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Oczyszczanie ścieków z przemysłu kosmetycznego za pomocą procesu koagulacji

Treść / Zawartość
Identyfikatory
Warianty tytułu
EN
Cosmetic wastewater treatment by coagulation
Języki publikacji
PL
Abstrakty
EN
In this study the coagulation process of five cosmetics wastewater types has been investigated. All samples were collected from big cosmetic factory in Poland. Due to changeable production profile, also significant changeability of the wastewater composition and the concentration of pollutants were observed. COD values of raw wastewaters samples 1, 2, 3, 4 and 5 were as follows: 7293, 3241, 3241, 5132 and 1089 mg/l, respectively. Before coagulation easily settleable suspended solids were removed by 30 min primary sedimentation. After sedimentation COD values were decreased to 1134, 2512, 3241, 1858 and 1089 mg/l, respectively. Coagulation with Al2 (SO4)3 at pH 7.0 and FeCl3 at pH 6.0 and 9.0 allowed to achieve COD removal in the range of 33.0–63.5%. The effect of coagulation was better for the samples of lower contents of easily settleable suspended solids and higher content of fine suspended solids. The best effects of COD removal by coagulation achieved for investigated wastewaters were as follow: sample 1 – 39.2%, by Al2 (SO4) 3 and FeCl3 at pH 9.0; sample 2 – 54.8%, by FeCl3 at pH 6.0; sample 3 – 60.0%, by Al2 (SO4) 3; sample 4 – 33.3%, by Al2 (SO4) 3; sample 5 – 63.5%, by FeCl3 at pH 6.0. The differences in coagulants effectiveness were not significant. Flopam flocculant improved the effect of coagulation – shortened the clarification time from 60 min to 5 min, reduced the coagulant doses by about 50 mg/l and increased COD removal. In the coagulation assisted by Flopam flocculant, Al2 (SO4) 3 proved to be the best coagulant for sample 3 (62.5%), FeCl3 at pH 6.0 was the best for sample 2 (54.8%) and sample 5 (63.9% – the best result of all) and FeCl3 at pH 9.0 for sample 4 (50.0%). The best effect of coagulation was achieved for sample no 5, which had no easily settleable suspended solids. The total effect of COD removal, including primary sedimentation and coagulation ranged from 63.9 to 90.6%. GC-MS analysis allowed to identify 110 compounds. The predominant compounds identified by GC-MS were: cyclopentasiloxane, decamethylcyclopentasiloxane and synthetic musk – galaxolide (HHCB). HHCB concentration was decreased in the coagulation by 87.3–92.2%. The degree of other compounds removal varied in the range 0–99.4%.
Rocznik
Strony
873--891
Opis fizyczny
Bibliogr. 28 poz., tab., rys.
Twórcy
autor
  • Politechnika Warszawska
  • Politechnika Warszawska
autor
  • Politechnika Warszawska
autor
  • Politechnika Warszawska
Bibliografia
  • 1. Aloui F., Kchaou S., Sayadi S.: Physicochemical treatments of anionic surfactants wastewater: Effect on aerobic biodegradability. Journal of Hazardous Materials , 164, 353–359 (2009).
  • 2. Balk F. i Ford R. A.: Environmental Risk Assessment for polycyclic musks AHTN and HHCB in EU I. Fate and exposure assesment. Toxicology Letters, 111,57–59 (1999).
  • 3. Bautista P., Mohedano A. F., Gilarranz M. A., Casas J., Rodriguez J.: Application of Fenton oxidation to cosmetic wastewaters treatment. Journal of Hazardous Materials, 143, 128–134 (2007).
  • 4. Bautista P., Mohedano A., Menendez N., Casas J., Rodriguez J. J.: Catalytic wet peroxide oxidation of cosmetic wastewaters with Fe-bearing catalysts. Catalysis Today , 151, 148–152 (2010).
  • 5. Bester K.: Retention characteristics and balance assessment for two polycyclic musk fragrances (HHCB and ATHN) in a typical German Sewage treatment plant. Chemosphere, 57, 863–870 (2004).
  • 6. Boroski M., Rodrigues A. C., Garcia J. C., Sampaio L. C., Nozaki J., Hioka N.: Combined electrocoagulation and TiO2 photoassisted treatment applied to wastewater effluents from pharmaceutical and cosmetic industries. Journal of Hazardous Materials, 162, 448–454 (2009).
  • 7. Carballa M., Omil F., Lema J. M.: Removal of cosmetic ingredients and pharmaceuticals in sewage primary treatment. Water Research, 39, 4790–4796 (2005).
  • 8. El-Gohary F., Tawfik A., Mahmoud U.: Comparative study between chemical coagulation/precipitation (C/P) versus coagulation/dissolved air flotation (C/DAF) for pre-treatment of personal care products (PCPs) wastewater. Desalination, 252, 106–112 (2010).
  • 9. Felis E., Alder A., Surmacz-Górska J., Miksch K.: Advanced oxidation of the polycyclic musk fragrances with using UV and UV/H2O2 processes. Archives of Environmental Protection, 34, 13–23 (2008).
  • 10. HERA.: Human & Environmental Risk Assessment on ingredients of Household Cleaning Products Polycyclic musks AHTN (CAS 1506-02-1) and HHCB (CAS 1222-05-05), 2004.
  • 11. Juraszka B., Piecuch T.: Podczyszczanie ścieków poprodukcyjnych zawierających kleje organiczne metodą koagulacji chlorkiem żelaza, Rocznik Ochrona Środowiska (Annual Set the Environment Protection), 10, 221–242 (2008).
  • 12. Juraszka B., Sumara A.: Badania efektu oczyszczania ścieków produkcyjnych zawierających kleje organiczne w procesie koagulacji z zastosowaniem koagulanta PAX XL 19F i PIX 113, Rocznik Ochrona Środowiska (Annual Set the Environment Protection), 12, 221–242 (2010).
  • 13. Kowal A.L., Świderska-Bróż M.: Oczyszczanie wody. Podstawy tech¬niczne i technologiczne, procesy i urządzenia. Wydawnictwo Naukowe PWN, Warszawa, 2009
  • 14. Kupper T., Plagellat C., Brandli R., Alencastro D., Grandjean D., Tarradellas J.: Fate and removal of polycyclic musks, UV filters, and biocides during wastewater treatment. Water Research, 40, 2603–2612 (2006).
  • 15. Li W., Ma Y., Guo C., Hu W., Liu K., Wang Y., Zhu T.: Occurence and behavior of the most used sunscreen UV filters In a wastewater reclamation plant fragrances from wastewater. Water Research, 37 (80), 1976–1982 (2007).
  • 16. Malinka W.: Zarys chemii kosmetycznej. Volumed, Wrocław, 1999.
  • 17. Marzec A.: Chemia kosmetyków. Dom Organizatora, Toruń, 2009.
  • 18. Molski M.: Chemia piękna. Wydawnictwo Naukowe PWN, Warszawa, 2009.
  • 19. Ricking M., Schwarzbauer J., Hellou J., Svenson A., Zitko V.: Polycyclic aromatic musk compounds in sewage treatment plant effluents of Canada and Sweden – first results. Marine Pollution Bulletin, 46, 410–417 (2003).
  • 20. Rosal R., Rodriguez A., Perdignon-Melon J. A., Petre A., Garcia-Calvo E., Gomez M. J., Aguera A., Fernandez-Alba R.: Occurrence of emerging pollutants in urban wastewater and their removal through biological treatment followed by ozonation. Water Research, 44 (20), 578–588 (2009).
  • 21. Schlumpf M., Schmid P., Durrer S., Conscience M., Maerkel K., Henseler M., Gruetter M., Herzog I., Reolon S., Ceccatelli R., Faass O., Stutz E., Jarry H., Wuttke W., Lichtensteiger W.: Endocrine activity and developmental toxicity of cosmetic UV filters – an update. Toxicology, 205, 113–122 (2004).
  • 22. Seinen W., Lemmen J. C., Pieters R. H. H., Verbruggen E. M. J., van der Burg B.: ATHN and HHCB show weak estrogenic – but no eterothropic acticity. Toxicol. Letter., 111, 161–168 (1999).
  • 23. Suarez S., Lema J. M., Omil F.: Pretreatment of hospital wastewater by coagulation-flocculation and flotation, Bioresource Technology, 2138–2146 (2009).
  • 24. Suarez S., Lema J., Omil F.: Removal of Pharmaceuticals and Personal Care Products (PPCPs) under nitryfing and denitryfing conditions. Water Research, 44 , 3214–3224 (2010).
  • 25. Ternes T., Bonerz M., Herrmann N., Loffler D., Keller E., Lacida B.: Determination of pharmaceutical, iodinated contrast media and musk fragrances in sludge by LC/tandem MS and GC/MS. Journal of Chromatography A, 1067, 213–223 (2005).
  • 26. Ternes T. A., Stuber J., Hermann N., McDowell D., Ried A., Kapman M., Teiser B.: Ozonation: a tool for removal of pharmaceuticals, contrast media and musk fragrances from wastewater, Water Research, 37(80), 1976–1982 (2003).
  • 27. Thornton I., Butler D., Docx P., Hession M., Makropoulos C., McMullen M.: Pollutants in urban wastewater and sewage sludge. Luxembourg: Office for Official Publications of the European Communities, 2001.
  • 28. Zeng X., Sheng G., Xiong Y., Fu J.: Determination of polycyclic musks in sewage sludge from Guangdong, China using GC – EI –MS. Chemosphere, 60, 817–823 (2005).
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-9d211df2-a721-4b26-8409-c6229035783f
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