Search results

Filters

  • Journals
  • Authors
  • Keywords
  • Data
  • Type

Search results

Number of results: 632
items per page: 25 50 75
Sort by:
Download PDF Download RIS Download Bibtex

Abstract

Cyanobacterials (Cyanophyta) belong to phytoplancton. In normal stale concentration of cyanobacterial cells in water rangs between a few hundreds to a few thousands in I drn' of water but while blooming may be increased even to one million in I dm3. At this time water has characteristic color, depending on dominated species. Also characteristic smell is the results of the presence ofcyanobacterial and phytoplankton cells producing odour substances. The cyanobacterial blooms are very important hygienic problem for both human and animal health. While blooming they form foams and head coating on water surface. Also cyanobacterial toxins are huge problem. Cyanobacteria may produce acute toxins such as hepatotoxic peptides (microcystins, nodularins and cylindrospermopsin) and neurotoxic alkaloids (anatoxin-a, anatoxin-a(s), homoanatoxin and aphanotoxins). Cyanobacterial toxins are very dangerous substances which can intoxicate hepatocytes and the nervous system in humans and animals. In this situation it is very important to remove them effectively in water pretreatment processes. In the present paper have been presented for the first time in Poland data on removing cyanobacterial toxins from water in pretreatment process with application of chlorine dioxide and ozone on the example of Sulejów - Łódź water pipe system. In period I 998-200 I the effectiveness rnicrocystin-LR removal ranged between 74--92% while for other izoforms they were between 45-94%.
Go to article

Authors and Affiliations

Andrzej K.M. Kabziński
Helena Grabowska
Jerzy Cyran
Renata Juszczak
Józef Dziegieć
Alicja Zawadzka
Dominik Szczukocki
Konrad Szczytowski
Download PDF Download RIS Download Bibtex

Abstract

This paper identifies the adverse events occurring during the execution of water supply and sewerage systems construction. The basis for this paper is research conducted in 2010-2014 on the construction sites of water supply and sewerage systems located in the provinces of Lower Silesia and Opole. The research consisted of direct observations of construction sites and review of construction documentation. It showed that work stoppages on the examined construction sites were frequent. They were caused by violations of work discipline by the production employees, adverse weather conditions, and defects in the project documentation. The study demonstrated that in almost every case, these bad an adverse effect on the completion date and budget of the investment. The analyses show that in such important and expensive investments as water supply and sewerage systems, organizational structures in which a special role is assigned to middle-rank personnel should be adopted.

Go to article

Authors and Affiliations

I. Rybka
E. Bondar-Nowakowska
M. Połoński
Download PDF Download RIS Download Bibtex

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.
Go to article

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
Go to article

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
Download PDF Download RIS Download Bibtex

Abstract

The biofiltration process in the biologically activated carbon filters (BAC) is one of advanced methods of water treatment. It enables efficient elimination of dissolved organic matter and some inorganic pollutants. The production of high-quality drinking water requires an appropriate method of filter work control based on biofilm growth assessment. The first aim of the study was to assess the microbial development in beds of two BAC filters with the use of various methods. The second aim was to compare the obtained results and indicate the method which could support filter operators during routine control of biofiltration process. The study was carried out in a pilot scale on models of BAC filters during two filter runs. The analysis of Microorganisms was performed in water samples collected from different depths of the filter beds with the use of culture method (HPC), metabolica ctivity assay (with the FDA), epifluorescence microscopy – total cell count method (TCC) and biochemical method (system Vitek 2 Compact). No statistical correlation between HPC and metabolic activity assay was noted. Total bacteria number determined with the use of TCC was approx. 100–900 times higher than in the HPC method. The biochemical tests revealed the presence of several Gram-negative species. The comparison of the applied methods shows that microbial activity assay is the most useful, fast and low-cost method which may be applied additionally to the HPC method at standard water treatment plant laboratory.
Go to article

Bibliography

  1. Adam, G. & Duncan, H. (2001). Development of a sensitive and rapid method for the measurement of total microbial activity using fluorescein diacetate (FDA) in a range of soils. Soil Biology & Biochemistry, 33, 7-8, pp. 943-951, DOI: 10.1016/S0038-0717(00)00244-3
  2. Battin, T.J. (1997). Assessment of fluorescein diacetate hydrolysis as a measure of total esterase activity in natural stream sediment biomass. The Science of the Total Environment, 198, 1, pp. 51-60, DOI: 10.1016/S0048-9697(97)05441-7
  3. Boulos, L., Prévost, M., Barbeau, B., Coallier, J. & Desjardins, R. (1999). LIVE/DEAD® BacLightTM: application of a new rapid staining method for direct enumeration of viable and total bacteria in drinking water. Journal of Microbiological Methods, 37, 1, pp.77-86, DOI: 10.1016/s0167-7012(99)00048-2
  4. Burtscher, M.M., Zibuschka, F., Mach1, R.L., Lindne, G. & Farnleitner, A.H. (2009). Heterotrophic plate count vs. in situ bacterial 16S rRNA gene amplicon profiles from drinking water reveal completely different communities with distinct spatial and temporal allocations in a distribution net. Water SA, 35, 4, pp. 495-504, DOI: 10.4314/wsa.v35i4.76809
  5. Chaukura, N., Marais, S.S., Moyo, W., Mbali, N., Thakalekoala, L.C., Ingwani, T., Mamba, B.B., Jarvis, P. & Nkambule, T.T.I. (2020). Contemporary issues on the occurrence and removal of disinfection byproducts in drinking water - A review,  Journal of En-vironmental Chemical Engineering, 8, 2, 103659, DOI: 10.1016/j.jece.2020.103659
  6. Chrzanowski, T.H., Crotty, R.D., Hubbard, J.G. & Welch, R.P. (1984). Applicability of the fluorescein diacetate method of detecting active bacteria in freshwater. Microbial Ecology, 10, 2, pp.179-185, DOI: 10.1007/BF02011424.
  7. Directive (EU) 2020/2184 of the European Parliament and of the Council of 16 December 2020 on the quality of water intended for human consumption.
  8. Douterelo, I., Boxall, J.B., Deines, P., Sekar, R., Fish, K.E. & Biggs, C.A. (2014). Methodological approaches for studying the microbial ecology of drinking water distribution systems, Water Research 65, pp.134-156, DOI: 0.1016/j.watres.2014.07.008
  9. Elhadidy, A.M., Van Dyke, M.I., Chen, F., Peldszus, S. & Huck, P.M. (2017). Development and application of an improved protocol to characterize biofilms in biologically active drinking water filters, Environ. Sci. Water Res. Technol., 3, pp. 249–261, DOI: 10.1039/C6EW00279J
  10. Fu, J., Lee, W.-N., Coleman, C., Nowack, K., Carter, J. & Huang, C.-H. (2017). Removal of disinfection byproduct (DBP) precursors in water by two-stage biofiltration treatment. Water Research, 123, pp. 224-235 DOI: 10.1016/j.watres.2017.06.073
  11. Garrity G.M. (ed.) (2005a) Bergey’s Manual of Systematic Bacteriology. Vol. 2 The Proteobacteria, part B The Gammaproteobacteria, Springer, New York.
  12. Garrity G.M. (ed.) (2005b) Bergey’s Manual of Systematic Bacteriology. Vol. 2 The Proteobacteria, part C The Alpha- Beta-, Delta- and Epsilonproteobacteria. Springer, New York.
  13. Hasan, H.A., Muhammad, M.H. & Ismail, N.I. (2020), A review of biological drinking water treatment technologies for contaminants removal from polluted water resources, Journal of Water Process Engineering, 33, 101035, DOI: 10.1016/j.jwpe.2019.101035
  14. Holc, D., Pruss, A., Michałkiewicz, M. & Cybulski Z. (2016). Acceleration of carbon filters activation - experiments of pilot scale technological investigations. Water supply and water quality. PZITS, Poznań, pp. 683-703 (in Polish).
  15. Holc, D., Pruss, A., Michałkiewicz, M. & Cybulski Z. (2016). Effectiveness of organic compounds removing during water treatment by filtration through a biologically active carbon filter with the identification of microorganisms. Annual Set The Environment Protection, 18, 2, pp.235-246 (in Polish).
  16. Hopkins, Z.R., Sun, M., DeWitt, J.C. & Knappe, D.R.U. (2018). Recently Detected Drinking Water Contaminants: GenX and Other Per‐and Polyfluoroalkyl Ether Acids. Journal‐American Water Works Association, 110, 7, pp. 13-28, DOI: doi.org/10.1002/awwa.1073
  17. Kaarela, O. E., Harkki, H. A., Palmroth, M. R. T. & Tuhkanen T. A. (2015). Bacterial diversity and active biomass in full-scale granular activated carbon filters operated at low water temperatures, Environmental Technology, 36, 5-8, pp. 681-692, DOI: 10.1080/09593330.2014.958542
  18. Kaleta, J., Kida, M., Koszelnik, P., Papciak, D., Puszkarewicz, A. & Tchórzewska-Cieślak B. (2017). The use of activated carbons for removing organic matter from groundwater, Archives of Environmental Protection, 43, 3, pp. 32-41, DOI:10.1515/aep-2017-0031
  19. Kijowska, E., Leszczyńska, M. & Sozański, M.M. (2001): Metabolic activity test in investigation of biodegradation in biological filters, Water, Science & Technology: Water Supply, 1, 2, pp.151-158, DOI: doi.org/10.2166/ws.2001.0032
  20. Kołaski, P., Wysocka, A., Pruss, A., Lasocka-Gomuła, I., Michałkiewicz, M. & Cybulski Z. (2019). Removal of Organic Matter from Water During Rapid Filtration through a Biologically Active Carbon Filter Beds – a Full Scale Technological Investigation, Annual Set The Environment Protection, 21, 2, pp. 1136-1155
  21. Kołwzan, B. (2011). Analysis of biofilms – their formation and functioning. Environmental Pollution Control, 33, 4, pp. 3-14 (in Polish)
  22. Komorowska-Kaufman, M., Ciesielczyk, F., Pruss, A. & Jesionowski T. (2018). Effect of sedimentation time on the granulometric composition of suspended solids in the backwash water from biological activated carbon filters. E3S Web of Conferences, 44, 00072. EDP Sciences, DOI: 10.1051/e3sconf/20184400072
  23. Korotta-Gamage, S.M. & Sathasivan, A. (2017). A review: Potential and challenges of biologically activated carbon to remove natural organic matter in drinking water purification process, Chemosphere, 167, pp. 120-138, DOI: 10.1016/j.chemosphere.2016.09.097
  24. Liao, X., Chen, C., Chang, C.-H., Wang, Z., Zhang, X. & Xie, S. (2012) Heterogeneity of microbial community structures inside the up-flow biological activated carbon (BAC) filters for the treatment of drinking water. Biotechnology and Bioprocess Engineering, 17, pp. 881–886, DOI: 10.1007/s12257-012-0127-x
  25. Lis, A., Pasoń, Ł. & Stępniak, L. (2016). Review of Methods Used to Indication of Biological Carbon Filters Activity. Engineering and Protection of Environment, 19, 3, pp. 413-425, DOI: 10.17512/ios.2016.3.11 (in Polish)
  26. Mądrecka, B., Komorowska-Kaufman, M., Pruss, A. & Holc D. (2018). Metabolic activity tests in organic matter biodegradation studies in biologically active carbon filter beds. Water Supply and Wastewater Disposal, Politechnika Lubelska, 163-177.
  27. Oliver, J.D. (2010) Recent findings on the viable but nonculturable state in pathogenic bacteria. FEMS Microbiology Review, 34, 4, pp. 415-425, DOI: 10.1111/j.1574-6976.2009.00200.x
  28. Olszewska, M. & Łaniewska-Trokenheim, Ł. (2013) Fluorescence-based methods of cell staining in physiological state studies of bacteria. Advancements of Microbiology, 52, 4, pp. 409-418 (in Polish).
  29. Papciak D., Kaleta J., Puszkarewicz A., Tchórzewska-Cieślak B. (2016). The use of biofiltration process to remove organic matter from groundwater. Journal of Ecological Engineering, 17, 3, pp. 119–124, DOI: 10.12911/22998993/63481
  30. Pincus, D. H. (2013). Microbial identification using the bioMérieux Vitek 2 system, Encyclo-pedia of Rapid Microbiological Methods, PDA-DHI, p.1-31. (https://store.pda.org/tableofcontents/ermm_v2_ch01.pdf )
  31. Pruss, A. (2007): Contribution of Biofilm Thickness on Sand Filter Grains to Oxygen Uptake During Ammonia Nitrogen Removal. Environmental Pollution Control, 1, pp. 35-39 (in Polish).
  32. Pruss, A., Maciołek, A. & Lasocka-Gomuła I. (2009). Effect of the Biological Activity of Carbon Filter Beds on Organic Matter Removal from Water. Environmental Pollution Control, 31, pp. 31-34 (in Polish).
  33. Sadowska J. & Grajek W. (2009). Analysis of physiological state of single bacterial cell using fluorescent staining methods. Biotechnologia, 4, pp. 102-114 (in Polish).
  34. Seredyńska-Sobecka, B., Tomaszewska, M., Janus, M. & Morawski A. W. (2006). Biological activation of carbon filters. Water Research, 40, 2, pp.355-363, DOI: 10.1016/j.watres.2005.11.014
  35. Simpson D. R. (2008). Biofilm processes in biologically active carbon water purification, Water Research, 42, 12, pp. 2839-2848, DOI: 10.1016/j.watres.2008.02.025
  36. Smith, A.C. & Hussey M.A. (2016) Gram Stain Protocols, American Society for Microbiology, pp. 1-9.
  37. (https://asm.org/getattachment/5c95a063-326b-4b2f-98ce-001de9a5ece3/gram-stain-protocol-2886.pdf)
  38. Snyder, S.A., Adham, S., Redding, A.M., Cannon, F.S., DeCarolis, J., Oppenheimer, J., Wert, E.C. & Yoon, Y. (2007). Role of membranes and activated carbon in the removal of endocrine disruptors and pharmaceuticals. Desalination, 202, 1-3, pp. 156-181, DOI: 10.1016/j.desal.2005.12.052
  39. Standard Methods for the Examination of Water and Wastewater, 23’rd Edition, APHA, 2017 Washinghton
  40. Szeląg-Wasielewska, E., Joniak, T., Michałkiewicz, M., Dysarz, T. & Mądrecka, B. (2009) Bacterioplankton of the Warta River in relation to physicochemical parameters and flow rate. Ecohydrology & Hydrobiology, 9, 2-4, pp. 225-236. DOI: 10.2478/v10104-010-0008-x
  41. Szuster-Janiaczyk A. (2016). The Microbiological Evaluation of Deposits Come from Water Network on the Example of Selected Water Supply System. Annual Set The Environment Protection, 18, 2, pp. 815–827. (in Polish)
  42. van der Kooij, D. & van der Wielen, P.W.J.J. (2014). Microbial Growth in Drinking-Water Supplies. Problems, Causes, Control and Research Needs, IWA Publishing, UK
  43. Van Nevel, S., Koetzsch, S., Proctor, C. R., Besmer, M. D., Prest, E. I., Vrouwenvelder, J. S., Knezev, A., Boon, N. & Hammes F. (2017). Flow cytometric bacterial cell counts challenge conventional heterotrophic plate counts for routine microbiological drinking water monitoring. Water Research, 113, pp. 191-206. DOI: 10.1016/j.watres.2017.01.065
  44. Wagner, M., Amann, R., Lemmer, H. & Schleifer, K. (1993). Probing activated sludge with oligonucleotides specific for Proteobacteria: inadequacy of culture-dependent methods for describing microbial community structure. Applied and Environmental Microbiology, 59, 5, pp. 1520-1525, DOI: 10.1128/AEM.59.5.1520-1525.1993
  45. WHO (2003). Expert consensus. In: Bartram J., Cotruvo J.A., Exner M., Fricker C.R., Glasmacher A. (Eds.) Heterotrophic plate counts and drinking-water safety-the significance of HPCs for Water quality and human health. IWA Publishing on behalf of the World Health Organisation, London.
  46. Zamule, S.M., Dupre, C.E., Mendola, M.L., Widmer, J., Shebert, J.A., Roote, C.E. & Das P. (2021). Bioremediation potential of select bacterial species for the neonicotinoid insecticides, thiamethoxam and imidacloprid. Ecotoxicology and Environmental Safety 209, 111814; DOI: 10.1016/j.ecoenv.2020.111814
  47. Zhang, S., Gitungo, S.W., Axe, L., Raczko, R.F. & Dyksen, J.E. (2017). Biologically active filters – an advanced water treatment process for contaminants of emerging concern. Water Research, 114, pp. 31-41, DOI: 10.1016/j.watres.2017.02.014
  48. Ziglio, G., Andreottola, G., Barbesti, S., Boschetti, G., Bruni, L., Foladori, P. & Villa, R. (2002). Assessment of activated sludge viability with flow cytometry. Water Research, 36, 2, pp. 460-468, DOI: 10.1016/s0043-1354(01)00228-7
Go to article

Authors and Affiliations

Dorota Holc
1
ORCID: ORCID
Beata Mądrecka-Witkowska
1
ORCID: ORCID
Małgorzata Komorowska-Kaufman
1
ORCID: ORCID
Elżbieta Szeląg-Wasielewska
2
Alina Pruss
1
ORCID: ORCID
Zefiryn Cybulski
3

  1. Poznan University of Technology, Institute of Environmental Engineering and Building Installations, Poland
  2. Adam Mickiewicz University in Poznań, Faculty of Biology, Department of Water Protection, Poland
  3. Greater Poland Cancer Center, Microbiology Laboratory, Poland
Download PDF Download RIS Download Bibtex

Abstract

In the authors’ opinion, the issue of incorrectly functioning water insulation of foundation walls in the existing buildings in Poland is currently rather common. The paper includes a multicriteria analysis aimed at arranging the selected options of the foundation wall vertical water insulation technology in an existing model historic building using the weighted sum, entropy and AHP methods. Each of the studied solutions was evaluated in terms of the following criteria: costs of construction works, time of execution of construction works, popularity of using particular insulation options by other contractors, durability of the executed insulation and the degree of nuisance of the executed works

Go to article

Authors and Affiliations

J. Rosłon
M. Seroka
Download PDF Download RIS Download Bibtex

Abstract

The objective of the presented paper is to investigate the performance of concrete containing volcanic scoria as cement replacement after 7, 28, 90, and 180 days curing. Five performance indicators have been studied. Compressive strength, water permeability, porosity, chloride penetrability, and reinforcement corrosion resistance have all been evaluated. Concrete specimens were produced with replacement levels ranging from 10 to 35%. Test results revealed that curing time had a large influence on all the examined performance indicators of scoria-based concrete. Water permeability, porosity, and chloride penetrability of scoria-based concrete mixes were much lower than that of plain concrete. Concretes produced with scoria-based binders also decelerated rebar corrosion, particularly after longer curing times. Furthermore, an estimation equation has been developed by the authors to predict the studied performance indicators, focusing on the curing time and the replacement level of volcanic scoria. SEM/EDX analysis has been reported as well.

Go to article

Authors and Affiliations

A. M. al-Swaidani
Download PDF Download RIS Download Bibtex

Abstract

The present study examines some durability aspects of ambient cured bottom ash geopolymer concrete (BA GPC) due to accelerated corrosion, sorptivity, and water absorption. The bottom ash geopolymer concrete was prepared with sodium based alkaline activators under ambient curing temperatures. The sodium hydroxide used concentration was 8M. The performance of BA GPC was compared with conventional concrete. The test results indicate that BA GPC developes a strong passive layer against chloride ion diffusion and provides better protection against corrosion. Both the initial and final rates of water absorption of BA GPC were about two times less than those of conventional concrete. The BA GPC significantly enhanced performance over equivalent grade conventional concrete (CC).

Go to article

Authors and Affiliations

R. Saravanakumar
V. Revathi
Download PDF Download RIS Download Bibtex

Abstract

People rarely consider where their tap water comes from, or how much of it is actually available. At the same time, it is people who are most often responsible for water pollution. Problems involving the contamination of water-supply areas in Poland are scrutinized by an “intervention team” of experts at the Polish Hydrogeological Survey.

Go to article

Authors and Affiliations

Małgorzta Woźnicka
Rafał Janica
Download PDF Download RIS Download Bibtex

Abstract

There is often a need to improve the taste of mineral water by reducing the sulphate ion content. It was found that for such an effect, nanofiltration (NF) process can be used. In the case, the proposed formula was assumed obtaining a mineral water with reduction of H2S and SO42- content through the following processes: stripping - UF/MF or rapid fi ltration - nanofiltration - mixing with raw water or filtration through calcium bed. The paper shows the results of the tests, with use of mineral waters and nanofiltration. Commercial nanofiltration membranes NF-270 Dow Filmtec and NF-DK GE Infrastructure Water&Process Technologies were applied. NF was carried out for mixed water from both water intakes (1 and 2), recovery of 50%, at transmembrane pressure of 0.8-1.2 MPa in the dead-end fi ltration mode. In addition, the permeate obtained in NF was filtered through a column fi lled with 1.0-3.0 mm limestone rock, in order to improve the composition of mineral water. The tested mineral water is the sulphate-chloride-sodium-calcium-magnesium in nature and contains 991 mg/L of SO42- and 2398 mg/L of TDS, while the permeate after NF showed the chloride - sodium hydrogeochemical type (TDS: 780-1470 mg/L, sulfate 10-202.7 mg/L, calcium 23-39.7 mg/L, magnesium 11-28 mg/L). As a result of water treatment in the NF process, high reduction of SO42- ions was obtained (79-98.7%), while the TDS was reduced in 51-64%. Because the process of NF allows for relatively high reduction of bivalent ions, a significant reduction in calcium ion content (84-88%) and magnesium (84-89%) has been also obtained. Monovalent ions were reduced to a lesser extent, i.e. sodium in 46% and bicarbonates in 39-64.1%. Despite obtaining the positive effect of the sulphate ions content reduction, the NF process significantly changed the mineralogy composition of water. The permeate filtration (DK-NF membrane) on the CaCO3 deposit led to a correction of the hydrogeochemical type of water from chloridesodium to chloride-bicarbonate-sodium. The concentration of calcium ions was increased by 60.5% and was 28.2 mg/L, and bicarbonate ions by 7.78% (increased to 195 mg/L). Based on a morphological assessment of the deposits in the SEM image and their chemical composition, the presence of gypsum crystals was detected on the surface of the NF-270 membrane. The deposits formed on the NF-DK membrane were of a completely different character as aggregations of iron and aluminium oxides/hydroxides were found. Such significant mineralogical differences between the secondary deposits crystallising on the surface of the membranes point to the impact of several factors, including membrane characteristics, concentration polarisation, mass transport mechanisms, etc.

Go to article

Authors and Affiliations

Michał Bodzek
Mariola Rajca
Barbara Tomaszewska
Download PDF Download RIS Download Bibtex

Abstract

Compared to other European countries, Poland has scarce drinking water resources and exhibits

significant variation in annual runoff. On the other hand, the geothermal water resources present in sedimentary/structural basins, mostly in the Polish Lowlands and the Podhale geothermal system, not only provide a

valuable source of renewable energy, which is utilized, although only to a limited extent, but can also be used

for many other purposes. The paper presents the results of studies related to the desalination of low dissolved

mineral content geothermal waters from the Bańska IG-1 well using a dual hybrid system based on ultrafiltration and reverse osmosis. The desalination of geothermal waters may be considered a possible solution leading

to the decentralization of drinking water supply. In many cases, using cooled waters for drinking purposes may

be considered an alternative method of disposing of them, in particular for open drain arrangements, i.e. where

cooled water is dumped into surface waters.

Go to article

Authors and Affiliations

B. Tomaszewska
Download PDF Download RIS Download Bibtex

Abstract

In the southern Spitsbergen area, thermal and mineral waters are primarily

associated with subpermafrost deep circulation, being mixed with shallow circulation and

glacial waters. Four thermal springs, located in the region of Stormbukta (Sørkappland),

were studied and analyzed. In the thermal waters, the main cation is sodium, while the

main anions are chloride and bicarbonate. The temperatures of the mineral and thermal

waters range from 3.4 to 15.1°C. The pH values are between 7.43 and 8.41. The total

dissolved solids (TDS) content of the geothermal waters is in the range of 346–4031 mg/l

and the Olsok thermal spring has the highest TDS values. Based on the variation in

physicochemical characteristics, two thermal water types were distinguished in the study

area. The first type is associated with thermal waters originating from deep circulation

waters. The second type is associated with the thermal and mineral waters originating

from the mixture of subpermfrost hot brines with glacial waters.

Go to article

Authors and Affiliations

Tomasz Olichwer
Robert Tarka
Download PDF Download RIS Download Bibtex

Abstract

Recycling construction and demolition waste not only reduces project costs; and saves natural resources, but also solves the environmental threat caused by construction waste disposal. In this paper, C25 waste road concrete is used as an experimental material, the uniaxial compression strength and tensile splitting strength of C25 RAC whose coarse aggregate replacement rate is 0%, 25%, 50%, 75%, and 100% are tested under the condition that the water-to-cement ratio is 0.47, 0.55 and 0.61. The results show: (1) the uniaxial compression strength and tensile splitting strength decrease with the increase of RAC; (2) for concrete with the same water-to-cement ratio, when the coarse aggregate replacement rate changes from 0% to 50%, the uniaxial compression strength and tensile splitting strength of RAC changes slightly. When the coarse aggregate replacement rate changes from 50% to 100%, the uniaxial compression strength and tensile splitting strength of RAC decreases rapidly

Go to article

Authors and Affiliations

X.H. Deng
Z.L. Lu
P. Li
T. Xu
Download PDF Download RIS Download Bibtex

Abstract

Potok Golawiecki (a river in the province of Silesia) is polluted in a way typical for the Upper Silesian industrial zone. It is the river into which the Ziemowit coal mine discharges its salt waters and it also receives municipal sewage. Changes in the values of selected indicators ofwater quality for Potok Golawiecki along its course were determined in the paper. It was found that the hydrochcmical character of the water in Potok Goławiecki depended strongly on salt water discharges from mines, which were the main factor disturbing the river's natural environment. The pollution of the river makes its water non-potable, and excludes its use even in industry
Go to article

Authors and Affiliations

Beata Jabłońska
ORCID: ORCID
Download PDF Download RIS Download Bibtex

Abstract

The aim of the study was to determine species structure of aquatic bugs in four anthro-pogenic water reservoirs. Heteroptera structure observed in studied reservoirs was clearly differen-tiated, which refers to age of the ponds. Newly created water reservoirs become quickly colonized mainly by pioneering species Corixinae, which led to formation of taxonomic group population of density exceeding 2700 indiv. m-2. In older reservoirs there were fish, which potential predation pressure led to almost a complete decline of bugs. The reason of bugs poverty in water reservoirs colonized by fish was also probably a small habitat diversity, leading to lack of refuges from predators.
Go to article

Authors and Affiliations

Monika Tarkowska-Kukuryk
Wojciech Płaska
Jacek Rechulicz
Tomasz Mieczan
Wojciech Pęczuła
Download PDF Download RIS Download Bibtex

Abstract

The aim of research carried out was to describe the zonality and structure of zoopleuston in shallow eutrophic reservoirs. Zoopleuston structure discovered in examined reservoirs was quite different than in depression reservoirs and lakes on Łęczna-Włodawa Lakeland. It was related to morphometry of reservoirs and plant richness of shallow litoral zone. Higher species richness in the water/land contact zone was found which confirms previous studies, however, sometimes zoopleuston abundance showed the opposite pattern. Most differences occurred in dominants composition as in water/land contact zone and on the depth of 0.5 m dominated mainly by small species of Heteroptera: Micronecta minutissima and Cymatia coleoptrata.
Go to article

Authors and Affiliations

Monika Tarkowska-Kukuryk
Wojciech Płaska
Jacek Rechulicz
Tomasz Mieczan
Wojciech Pęczuła
Download PDF Download RIS Download Bibtex

Abstract

The studies concerned qualitative and quantitative analysis of seston Rotifera communities of Ślepiotka stream polluted with communal sewages. The samples were also taken from the small, inforest pond confluence with the stream. The studies were carried out from March to November 1999. The water from the pond, which flew down into the stream, had a good influence on the Rotifera communities living there. The stable increase in species diversity, abundance and stability of Rotifera communities of Ślepiotka stream below the inflow was recorded. The physic-chemical analysis confirmed the favorable influence of the pond on Ślepiotka stream water quality.
Go to article

Authors and Affiliations

Anna Niesler
Download PDF Download RIS Download Bibtex

Abstract

The results from the experimental research are presented in the abstract. The experimental research involved utilization of the sludge from the mine water treatment plant of Coal Quarry ČSA/Czechoslovak Army/ (hereinafter “ČSA”) and Coal Quarry Jana Švermy (hereinafter “JŠ”) in the segment of thermal insulation mortars. The mine water treatment is described below including chemical and mineralogical sludge composition as the additional component of the binding material in the polyurethane thermal insulation mortars. Furthermore the composition of experimental mixtures of the thermal insulation polyurethane mortar is presented in the work and its physical-mechanical properties. The monitored elements included the strength characteristics, heat conductivity coefficient λ, and water vapour diffusion coefficient μ.

Go to article

Authors and Affiliations

V. Václavík
J. Daxner
J. Valíček
V. Dombek
T. Dvorský
M. Kušnerová
B. Václavíková
Download PDF Download RIS Download Bibtex

Abstract

The data set of the Warta discharges in Poznań (Poland) is one of the largest in the world as the daily observations of river stages have been conducted without interruptions since January, 1st, 1822. The Poznań measurement profile is situated in the 243.6 km and closes the catchment area of approximately 25 thousand square kilometers. The data used as the input in the paper were daily values of the Warta discharges in Poznań in the years 1822-2012. The climate in Poznań, a city situated in the centre of the Wielkopolska (Greater Poland) region, is relatively stable (Miler et al. 2005). Also the Warta River runoff shows considerable stability, especially in terms of mean annual values. Short-term trends are random in character. It was found that the Jeziorsko reservoir (total storage volume of 203 000 000 m3, officially put to use on September, 9th, 1987) significantly reduced daily variability of the flows and reduced peak discharge of the flood wave in the summer of 1997 on the Warta River at Poznań. The calculated periodogram for mean annual discharges of the Warta River in Poznań shows that there are main periodicities of ca. 10 year lengths. The research of the Provincial Inspectorate for Environmental Protection (WIOŚ) in Poznań shows a gradual improvement of water quality in the Warta River in Poznań.

Go to article

Authors and Affiliations

Antoni T. Miler
Download PDF Download RIS Download Bibtex

Abstract

The work is an attempt to assess piped water quality in four counties located in east central Poland. Piped water was analysed for three successive years in each county. Water samples were tested for the following physical and chemical parameters: turbidity, colour, conductivity, taste, odour, pH, nitrates (III), nitrates (V), iron and manganese. They were compared with the current standard values. Preliminary data analysis included an analysis of maximum and minimum values of physical and chemical parameters, and it revealed that turbidity, colour, iron and manganese contents exceeded the permissible standards in all the counties. Percentages of parameters exceedances and mean values of the exceedances were used to rank the counties in terms of water quality. The ranking was obtained by means of multidimensional comparative analysis. It was demonstrated that best quality water was supplied by Węgrów County water supply system which was followed by Mińsk Mazowiecki County. The third rank was assigned to Łosice County and the poorest quality water was found to be supplied by Siedlce County water supply system.

Go to article

Authors and Affiliations

Elżbieta Radzka
Katarzyna Rymuza
Jolanta Jankowska
Download PDF Download RIS Download Bibtex

Abstract

Groundwater quality depends on many factors, among which public water supply systems and wastewater infrastructure in built-up areas plays a very important role. Analyses of influence of designed water supply and sewage network in Maciejowa village on the ground- and surface water quality have been the main aim of the paper. A mathematical model based on deterministic description of groundwater flow and migration of pollutants has been applied. An influence of various scenarios of drinking water/wastewater system development and management on pollution loads entering water environment were simulated. Recommendations regarding the sequence of individual piping systems construction were formulated to assure the best protection of water resources.
Go to article

Authors and Affiliations

Mieczysław Chalfen
Tadeusz Molski
Katarzyna Wiącek
Download PDF Download RIS Download Bibtex

Abstract

The objective of the paper is to use life cycle assessment to compare environmental impact of different technologies used in the process of water disinfection. Two scenarios are developed for water disinfection life cycle at ZUW Raba water treatment plant: (1) historical, in which gaseous chlorine is used as a disinfectant and (2) actual, in which UV radiation and electrolytically generated sodium hypochlorite are used for that purpose. Primary data is supplemented with ecoinvent 3 database records. Environmental impact is assessed by IMPACT2002+ method and its midpoint and endpoint indicators that are calculated with the use of SimaPro 8.4 software. The focus of the assessment is on selected life cycle phases: disinfection process itself and the water distribution process that follows. The assessment uses the data on flows and emissions streams as observed in the Raba plant. As the results of primal analysis show, a change of disinfectant results in quantitative changes in THMs and free chlorine in water supplied to the water supply network. The results of analysis confirm the higher potential of THMs formation and higher environmental impact of the combined method of UV/NaClO disinfection in distribution phase and in whole life cycle, mainly due to the increase of human toxicity factors. However, during the disinfection phase, gaseous chlorine use is more harmful for environment. But the final conclusion states that water quality indicators are not significant in the context of LCA, while both disinfection and distribution phases are concerned.

Go to article

Authors and Affiliations

Artur Jachimowski
Tomasz Nitkiewicz
Download PDF Download RIS Download Bibtex

Abstract

The aim of this study was to examine the changes in the chemical composition of shallow groundwater and its quality that have occurred in the last decade in an agriculturally used, heavily populated and characterized by a complex geological structure, catchment of the Stara Rzeka river, located in the flysch part of the Outer Carpathians. Water samples were collected during 2013 from 19 still operating wells. Analyses of pH, electrolytic conductivity and chemical composition by ion chromatography were conducted. The obtained results were compared with the results of studies conducted in 2003 for the same wells. The quality of groundwater and its suitability for consumption was assessed based on the regulations currently existing in Poland. 21% of the wells still do not meet the requirements for drinking water in terms of at least one component. However, there was a decrease in the concentration of mineral forms of nitrogen and phosphorus in most of the wells and their mean concentration as compared to 2003 was reduced. In terms of physical and chemical characteristics groundwater of this region is typical of the hypergenic zone of the temperate climate. The highest concentrations were observed for Ca2+ and HCO3- ions, while K+ and Cl- were characterized by the largest variability. Principal Component Analysis (PCA) demonstrated that the factors determining the quality and chemical composition of the analyzed waters include the composition of bedrock (mineralogy of the rock environment) and human economic activity, and that they have not been significantly changed over the past decade.

Go to article

Authors and Affiliations

Anna Bojarczuk
Ewelina Jelonkiewicz
Łukasz Jelonkiewicz
Anna Lenart-Boroń

This page uses 'cookies'. Learn more