating on the performance of carbon nanotube bucky paper membranes in membrane distillation, Desalination, 283, pp. 64–67. DOI: 10.1016/j.desal.2011.02.046.
  44. Engel, M. & Chefetz, B. (2016). Adsorption and desorption of dissolved organic matter by carbon nanotubes: effects of solution chemistry, Environ. Pollut., 213, pp. 90–98. DOI: 10.1016/j.envpol.2016.02.009.
  45. Fornasiero, F., Park, H.G., Holt, J.K., Stadermann, M., Grigoropoulos, C.P., Noy, A. & Bakaijn, O. (2008). Ion exclusion by sub-2-nm carbon nanotube pores, Proc. Natl. Acad. Sci., 105, pp. 17250–17255. DOI: 10.1073/pnas.0710437105.
  46. Goh, P.S, Ismail, A.F. & Ng, B.C. (2013a). Carbon nanotubes for desalination: Performance evaluation and current hurdles, Desalination, 308, pp. 2–14. DOI: 10.1016/j.desal.2012.07.040.
  47. Goh, K., Setiawan, L., Wei, L., Jiang, W., Wang, R. & Chen, Y. (2013b). Fabrication of novel functionalized multi-walled carbon nanotube immobilized hollow fiber membranes for enhanced performance in forward osmosis process, J. Membr. Sci., 446, pp. 244–254. DOI: 10.1016/j.memsci.2013.06.022.
  48. Goh, P.S. & Ismail, A.F. (2015). Graphene-based nanomaterial: the state-of-the-art material for cutting edge desalination technology, Desalination, 356, pp. 115–128. DOI: 10.1016//j.desal.2014.10.001
  49. Goh, K., Karahan, H.E., Wei, L., Bae, T.-H., Fane, A.G., Wang, R. & Chen, Y. (2016a). Carbon nanomaterials for advancing separation membranes: a strategic perspective, Carbon, 109, pp. 694–710. DOI: 10.1016/j.carbon.2016.08.077.
  50. Goh, P.S., Ismail, A.F. & Hilal, N. (2016b). Nano-enabled membranes technology: sustainable and revolutionary solutions for membrane desalination? Desalination, 380, pp. 100–104. DOI: 10.1016/j.desal.2015.06.002.
  51. Goh, P.S., Matsuura, T., Ismail, A.F. & Hilal, N. (2016c). Recent trends in membranes and membrane processes for desalination, Desalination, 391, pp. 43–60. DOI: 10.1016/j.desal.2015.12.016
  52. Gong, J.L., Wang, B., Zeng, G.M., Yang, C.P., Niu, C.G., Niu, Q.Y., Zhou, W.J. & Liang, Y. (2009). Removal of cationic dyes from aqueous solution using magnetic multi-wall carbon nanotube nanocomposite as adsorbent, J. Hazard. Mater., 164, 2-3, pp. 1517-1522. DOI: 10.1016/j.jhazmat.2008.09.072.
  53. Guo, J., Zhang, Q., Cai, Z. & Zhao, K. (2016). Preparation and dye filtration property of electrospun polyhydroxybutyrate–calcium alginate/carbon nanotubes composite nanofibrous filtration membrane, Sep. Purif. Technol., 161, pp. 69-79. DOI: 10.1016/j.seppur.2016.01.036.
  54. Han, Y., Xu, Z. & Gao, C. (2013). Ultrathin graphene nanofiltration membrane for water purification, Adv. Funct. Mater., 23, pp. 3693–3700. DOI: 10.1002/adfm.201202601.
  55. Hinds, B.J., Chopra, N., Rantell, T., Andrews, R., Gavalas, V. & Bachas, L.G. (2004). Aligned multiwalled carbon nanotube membranes, Science, 303, pp. 62–65. DOI: 10.1126/science.1092048.
  56. Holt, J.K., Park, H.G., Wang, Y., Stadermann, M., Artyukhin, A.B., Grigoropoulos, C.P, Noy, A. & Bakajin, O. (2006). Fast mass transport through sub-2-nanometer carbon nanotubes, Science, 312, pp. 1034–1037. DOI: 10.1126/science.1126298.
  57. Hoon, C., Baek, Y., Lee, C., Ouk, S., Kim, S., Lee, S., Kim, S., Seek, S., Park, J. & Yoon, J. (2012). Carbon nanotube-based membranes: fabrication and application to desalination, J.Ind. Eng. Chem., 18, pp. 1551–1559. DOI: 10.1016/j.jiec.2012.04.005.
  58. Hou, C.-H., Liu, N.-L., Hsu, H.-L. & Den, W. (2014). Development of multi-walled carbon nanotube/poly(vinyl alcohol) composite as electrode for capacitive deionization, Sep. Purif. Technol., 130, pp. 7–14. DOIL: 10.1016/j.seppur.2014.04.004.
  59. Huczko, A., Kurcz, M. & Popławska, M. (2015). Nanorurki węglowe. Otrzymywanie, charakterystyka, zastosowania, Wydawnictwo Uniwersytetu Warszawskiego, Warszawa.
  60. Hummer, G., Rasaiah,i J.C. & Noworyta, J.P. (2001). Water conduction through the hydrophobic channel of a carbon nanotube, Nature, 414, pp. 188–190. DOI: 10.1038/35102535
  61. Ihsanullah, F.A., Al-Khaldi, B. Abu-sharkh, M., Khaled Atieh, M.A., Nasser, M.S., Laoui, T., Saleh, T.A., Agarwal, S., Tyagi, I. & Gupta, V.K. (2015a). Adsorptive removal of cadmium(II) ions from liquid phase using acid modified carbon-based adsorbents, J.Mol.Liq., 204, pp. 255–263. DOI: 10.1016/j.molliq.2015.01.033.
  62. Ihsanullah, H.A., Asmaly, T.A., Saleh, T., Laoui, V.K., Gupta, M.A. & Atieh, M.A. (2015b). Enhanced adsorption of phenols from liquids by aluminum oxide/carbon nanotubes: comprehensive study from synthesis to surface properties, J. Mol. Liq., 206, pp 176–182. DOI: 10.1016/j.molliq.2015.02.028.
  63. Ihsanullah, T.L., Marwan, K., Muataz, A.A., Adnan, M.A., Amjad, B.K. & Aamir, A. (2015c). Novel anti-microbial membrane for desalination pretreatment: a silver nanoparticle-doped carbon nanotube membrane, Desalination, 376, pp. 82–93. DOI: 10.1016/j.desal.2015.08.017.
  64. Ihsanullah A.A., Al-Amer, A.M., Laoui, T., Al-Marri, M.J., Nasser, M.S., Khraisheh, M. & Atieh, M.A. (2016a). Heavy metal removal from aqueous solution by advanced carbon nanotubes: critical review of adsorption applications, Sep. Purif. Technol., 157, pp. 141–161. DOI: 10.1016/j.seppur.2015.11.039.
  65. Ihsanullah, A., Al Amer, A.M., Laoui, T., Abbas, A., Al-Aqeeli, N., Patel, F., Khraisheh, M., Atieh, M.A., Hilal, N. (2016b). Fabrication and antifouling behaviour of a carbon nanotube membrane, Mater. Des., 89, pp. 549–558. DOI: 10.1016/j.matdes.2015.10.018.
  66. Ihsanullah, F.A., Al-Khaldi, B., Abu-sharkh, M., A., Qureshi, M.I., Laoui, T. & Atieh, M.A. (2016c). Effect of acid modification on adsorption of hexavalent chromium (Cr(VI)) from aqueous solution by activated carbon and carbon nanotubes, Desalin.Water Treat., 57, pp. 7232–7244. DOI: 10.1080/19443994.2015.102184.
  67. Ihsanullah, A.A. (2019). Carbon nanotube membranes for water purification: Developments, challenges, and prospects for the future, Sep Purif Technol., 209, pp. 307–337. DOI: 10.1016/j.seppur.2018.07.043.
  68. Jia, G., Wang, H., Yan, L., Wang, X., Pei, R., Yan, T., Zhao, Y. & Guo, X. (2005). Cytotoxicity of carbon nanomaterials: Single-wall nanotube, multi-wall nanotube, and fullerene, Environmental Science & Technology, 39, pp. 1378-1383. DOI: 10.1021/es048729l.
  69. Kabbashi, N.A., Atieh, M.A., Al-Mamun, A., Mirghami, M.E.S., Alam, M.D.Z. & Yahya, N. (2009). Kinetic adsorption of application of carbon nanotubes for Pb(II) removal from aqueous solution, J. Environ. Sci., 21, 4, pp. 539–544. DOI: 10.1016/S1001-0742(08)62305-0.
  70. Kaminska, G., Bohdziewicz, J., Palacio, L., Hernández, A. & Prádanos, P. (2016). Polyacrylonitrile membranes modified with carbon nanotubes: Characterization and micropollutants removal analysis, Desalin. Water Treat., 57, pp. 1344–1353. DOI: 10.1080/19443994.2014.1002277.
  71. Kandah, M.I. & Meunier, J.L. (2007). Removal of nickel ions from water by multi-walled carbon nanotubes, J. Hazard. Mater., 146, 1-2, pp. 283-288. DOI: 10.1016/j.jhazmat.2006.12.019.
  72. Kang, S., Pinault, M., Pfefferle, L.D. & Elimelech, M. (2007). Single-walled carbon nanotubes exhibit strong antimicrobial activity, Langmuir, 23, pp. 8670–8673. DOI: 10.1021/la701067r.
  73. Kang, S., Herzberg, M., Rodrigues, D.F. & Elimelech, M. (2008). Antibacterial effects of carbon nanotubes: Size does matter, Langmuir, 24, pp. 6409–6413. DOI: 10.1021/la800951v.
  74. Kang G.D., Cao Y.M. (2012). Development of antifouling reverse osmosis membranes for water treatment: a review, Water Res., 46, 3, pp. 584–600. DOI: 10.1016/j.watres.2011.11.041.
  75. Kar, S., Bindal, R.C. & Tewari, P.K. (2012). Carbon nanotube membranes for desalination and water purification: challenges and opportunities, Nano Today, 7, pp. 385–389. DOI: 10.1016/j.nantod.2012.09.002.
  76. Khalid, A., Al-Juhani, A.A., Al-Hamouz, O.C., Laoui, T., Khan, Z. & Atieh, M.A. (2015). Preparation and properties of nanocomposite polysulfone/multi-walled carbon nanotubes membranes for desalination, Desalination, 367, pp. 134–144./ DOI: 10.1016/j.desal.2015.04.001.
  77. Kim, E.-S., Hwang, G., Gamal El-Din, M. & Liu, Y. (2012). Development of nanosilver and multi-walled carbon nanotubes thin-film nanocomposite membrane for enhanced water treatment, J. Membr. Sci., pp. 394-395, 37-48. DOI: 10.1016/j.memsci.2011.11.041.
  78. Kim, H.J., Choi, K., Baek, Y., Kim, D., Shim, J., Yoon, J. & Lee, J. (2014). High-Performance reverse osmosis CNT/polyamide nanocomposite membrane by controlled interfacial interactions, ACS Appl. Mater. Interf., 6, pp. 2819–2829. DOI: 10.1021/am405398f.
  79. Kochkodan, V. & Hilal, N. (2015). A comprehensive review on surface modified polymer membranes for biofouling mitigation, Desalination, 356, pp. 187–207. DOI: 10.1016/j.desal.2014.09.015.
  80. Lam, C.-W., James, J.T., McCluskey, R., Arepalli, S. & Hunter, R.L. (2008). A review of carbon nanotube toxicity and assessment of potential occupational and environmental health risks, Crit. Rev. Toxicol., 36, 3, pp. 189–217. DOI: 10.1080/10408440600570233.
  81. Lee, C. & Baik, S. (2010). Vertically-aligned carbon nano-tube membrane filters with superhydrophobicity and superoleophilicity, Carbon, 48, pp. 2192–2197. DOI: 10.1016/j.carbon.2010.02.020.
  82. Lee, B., Baek, Y., Lee, M., Jeong, D.H., Lee, H.H., Yoon, J. & Kim, Y.H. (2015). A carbon nanotube wall membrane for water treatment, Nat. Commun., 6, pp. 7109. DOI: 10.1038/ncomms8109.
  83. Lee, J., Jeong, S. & Liu, Z. (2016). Progress and challenges of carbon nanotube membrane in water treatment, Crit. Rev. Environ. Sci. Technol., 46, pp. 999–1046. DOI: 10.1080/10643389.2016.1191894.
  84. Lee, J.-G., Lee, E.-J., Jeong, S., Guo, J., An, A.K., Guo, H., Kim, J., Leiknes, T. & Ghaffour, N. (2017). Theoretical modeling and experimental validation of transport and separation properties of carbon nanotube electrospun membrane distillation, J. Membr. Sci., 526, pp. 395-408. DOI: 10.1016/j.memsci.2016.12.045
  85. Li, J., Chen, S., Sheng, G., Hu, J., Tan, X. & Wang, X., (2011). Effect of surfactants on Pb(II) adsorption from aqueous solutions using oxidized multiwall carbon nanotubes, Chem. Eng. J., 166, 2, pp. 551-558. DOI: 10.1016/j.cej.2010.11.018.
  86. Li, S., Liao, G., Liu, Z., Pan, Y., Wu, Q., Weng, Y., Zhang, X., Yang, Z. & Tsui O.K.C. (2014). Enhanced water flux in vertically aligned carbon nanotube arrays and polyethersulfone composite membranes, J. Mater. Chem. A., 2, pp. 12171–12176. DOI: 10.1039/C4TA02119C
  87. Li, S., He, M., Li, Z., Li, D. & Pan, Z. (2017). Removal of humic acid from aqueous solution by magnetic multi-walled carbon nanotubes decorated with calcium, J. Mole. Liquids, 230, pp. 520–528. DOI: 10.1016/j.molliq.2017.01.027
  88. Liu, L., Son, M., Chakraborty, S. & Bhattacharjee, C. (2013). Fabrication of ultra-thin polyelectrolyte/carbon nanotube membrane by spray-assisted layer-by- layer technique: characterization and its anti- protein fouling properties for water treatment, Desalin. Water Treat., 51, pp. 6194–6200. DOI: 10.1080/19443994.2013.780767.
  89. Liu, J., Wang, Y., Yu, Z., Cao, X., Tian, L., Sun, S. & Wu, P. (2017). A comprehensive analysis of blue water scarcity from the production, consumption and water transfer perspectives, Ecol. Indic., 72, pp. 870–880. DOI: 10.1016/j.ecolind.2016.09.021.
  90. Lu, C. & Chiu, H. (2006). Adsorption of zinc(II) from water with purified carbon nanotubes, Chem. Eng. Sci., 61, 4, pp. 1138–1145. DOI: 10.1016/j.ces.2005.08.007.
  91. Madhura, L., Kanchi, S., Myalowenkosi, I., Singh, S., Bisetty, K. & Inamuddin (2018). Membrane technology for water purification, Environmental Chemistry Letters, 16, pp. 343–365. DOI: 10.1007/s10311-017-0699-y.
  92. Majumder, M., Chopra, N., Andrews, R. & Hinds, B.J. (2005). Nanoscale hydrodynamics: enhanced flow in carbon nanotubes, Nature, 438, pp. 44. DOI: 10.1038/438044a.
  93. Manawi, Y., Kochkodan, V., Ali Hussein, M., M.A. Khaleel, M.A., Khraisheh M. & Hilal, N. (2016). Can carbon-based nanomaterials revolutionize membrane fabrication for water treatment and desalination? Desalination, 391, pp. 69–88. DOI: 10.1016/j.desal.2016.02.015.
  94. Manawi, Y.M., Ihsanullah, A. Samara Al-Ansari, T. & Atieh, M.A. (2018). A review of carbon nanomaterials’ synthesis via the chemical vapor deposition (CVD) method, Materials, 11, pp. 822. DOI: 10.3390/ma11050822.
  95. Mauter, M.S. & Elimelech, M. (2008). Environmental applications of carbon-based nanomaterials, Environ. Sci. Technol., 42, 16, pp. 5843–5859. DOI: 10.1021/es8006904.
  96. McCarthy B., Coleman J.N., Czerw R., Dalton A.B., Panhuis M.I.H., Maiti A., Drury A., Bernier P., Nagy J.B., Lahr B., Byrne H.J., Carroll D.L., Blau W.J. (2002). A microscopic and spectroscopic study of interactions between carbon nanotubes and a conjugated polymer, J. Phys. Chem. B 106, pp. 2210–2216. DOI: 10.1021/jp013745f.
  97. McGinnis R.L., Reimund K., Ren L. Xia M.R., Chowdhury X., Sun M., Abril J.D., Moon M.M., Merrick J., Park K.A., Stevens J.R., McCutcheon B.D., Freeman. (2018). Large-scale polymeric carbon nanotube membranes with sub–1.27-nm pores, Sci. Adv. 4, e1700938. DOI: 10.1126/sciadv.1700938.
  98. Mechrez G., Krepker M.A., Harel Y., Lellouche J.-P., Segal E. (2014). Biocatalytic carbon nanotube paper: A ‘one-pot’ route for fabrication of enzyme-immobilized membranes for organophosphate bioremediation, J. Mater. Chem. B, 2, pp. 915–922. DOI: 10.1039/C3TB21439G.
  99. Mehwish N, Kausar A., Siddiq M. (2015). High-performance polyvinylidene fluoride/poly (styrene – butadiene – styrene)/functionalized MWCNTs-SCN-Ag nanocomposite membranes, Iran. Polym. J. 24, pp. 549–559. DOI: 10.1007/s13726-015-0346-z.
  100. Morsi R.E., Alsabagh A.M., Nasr S.A., Zaki M.M. (2017). Multifunctional nanocomposites of chitosan, silver nanoparticles, copper nanoparticles and carbon nanotubes for water treatment: Antimicrobial characteristics. Int. J. Biol. Macromol., 97, pp. 264-269. DOI: 10.1016/j.ijbiomac.2017.01.032.
  101. Mubarak N.M., Alicia R.F., Abdullah E.C., Sahu J.N., Haslija A.B.A., Tan J. (2013). Statistical optimization and kinetic studies on removal of Zn2+ using functionalized carbon nanotubes and magnetic biochar, J. Environ. Chem. Eng., 1 (3), pp. 486-495. DOI: 10.1016/j.jece.2013.06.011.
  102. Nie C., Yang Y., Cheng C., Ma L., Deng J., Wang L., Zhao C. (2017). Bioinspired and biocompatible carbon nanotube-Ag nanohybrid coatings for robust antibacterial applications, Acta. Biomater., 51, pp. 479-494. DOI: 10.1016/j.actbio.2017.01.027.
  103. Ntim, S.A., Mitra, S. (2011). Removal of trace arsenic to meet drinking water standards using iron oxide coated multiwall carbon nanotubes, J. Chem. Eng. Data, 56, 2077-2083. DOI: https://doi.org/10.1016/j.actbio.2017.01.027.
  104. Ntim, S.A., Mitra, S. (2012). Adsorption of arsenic on multiwall carbon nanotube-zirconia nanohybrid for potential drinking water purification, J. Colloid Interface Sci., 375 (1), 154-159. DOI: 10.1016/j.jcis.2012.01.063.
  105. Park O.-K., Kim N.H., Lau K.-t., Lee J.H. (2010a). Effect of surface treatment with potassium persulfate on dispersion stability of multi-walled carbon nanotubes, Mater. Lett., 64, pp. 718–721. DOI: 10.1016/j.matlet.2009.12.048.
  106. Park J., Choi W., Cho J., Chun B.H., Kim S.H., Lee K.B., Bang J. (2010b). Carbon nanotube based nanocomposite desalination membranes from layer-by-layer assembly, Desalin. Water Treat., 15, pp. 76–83. DOI: 10.5004/dwt.2010.1670.
  107. Park J., Choi W., Kim S.H., Chun B.H., Bang J., Lee K.B., Park J., Choi W., Kim S.H., Chun B.H., Bang J., Lee K.B. (2010c). Enhancement of chlorine resistance in carbon nanotube based nanocomposite reverse osmosis membranes, Desalin. Water Treat., 15, pp. 198–204. DOI: 10.5004/dwt.2010.1686.
  108. Park S.-M., Jung J., Lee S., Baek Y., Yoon J., Seo D.K., et al. (2014). Fouling and rejection behavior of carbon nanotube membranes, Desalination, 343, pp. 180–186. DOI: 10.1016/j.desal.2013.10.005.
  109. Peng X., Jin J., Ericsson E.M., Ichinose I. (2007). General method for ultrathin free-standing films of nanofibrous composite materials, J. Am. Chem. Soc., 129, pp. 8625–8633. DOI: 10.1021/ja0718974.
  110. Pillay K., Cukrowska E.M., Coville N.J. (2009). Multi-walled carbon nanotubes as adsorbents for the removal of parts per billion levels of hexavalent chromium from aqueous solution, J. Hazard. Mater., 166 (2-3), pp. 1067-1075. DOI: 10.1016/j.jhazmat.2008.12.011.
  111. Qadir D., Mukhtar H., Keong L.K. (2017). Mixed matrix membranes for water purification applications, Sep. Purif Rev. 46, pp. 62–80. DOI: 10.1080/15422119.2016.1196460.
  112. Raghavendra S. Hebbar, Arun M. Isloor, Inamuddin, Asiri A.M. (2017). Carbon nanotube- and graphene-based advanced membrane materials for desalination, Environ Chem. Lett., 15, pp. 643–671. DOI: 10.1007/s10311-017-0653-z.
  113. Rashid M., Ralph S.F. (2017). Carbon nanotube membranes: synthesis, properties, and future filtration applications, Nanomaterials, 7 (5), 99-1-99-28. DOI: 10.3390/nano7050099.
  114. Ratto T.V., Holt J.K., Szmodis A.W. (2010). Membranes with embedded nanotubes for selective permeability, Patent Application No. 20100025330 (2010), https://pdfpiw.uspto.gov/.piw?Docid=07993524.
  115. Ren X., Chen C., Nagatsu M., Wang X. (2011). Carbon nanotubes as adsorbents in environmental pollution management: a review, Chem. Eng. J., 170 (2–3) pp. 395–410. DOI: 10.1016/j.cej.2010.08.045.
  116. Roy S., Jain V., Bajpai R., Ghosh P., Pente A.S., Singh B.P., Misra D.S. (2012). Formation of carbon nanotube bucky paper and feasibility study for filtration at the nano and molecular scale, J. Phys. Chem. C, 116, pp. 19025–19031. DOI: 10.1021/jp305677h.
  117. Rodrigues D.F., Elimelech M. (2010). Toxic Effects of Single-Walled Carbon Nanotubes in the Development of E. coli Biofilm, Environmental Science & Technology, 44, pp. 4583-4589. DOI: 10.1021/es1005785.
  118. Scoville C., Cole R., Hogg J., Farooque O., and A. Russell, (2019). CarbonNanotubes, https://courses.cs.washington.edu/courses/csep590a/08sp/projects/CarbonNanotubes.pdf(Accessed:11.25.2019
  119. Sears K., Dumée L., Schütz J., She M., Huynh C., Hawkins S., Duke M., Gray S. (2010). Recent developments in carbon nanotube membranes for water purification and gas separation, Materials 3, pp. 127. DOI: 10.3390/ma3010127.
  120. Seckler, D., R. Barker R., Amarasinghe U. (1999). Water scarcity in the twenty-first century, Int. J. Water Resour. Dev., 15, pp. 29–42. DOI: 10.1080/07900629948916.
  121. Selvan M.E., Keffer D., Cui S., Paddison S. (2010). Proton transport in water confined in carbon nanotubes: a reactive molecular dynamics study, Molecular Simulation, 36 (7-8), pp. 568-578. DOI: 10.1080/08927021003752887.
  122. Shah P., Murthy C.N. (2013). Studies on the porosity control of MWCNT/polysulfone composite membrane and its effect on metal removal, J. Membr. Sci., 437, pp. 90–98. DOI: 10.1016/j.memsci.2013.02.042.
  123. Shao D., Sheng G., Chen C., Wang X., Nagatsu M. (2010). Removal of polychlorinated biphenyls from aqueous solutions using beta-cyclodextrin grafted multiwalled carbon nanotubes, Chemosphere, 79 (7), pp. 679-685. DOI: 10.1016/j.chemosphere.2010.03.008.
  124. Shawky H.A., Chae S., Lin S., Wiesner M.R. (2011). Synthesis and characterization of a carbon nanotube/polymer nanocomposite membrane for water treatment, Desalination, 272, pp. 46–50. DOI: 10.1016/j.desal.2010.12.051.
  125. Shen J- Nan, Yu C- Chao., Hui min R., Cong jie Gao., Van Der Bruggen B. (2013). Preparation and characterization of thin-film nanocomposite membranes embedded with poly(methyl methacrylate) hydrophobic modified multiwalled carbon nanotubes by interfacial polymerization, J. Membr. Sci., 442, pp. 18–26. DOI: 10.1016/j.memsci.2013.04.018.
  126. Shen Y.-X., Saboe P.O., Sines I.T., Erbakan M., Kumar M. (2014). Biomimetic membranes: a review, J. Membr. Sci., 454, pp. 359–381. DOI: 10.1016/j.memsci.2013.12.019.
  127. Song X., Wang L., Tang C.Y., Wang Z., Gao C. (2015). Fabrication of carbon nanotubes incorporated double-skinned thin film nanocomposite membranes for enhanced separation performance and antifouling capability in forward osmosis process, Desalination, 369, pp. 1–9. DOI: 10.1016/j.desal.2015.04. 020.
  128. Stankovich S., Dikin D.A., Dommett G.H.B., Kohlhaas K.M., Zimney E.J., Stach E.A., Piner R.D., Nguyen S.T., Ruoff R.S. (2006). Graphene-based composite materials, Nature, 442, pp. 282–286. DOI: 10.1038/nature04969.
  129. Sweetman L.J., Nghiem L., Chironi I., Triani G., In Het Panhuis M., Ralph S.F. (2012). Synthesis, properties and water permeability of swnt buckypapers, J. Mater. Chem. A, 22, pp. 13800–13810. DOI: 10.1039/C2JM31382K.
  130. Sweetman L.J., Alcock, L.J., McArthur J.D., Stewart E.M., Triani G., Ralph S.F. (2013), Bacterial filtration using carbon nanotube/antibiotic buckypaper membranes, J. Nanomater, 2013, 1-11. DOI: 10.1155/2013/781212.
  131. Tian M., Wang R., Goh K, Liao Y., Fane A.G. (2015). Synthesis and characterization of high performance novel thin film nanocomposite PRO membranes with tiered nanofiber support reinforced by functionalized carbon nanotubes, J. Membr. Sci., 486, pp. 151–160. DOI: 10.1016.j.memsci.2015.03.054.
  132. Tiede K, Hassellov M., Breitbarth E., Chaudhry Q., Boxall A.B.A. (2009). Considerations for environmental fate and ecotoxicity testing to support environmental risk assessments for engineered nanoparticles, J. Chromatogr., A, 1216, pp. 503–509. DOI: 10.1016/j.chroma.2008.09.008.
  133. Tiraferri A., Vecitis C.D., Elimelech M. (2011). Covalent binding of single-walled carbon nanotubes to polyamide membranes for antimicrobial surface properties, ACS Appl. Mater. Interfaces, 3, pp. 2869–2877. DOI: 10.1021/am200536p.
  134. Tofighy, M.A., Mohammadi, T. (2011). Adsorption of divalent heavy metal ions from water using carbon nanotube sheets, J. Hazard. Mater., 185 (1), pp. 140-147. DOI: 10.1016/j.jhazmat.2010.09.008.
  135. Tunuguntla R.H., Henley R.Y., Yao Y.-C., Pham T.A., Wanunu M., Noy A. (2017). Enhanced water permeability and tunable ion selectivity in subnanometer carbon nanotube porins, Science, 357, pp. 792–796. DOI: 10.1126/science.aan2438.
  136. Upadhyayula V.K., Deng S., Mitchell M.C., Smith G.B. (2009). Application of carbon nanotube technology for removal of contaminants in drinking water: a review, Sci. Total Environ., 408 (1), pp. 1–13. DOI: 10.1016/j.scitotenv.2009.09.027.
  137. Usman F.M., Luan H.-Y., Wang, Y., Huang H., An A.K., Jalil K.R. (2017). Increased adsorption of aqueous zinc species by Ar/O2 plasma-treated carbon nanotubes immobilized in hollow-fiber ultrafiltration membrane, Chem. Eng. J., 325, pp. 239–248. DOI: 10.1016/j.cej.2017.05.020.
  138. Vatanpour V., Esmaeili M., Hossein M., Abadi D. (2014). Fouling reduction and retention increment of polyethersulfone nanofiltration membranes embedded by amine-functionalized multi-walled carbon nanotubes, J. Memb. Sci., 466, pp. 70–81. DOI: 10.1016/j.memsci.2014.04.031.
  139. Vatanpour V., Zoqi N. (2017). Surface modification of commercial seawater reverse osmosis membranes by grafting of hydrophilic monomer blended with carboxylated multiwalled carbon nanotubes, Appl. Surf. Sci., 396, pp. 1478–1489. DOI: 10.1016/j.apsusc.2016.11.195.
  140. Vuković G.D., Marinković A.D., Čolić M., Ristić M.Đ., Aleksić R., Perić-Grujić A.A.,Uskoković P.S. (2010). Removal of cadmium from aqueous solutions by oxidized and ethylenediamine-functionalized multi-walled carbon nanotubes, Chem. Eng. J., 157 (1), pp. 238–248. DOI: 10.1016/j.cej.2009.11.026.
  141. Wang X., Li Q., Xie J., Jin Z., Wang J., Li Y., Jiang K., Fan S. (2009). Fabrication of ultralong and electrically uniform single-walled carbon nanotubes on clean substrates, Nano Lett.,9, pp. 3137–3141. DOI: 10.1021/nl901260b
  142. Wang H., Yan N., Li Y., Zhou X., Chen J., Yu B., Gong M., Chen Q. (2012). Fe nanoparticle-functionalized multi-walled carbon nanotubes: one-pot synthesis and their applications in magnetic removal of heavy metal ions, J. Mater. Chem., 22 (18), pp. 9230-9236. DOI: 10.1039/C2JM16584H.
  143. Wang H., Dong Z., Na C. (2013). Hierarchical carbon nanotube membrane-supported gold nanoparticles for rapid catalytic reduction of p-nitrophenol, ACS Sustain. Chem. Eng., 1 (7), pp. 746–752. DOI: 10.1021/sc400048m.
  144. Wang S., Liang S., Liang P., Zhang X., Sun J., Wu S., Huang X. (2015a). In-situ combined dual-layer CNT/PVDF membrane for electrically-enhanced fouling resistance, J. Membr. Sci., 491, pp. 37–44. DOI: 10.1016/j.memsci.2015.05.014.
  145. Wang Y., Zhu J., Huang H., Cho H.-H. (2015b). Carbon nanotube composite membranes for microfiltration of pharmaceuticals and personal care products: capabilities and potential mechanisms, J. Membr. Sci., 479, pp. 165–174. DOI: 10.1016/j.memsci.2015.01.034.
  146. Wang Y., Ma J., Zhu J., Ye N., Zhang X., Huang H. (2016a). Multi-walled carbon nanotubes with selected properties for dynamic filtration of pharmaceuticals and personal care products, Water Res., 92, pp. 104–112. DOI: 10.1016/j.watres.2016.01.038.
  147. Wang J., Zhang P., Liang B., Liu Y., Xu T., Wang L., Cao B., Pan K. (2016b). Graphene oxide as an effective barrier on a porous nanofibrous membrane for water treatment, ACS Appl. Mater. Interfaces, 8, pp. 6211–6218. DOI: 10.1021/acsami.5b12723.
  148. Wang, Y., Huang, H.,Wei, X. (2018). Influence of wastewater precoagulation on adsorptive filtration of pharmaceutical and personal care products by carbon nanotube membranes, Chem. Eng. J., 333, pp. 66–75. DOI: 10.1016/j.cej.2017.09.149.
  149. WHO/UNICEF Joint Monitoring Programme. Progress on household drinking water, sanitation, and hygiene 2000-2017. Geneva, Switzerland; New York, NY: WHO; UNICEF, 2019, https://washdata.org
  150. Wu H., Tang B., Wu P. (2010a). MWNTs/Polyester thin film nanocomposite membrane: an approach to overcome the trade-off effect between permeability and selectivity, J. Phys. Chem. C, 114, pp. 16395–16400. DOI: 10.1021/jp107280m.
  151. Wu H., Tang B., Wu P. (2010b). Novel ultrafiltration membranes prepared from a multiwalled carbon nanotubes/polymer composite, J. Membr. Sci., 362, pp. 374–383. DOI: 10.1016/j.memsci.2010.06.064.
  152. www.fizyka.iss.com.pl/nanorurki/01nanorurki_.html (Accessed: 13.03.2021)
  153. Xiu Z.-M., Zhang Q.-B., Puppala H.L., Colvin V.L., Alvarez, P.J.J. (2012). Negligible particle-specific antibacterial activity of silver nanoparticles, Nano Lett., 12, pp. 4271–4275. DOI: 10.1021/nl301934w.
  154. Xue S.-M., Xu Z.-L, Tang Y.-J., Ji C.-H. (2016). Polypiperazine-amide nanofiltration membrane modified by different functionalized multiwalled carbon nanotubes (MWCNTs), ACS Appl. Mater. Interfaces, 8, pp. 19135–19144. DOI: 10.1021/acsami.6b05545.
  155. Yan X.M., Shi B.Y., Lu J.J., Feng C.H., Wang D.S., Tang H.X. (2008). Adsorption and desorption of atrazine on carbon nanotubes, J. Colloi. Interf. Sci., 321 (1), pp. 30-38. DOI: 10.1016/j.jcis.2008.01.047.
  156. Yang H.Y., Han Z.J., Yu S.F., Pey K.L., Ostrikov K., Karnik R. (2013a). Carbon nanotube membranes with ultrahigh specific adsorption capacity for water desalination and purification, Nat. Commun., 4, pp. 2220. DOI: 10.1038/ncomms3220.
  157. Yang, X., Lee, J., Yuan, L., Chae, S.-R., Peterson, V.K., Minett, A.I., Yin, Y., Harris, A.T. (2013b). Removal of natural organic matter in water using functionalised carbon nanotube buckypaper, Carbon, 59, pp. 160–166. DOI: 10.1016/j.carbon.2013.03.005.
  158. Yin J., Deng B. (2015). Polymer-matrix nanocomposite membranes for water treatment, J.Membr. Sci., 479, pp. 256–275. DOI: 10.1016/j.memsci.2014.11.019.
  159. Zarrabi H., Ehsan M., Vatanpour V., Shockravi A., Safarpour M. (2016). Improvement in desalination performance of thin film nanocomposite nanofiltration membrane using amine-functionalized multiwalled carbon nanotube, Desalination, 394, pp. 83–90. DOI: 10.1016/j.desal.2016.05.002.
  160. Zhang L., Chen H. (2011). Preparation of high-flux thin film nanocomposite reverse osmosis membranes by incorporating functionalized multi-walled carbon nanotubes, Desalin. Water Treat., 34, pp. 19–24. DOI: 10.5004/dwt.2011.2801.
  161. Zhang J., Xu Z., Shan M., Zhou B., Li Y., Li B., Niu J., Qian X. (2013). Synergetic effects of oxidized carbon nanotubes and graphene oxide on fouling control and anti-fouling mechanism of polyvinylidene fluoride ultrafiltration membranes, J. Membr. Sci., 448, pp. 81–92. DOI: 10.1016/j.memsci.2013.07.064.
  162. Zhang Y., Wu B., Xu H., Liu H., Wang M., He Y., Pan B. (2016). Nanomaterials-enabled water and wastewater treatment, NanoImpact, 3-4, pp. 22–39. DOI: 10.1016/j.impact.2016.09.004.
  163. Zhao Y.L., Stoddart J.F. (2009). Noncovalent functionalization of single-walled carbon nanotubes, Acc. Chem. Res., 42, pp. 1161–1171. DOI: 10.1021/ar900056z.
  164. Zhao C., Xu X., Chen J., Yang F. (2013a). Effect of graphene oxide concentration on the morphologies and antifouling properties of PVDF ultrafiltration membranes, J. Environ. Chem. Eng., 1, pp. 349–354. DOI: 10.1016/j.jece.2013.05.014.
  165. Zhao H., Wu L., Zhou Z., Zhang L., Chen H. (2013b). Improving the antifouling property of polysulfone ultrafiltration membrane by incorporation of isocyanate-treated Graphene oxide, Phys. Chem. Chem. Phys., 15, pp. 9084–9092. DOI: 10.1039/c3cp50955a.
  166. Zhao H., Qiu S., Wu L., Zhang L., Chen H., Gao C. (2014). Improving the performance of polyamide reverse osmosis membrane by incorporation of modified multi-walled carbon nanotubes, J. Membr. Sci., 450, pp. 249–256. DOI: 10.1016/j.memsci.2013.09.014.
  167. Zheng J., Li M., Yu K., Hu J., Zhang X., Wang L. (2017). Sulfonated multiwall carbon nanotubes assisted thin-film nanocomposite membrane with enhanced water flux and anti-fouling property, J. Membr. Sci., 524, pp. 344–353. DOI: 10.1016/j.memsci.2016.11.032
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Authors and Affiliations

Michał Bodzek
1
ORCID: ORCID
Krystyna Konieczny
2
ORCID: ORCID
Anna Kwiecińska-Mydlak
3
ORCID: ORCID

  1. Institute of Environmental Engineering Polish Academy of Sciences, Poland
  2. Silesian University of Technology, Faculty of Energy and Environmental Engineering, Poland
  3. Institute for Chemical Processing of Coal, Poland
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Abstract

The article presents research results of the introduction of powdery activated carbon to the existing technological system of the groundwater treatment stations in a laboratory, pilot plant and technical scale. The aim of the research was to reduce the content of organic compounds found in the treated water, which create toxic organic chlorine compounds (THM) after disinfection with chlorine. Nine types of powdery active carbons were tested in laboratory scale. The top two were selected for further study. Pilot plant scale research was carried out for the filter model using CWZ-30 and Norit Sa Super carbon. Reduction of the organic matter in relation to the existing content in the treated water reached about 30%. Research in technical scale using CWZ-30 carbon showed a lesser efficiency with respect to laboratory and pilot-plant scale studies. The organic matter decreased by 15%. Since filtration is the last process before the individual disinfection, an alternative solution is proposed, i.e. the second stage of filtration with a granular activated carbon bed, operating in combined sorption and biodegradation processes. The results of tests carried out in pilot scale were fully satisfactory with the effectiveness of 70–100%.

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Authors and Affiliations

Jadwiga Kaleta
Małgorzata Kida
Piotr Koszelnik
Dorota Papciak
Alicja Puszkarewicz
Barbara Tchórzewska-Cieślak
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Abstract

The removal of benzene (B) and toluene (T) from aqueous solution by multi walled, single walled, and hybrid carbon nanotubes (MWCNTs, SWCNTs, and HCNTs) was evaluated for a nanomaterial dose of 1 g/l, concentration of 10-100 mg/l, and pH 7. The equilibrium amount removed by SWCNTs (B: 9.98 mg/g and T: 9.96 mg/g) was higher than for MWCNTs and HCNTs. Toluene has a higher adsorption tendency on CNTs than benzene, which is related to the increasing water solubility and the decreasing molecular weight of the compounds. The SWCNTs performed better for B and T sorption than the MWCNTs and HCNTs. Isotherms study based on isofit program indicate that the Generalized Langmuir-Freundlich (GLF) isotherm expression provides the best fit for benzene sorption, and that Brunauer-Emmett-Teller (BET) isotherm is the best fit for toluene adsorption by SWCNT. SWCNTs are efficient B and T adsorbents and possess good potential applications to water and wastewater treatment and maintain water of high quality that could be used for cleaning up environmental pollution.

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Authors and Affiliations

Bijan Bina
Mohammad Mehdi Amin
Alimorad Rashidi
Hamidreza Pourzamani
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Abstract

Binary vapour-liquid equilibrium of thymoquinone and carbon dioxide at the isothermal conditions was carried out at temperature 323.15 K and pressures from 6 to 10 MPa. The experimental data were fitted to the Soave-Redlich-Kwong equation of state. Results could be used for selection of process parameters in separation of volatiles from raw oil or for evaluation of existing separation technologies.

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Authors and Affiliations

Karina Gurgenova
Rafał Bogeł-Łukasik
Paweł Wawrzyniak
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Abstract

Labile fractions of organic matter can rapidly respond to changes in soil and they have been suggested as sensitive indicators of soil organic matter. Two labile fractions of organic carbon in the soils amended with fresh municipal sewage sludge in two rates (equivalent of 60 kg P ha-1 and 120 kg P ha-1) were studied. Soils under studies were overgrown with Salix in Germany, Estonia and Poland. In Polish soils application of sewage sludge increased the content of both labile organic carbon fractions (KMnO4-C and HWC) for a period of one year. Estonian soils were stable and no distinct changes in labile organic carbon fractions occurred.

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Authors and Affiliations

Barbara Kalisz
Andrzej Klasa
Andrzej Lachacz
Roman Głażewski
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Abstract

Twenty-eight two-, three-, four-, and five-component amine mixtures have been evaluated as possible activators of CO2 absorption into aqueous carbonate/bicarbonate solutions. Measurements were per- formed using a pressure autoclave with a sparger at conditions close to industrial ones. On the basis of these results, a formula for a new, more efficient amine activator named INS13 was developed. The activator was tested both in a pilot plant and on an industrial scale in an ammonia plant producing 300 tons/day of ammonia. Activator INS13 was applied in a number of ammonia plants in Poland and abroad.

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Authors and Affiliations

Grzegorz Bińczak
Ryszard Pohorecki
Władysław Moniuk
Cezary Możeński
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Abstract

In this study, the electrospray deposition (ESD) method was used to deposit carbon nanotubes (CNT) onto the surfaces of carbon fibers (CF) in order to produce hybrid carbon fiber-carbon nanotubes (CF-CNT) which is rarely reported in the past. Extreme high-resolution field emission scanning electron microscopy (XHR-FESEM), high-resolution transmission electron microscopy (HRTEM) and x-ray photoelectron spectroscopy (XPS) were used to analyse the hybrid carbon fiber-carbon nanotube (CF-CNT). The results demonstrated that CNT was successfully and homogenously distributed on the CF surface. Hybrid CF-CNT was then prepared and compared with CF without CNT deposition in terms of their tensile properties. Statistically, the tensile strength and the tensile modulus of the hybrid CF-CNT were increased by up to 3% and 25%, respectively, as compared to the CF without CNT deposition. The results indicated that the ESD method did not cause any reduction of tensile properties of hybrid CF-CNT. Based on this finding, it can be prominently identified some new and significant information of interest to researchers and industrialists working on CF based products.
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Authors and Affiliations

Muhammad Razlan Zakaria
1 2
ORCID: ORCID
Hazizan Md Akil
3
ORCID: ORCID
Mohd Firdaus Omar
1 2
ORCID: ORCID
Mohd Mustafa Al Bakri Abdullah
1 2
ORCID: ORCID
Shayfull Zamree Abd Rahim
2
ORCID: ORCID
M. Nabiałek
4
ORCID: ORCID
J.J. Wysłocki
4
ORCID: ORCID

  1. Universiti Malaysia Perlis, Faculty of Chemical Engineering Technology, Kompleks Pengajian Jejawi 2, 02600 Arau, Perlis, Malaysia
  2. Universiti Malaysia Perlis, Geopolymer & Green Technology, Centre of Excellent (CEGeoGTech) Perlis, Malaysia
  3. Universiti Sains Malaysia, School of Materials and Mineral Resources Engineering, Engineering Campus, 14300 Nibong Tebal, Pulau Pinang, Malaysia
  4. Czestochowa University of Technology, Faculty of Production Engineering and Materials Technology, Department of Physics 42-201 Czestochowa, Poland
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Abstract

“Soon we will be able to fit the contents of the Encyclopedia Britannica on a head of a pin,” the famous physicist Richard Feynman argued back in the 1960s. Perhaps even he would be amazed at the possibilities now offered by carbon nanotubes, several hundred thousand times tinier than a pin. Their amazing properties have been exploited in an integrated circuit developed at the Karlsruhe Institut für Technologie.

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Authors and Affiliations

Karolina Słowik
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Abstract

The process of carbon dioxide removal from monoethanolamine (MEA) - water solution was investigated on Poly Di Methyl Siloxane (PDMS) hydrophobic tubular membrane with a ceramic support. The effects of feed temperature, liquid flow rate and MEA concentration on CO2 mass transfer and selectivity were examined and found to be with a reasonable deviation (±25%) with predictions based on the multilayer film model. The membrane resistance was evaluated in separate experiments. The measured CO2 mass fluxes (0.17-0.45 kg/(m2h)) were found to be independent of the MEA concentration in the feed.

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Authors and Affiliations

Roman Krupiczka
Adam Rotkegel
Zenon Ziobrowski
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Abstract

Balance, thermodynamic and mainly kinetic approaches using methods of process engineering enable to determine conditions under which iron technology can actually work in limiting technological states, at the lowest reachable fuel consumption (reducing factor) and the highest reachable productivity accordingly. Kinetic simulation can be also used for variant prognostic calculations. The paper deals with thermodynamics and kinetics of iron making process. It presents a kinetic model of iron oxide reduction in a low temperature area. In the experimental part it deals with testing of iron ore feedstock properties. The theoretical and practical limits determined by heat conditions, feedstock reducibility and kinetics of processes are calculated.

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Authors and Affiliations

Pavlína Pustějovská
Simona Jursová
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Abstract

Measurements of the absorption rate of carbon dioxide into aqueous solutions of N-methyldiethanoloamine (MDEA) and 2-ethylaminoethanol (EAE) have been carried out. On this basis a mathematical model of the performance of an absorption column operated with aqueous solution of a blend of the above amines at elevated temperatures and pressures have been proposed. The results of simulations obtained by means of this model are described. The work is a part of a wider program, aimed at the development of a new process.

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Authors and Affiliations

Ryszard Pohorecki
Władysław Moniuk
Piotr Machniewski
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Abstract

It was found that the addition of carbon fibers (CFs) does not affect the crosslinking process in the microwave radiation (800 W, 2.45

GHz) of the BioCo2 binder, which is a water solution of poly(acrylic acid) and dextrin (PAA/D). It has influence on BioCo2 thermal

properties. The CFs addition improves the thermostability of a binder and leads to the reduction of gas products quantity generated in the

temperature range of 300-1100°C (TG-DTG, Py-GC/MS). Moreover, it causes the emission of harmful decomposition products such as

benzene, toluene, xylene and styrene to be registered in a higher temperatures (above 700°C). BioCo2 binder without CFs addition is

characterized by the emission of these substances in the lower temperature range. This indicates the positive effect of carbon fibers

presence on the amount of released harmful products.

The selected technological tests (permeability, friability, bending strength, tensile strength) have shown that the moulding sand with the

0.3 parts by weight carbon fibers addition displays the worst properties. The addition of 0.1 parts by weight of CFs is sufficient to obtain a

beneficial effect on the analyzed moulding sands properties. The reduction of harmful substances at the higher temperatures can also be

observed.

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Authors and Affiliations

S. Żymankowska-Kumon
B. Grabowska
A. Bobrowski
D. Drożyński
K. Kaczmarska
S. Cukrowicz
B. Gawluk
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Abstract

Extremely intense development of civilization requires from foundry casting technologies very high quality and not expensive castings. In

the foundries, there are many treatments that allow increasing of the final properties of produced castings such as refining, modification,

heat treatment, etc. One of the methods of increasing the quality of the casting by removing inclusions from the liquid alloy is filtration.

The use of ceramic-carbon foam filters in filtration process is still analysed phenomenon that allows improving the final properties of

castings. A modern method of research, testing and synthesis of innovative chemical compositions allows improving the properties of such

filters. In the paper the evaluation of application properties of developed ceramic-carbon bonded foam filters is presented. The quality of

the foam filters is evaluated by Computer Tomography and foundry trials in pouring of liquid metal in test molds. Additionally computer

simulations were made to visualize the flow characteristics in the foam filter. The analysed filters are the result of the research work of

Foundry Research Institute and the Institute of Ceramics and Building Materials, Refractory Materials Department in Gliwice.

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Authors and Affiliations

A. Karwiński
P. Wieliczko
M. Małysza
A. Gil
B. Lipowska
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Abstract

A number of micromechanical investigations have been performed to predict behaviour of composite interfaces, showing that the detailed behaviour of the material at these interfaces frequently dominates the behaviour of the composite as a whole. The interfacial interaction is an extremely complex process due to continuous evolution of interfacial zones during deformation and this is particularly true for carbon nanotubes since the interfacial interaction is confined to the discrete molecular level. The atomic strain concept based upon Voronoi tessellation allows analyzing the molecular structure atom by atom, which may give a unique insight into deformation phenomena operative at molecular level such as interface behaviour in nanocomposites.

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Authors and Affiliations

R. Pyrz
B. Bochenek
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Abstract

Aiming to create more sustainable cities it is necessary to understand and manage different ecological factors which influence human health. One of such factors is black carbon (BC) in atmosphere, which currently is not commonly monitored by environmental monitoring systems. The aim of this research was to estimate by indirect approach the relation between eBC (equivalent of black carbon) concentration and other air pollutants in order to define approximate level of eBC in more efficient approach. The study was conducted in Wrocław (Poland) in October 2021, and combined data on eBC concentration (measured by microaethalometer), air quality (from national environmental monitoring system) and traffic (from municipal traffic management system). Quantile regression was used to assess the relationship between the concentrations of pollutants. The obtained results show that for rise 1 mg∙m<sup>–3</sup> of carbon monoxide, eBC concentration rise between 4.2 and 8.0 μg∙m<sup>–3</sup>, depending on the period of a day. Precision of eBC concentration evaluation is influenced by sun light which results in higher precision of defining a scaling factor for night hours. Outcomes of this study constitute an added value to understanding of interconnections between different factors describing environmental conditions in cities and might be helpful for more effective environmental assessment of human habitats.



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Authors and Affiliations

Joanna A. Kamińska
1
ORCID: ORCID
Jan K. Kazak
2
ORCID: ORCID

  1. Wrocław University of Environmental and Life Sciences, Department of Applied Mathematics, Wrocław, Poland
  2. Wrocław University of Environmental and Life Sciences, Institute of Spatial Management, Grunwaldzka 53, 50-357, Wrocław, Poland
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Abstract

Carbonic anhydrase is an important enzyme that can play a significant role in the processes of lowering carbon dioxide concentration in the atmosphere. The aim of the work was to investigate the extracellular carbonic anhydrase (CA) production by the bacteria Pseudomonas fragi. In the research, we focused on the evaluation of the phase of bacterial growth correlated with carbonic anhydrase production and on the evaluation of induction of CA production by calcium carbonate concentration in the nutrient medium. Presented data indicated that calcium carbonate can serve as the only carbon source for Pseudomonas fragi, inducing carbonic anhydrase secretion to culture broth. The enzyme was produced mainly in the adaptation growth phase reaching the maximal activity at the end of this phase or at the beginning of the growth phase. The maximal enzyme activity detected in all batches was at a similar level. The enzyme activity was constant but lower in the exponential phase growth. Therefore, the enzyme production is not growth-dependent, but it is correlated with bacteria adaptation to cultivation conditions.
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Authors and Affiliations

Andrzej Tietz
1
Małgorzata M. Jaworska
1
ORCID: ORCID

  1. Warsaw University of Technology, Faulty of Chemical and Process Engineering, ul. Warynskiego 1, 00-645 Warsaw, Poland
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Abstract

In this study, the synthesis of lithium carbonate (Li2CO3) powder was conducted by a carbonation process using carbon dioxide gas (CO2) from waste acidic sludge based on sulfuric acid (H2SO4) containing around 2 wt.% lithium content. Lithium sulfate (Li2SO4) powder as a raw material was reacted with CO2 gas using a thermogravimetric apparatus to measure carbonation conditions such as temperature, time and CO2 content. It was noted that carbonation occurred at a temperature range of 800℃ to 900℃ within 2 hours. To prevent further oxidation during carbonation, calcium sulfate (CaO4S) was first introduced to mixing gases with CO2 and Ar and then led to meet in the chamber. The lithium carbonate obtained was examined by inductively coupled plasma–mass spectroscopy (ICP-MS), X-ray diffraction (XRD) and scanning electron microscopy (SEM) and it was found that of lithium carbonate with a purity above 99% was recovered.

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Authors and Affiliations

Dong Hyeon Choi
Jei Pil Wang
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Abstract

Phytolith-occluded carbon (PhytOC) is highly stable, and constitutes an important source of long-term C storage in agrosystems. This stored carbon is resistant to the processes of oxidation of carbon compounds. In our research phytolith content in barley (Estonia) and oat (Poland) grain and straw was assessed at field trials, with Si as a liquid immune stimulant OPTYSIL and compost fertilisation. We showed that cereals can produce relatively high amounts of phytoliths. PhytOC plays a key role in carbon sequestration, particularly for poor, sandy Polish and Estonian soils. The phytolith content was always higher in straw than in grain regardless of the type of cereals. The phytolith content in oat grains varied from 18.46 to 21.28 mg∙g−1 DM, and in straw 27.89–38.97 mg∙g−1 DM. The phytolith content in barley grain ranged from 17.24 to 19.86 mg∙g−1 DM, and in straw from 22.06 to 49.08 mg∙g−1 DM. Our results suggest that oat ecosystems can absorb from 14.94 to 41.73 kg e-CO2∙ha−1 and barley absorb from 0.32 to 1.60 kg e-CO2∙ha−1. The accumulation rate of PhytOC can be increased 3-fold in Polish conditions through foliar application of silicon, and 5-fold in Estonian conditions. In parallel, the compost fertilisation increased the phytolith content in cereals.
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Authors and Affiliations

Beata Rutkowska
1
ORCID: ORCID
Peter Schröder
2
ORCID: ORCID
Michel Mench
3 4
ORCID: ORCID
Francois Rineau
5
ORCID: ORCID
Witold Szulc
6
ORCID: ORCID
Wiesław Szulc
1
ORCID: ORCID
Jarosław Pobereżny
7
ORCID: ORCID
Kristjan Tiideberg
8
ORCID: ORCID
Tomasz Niedziński
1
ORCID: ORCID
Evelin Loit
8
ORCID: ORCID

  1. Warsaw University of Life Sciences – SGGW, Institute of Agriculture, Nowoursynowska St, 166, 02-787 Warsaw, Poland
  2. Helmholtz Center for Environmental Health, German Research Center for Environmental Health, Research Unit Environmental Simulation, Ingolstädter Landstraße 1, D-85764 Neuherberg, Munich, Germany
  3. University of Bordeaux, Amphithéâtre 3 à 12, 33000, Bordeaux, France
  4. INRAE – National Research Institute for Agriculture, Food and the Environment, 147 rue de l’Université 75338, Paris, France
  5. Hasselt University, Martelarenlaan 42, 3500, Hasselt, Belgium
  6. Fire University, Słowackiego St, 52/54, 01-629 Warsaw, Poland
  7. University of Science and Technology, Kaliskiego Ave., 7, 85-796 Bydgoszcz, Poland
  8. Estonian University of Life Sciences, Institute of Agricultural and Environmental Sciences, Fr. R. Kreutzwaldi 1, 51006, Tartu, Estonia
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Abstract

Samples for the study were collected from, known from the literature, outcrop profiles in Zarzecze, Radymno, Dybawka, Tarnawce and Pikulice-Nehrybka, situated at the Carpathian border, in the vicinity of the Przemyśl town, close to the San River valley (SE Poland). They represent the Vistulian loess-palaeosol sequences. Carbonates occur mainly in the loesses representing OIS 2 and 3. Pollen analysis, carried out for two profiles (Tarnawce, Radymno), throws light on palaeoecological conditions of loess cover formation and transformation.Isotopic analysis of authigenic carbonates was carried out on carbonate cemented bodies dispersed throughout the loess in forms of nodule, rhizolith and rhizocretion and on bioclasts, mainly snail shells, ostracod valves, and sparse globules (probably the internal shells of the naked snails).In the successions studied, the upper Vistulian loess deposited in environment with poor vegetation, contains rhizo- liths and rhizocretions mainly, while in the middle and lower Vistulian loess with well developed soils, gley horizons, and intercalations of subaqueous sediments, remains of snail shells and ostracod valves prevail. The two main forms of carbonates differ markedly in isotopic composition from one another. These differences seem to be more important than those between samples of one form of carbonates along particular sections. That is the result of numerous factors affecting the fractionation of carbon and, in particular, oxygen stable isotopes in the environment of precipitation of authigenic calcite. The isotopic composition of carbonates cementing sediments is controlled mainly by biominerali- zation of organic matter and local climatic parameters which were rather slightly differentiated during the formation of the studied sediments. The d13C values for bioclasts vary in a broader range than for calcitic cements. Usually the snail shell carbonate is more enriched with heavier carbon isotope than that from ostracod valves, resulting from the isotopic equilibrium with precipitation and with surface waters, respectively. Basing on our study we can conclude that fluctuations of isotope composition of authigenic carbonates make it hard to apply as a paleoclimatic indicator. However, the general trend of d18O variation in analysed carbonate fractions from leoss-palaeosol sequences displays some connections with climatic fluctuations.

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Authors and Affiliations

Bożena Łącka
Maria Łanczont
Maryna Komar
Teresa Madeyska
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Abstract

A sediment core (LS-1) collected from Long Lake in King George Island, South Shetland Islands (West Antarctica) was analyzed for a variety of textural, geochemical, isotopic and paleontological properties together with 14C age dates. These data combined with published records of other studies provide a detailed history of local/regional postglacial paleoproductivity variation with respect to terrestrial paleoclimate change. The lithologic contrast of a lower diamicton and an upper fine-grained sediment demonstrates glacial recession and subsequent lake formation. The upper fine-grained deposit, intercalated by mid-Holocene tephra-fallout followed by a tephra gravity flow, was formed in a lacustrine environment. Low total organic carbon (TOC) and biogenic silica (Sibio) contents with high C/N ratios characterize the diamicton, whereas an increase of TOC and Sibio contents characterize the postglacial lacustrine fine-grained sediments, which are dated at c. 4000 yrBP. More notable are the distinct TOC maxima, which may imply enhanced primary productivity during warm periods. Changes in Sibio content and δ13C values, which support the increasing paleoproductivity, are in sympathy with these organic matter variations. The uniform and low TOC contents that are decoupled by Sibio contents are attributed to the tephra gravity flows during the evolution of the lake rather than a reduced paleoproductivity. A very recent TOC maximum is also characterized by high Sibio content and δ13C values, clearly indicating increased paleoproductivity consequent upon gradual warming across King George Island . Comparable with changes in sediment geochemistry, the occurrence and abundance of several diatom species corroborate the paleoproductivity variations together with the lithologic development. However, the paleoclimatic signature in local terrestrial lake environment during the postglacial period (for example the Long Lake) seems to be less distinct, as compared to the marine environment.

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Authors and Affiliations

Ho-Il Yoon
Boo-Keun Khim
Kyung Lee
Yu-Hyeon Park
Kyu-Cheul Yoo
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Abstract

The reports of Intergovernmental Panel for Climate Change indicate that the growing emission of greenhouse gases, produced from the combustion of fossil fuels, mainly carbon dioxide, leads to negative climate changes. Therefore, the methods of mitigating the greenhouse gases emission to the atmosphere, especially of carbon dioxide, are being sought. Numerous studies are focused on so-called geological sequestration, i.e. injecting carbon dioxide to appropriate geological strata or ocean waters. One of the methods, which are not fully utilized, is the application of appropriate techniques in agriculture. The plant production in agriculture is based on the absorption of carbon dioxide in the photosynthesis process. Increasing the plant production directly leads to the absorption of carbon dioxide. Therefore, investigation of carbon dioxide absorption by particular crops is a key issue. In Poland, ca. 7.6 mln ha of cereals is cultivated, including: rye, wheat, triticale, oat and barley. These plants absorb approximately 23.8 mln t C annually, including 9.8 mln t C/yr in grains, 9.4 mln t C/yr in straw and 4.7 mln t C/yr in roots. The China, these cereals are cultivated on the area over 24 mln ha and absorb 98.9 mln t C/yr, including 55 mln tC/yr in grains, 36 in straw, and 7.9 mln t C/yr in roots. The second direction for mitigating the carbon dioxide emission into the atmosphere involves substituting fossil fuels with renewable energy sources to deliver primary energy. Cultivation of winter cereals as cover crops may lead to the enhancement of carbon dioxide removal from the atmosphere in the course of their growth. Moreover, the produced biomass can be used for energy generation.

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Authors and Affiliations

Lucjan Pawłowski
Małgorzata Pawłowska
Wojciech Cel
Lei Wang
Chong Li
Tingting Mei
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Abstract

The paper presents the application of similarity theory to investigations of transient heat transfer in materials with complex structure. It describes the theoretical-experimental method for identification and design of the structure of two-component composite walls based on the research of the thermal diffusivity for the composite and its matrix separately. The thermal diffusivity was measured by means of the modified flash method. The method was tested on two samples of double-layer ‘epoxy resin – polyamide’. All the investigated samples had the same diameter of 12 mm and thickness ranging from 1.39–2.60 mm and their equivalent value of thermal diffusivity ranging from (1.21–1.98)×10-7m2/s. Testing the method and research on carbon/epoxy composites was carried out at temperatures close to room temperature.
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Authors and Affiliations

Janusz Terpiłowski
Bartosz Gawron
Grzegorz Woroniak

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