Dergiler / Journal of the Turkish Chemical Society Section A: Chemistry / 2018 / Cilt: 5 - Sayı: 2

Nicotinamide-Modified poly(HEMA-GMA)-Nic Cryogels for Removal of Pesticides

Sayfa
941–952
Yayın Tarihi
2018-01-01
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

As expected, the removal of chlordane was performed with the highest adsorption performance in cyclohexane with the lowest dielectric constant.

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:Chlordane is only one of the persistent pesticides used in some countries despite the ban.
📊
Temel Bulgular & Veri:Removal of chlordane, a severe threat to all living things, was performed using nicotinamide-modified poly (2-hydroxyethyl methacrylate-glycidyl methacrylate), poly(HEMA-GMA)-Nic, polymeric cryogels in this study.
💡
Sonuç & Katkı:As expected, the removal of chlordane was performed with the highest adsorption performance in cyclohexane with the lowest dielectric constant.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Chlordane · Pesticide · Alcoho-phobic

Abstract

Chlordane is only one of the persistent pesticides used in some countries despite the ban. Removal of chlordane, a severe threat to all living things, was performed using nicotinamide-modified poly (2-hydroxyethyl methacrylate-glycidyl methacrylate), poly(HEMA-GMA)-Nic, polymeric cryogels in this study. Pesticides are practically insoluble in water. For that reason, ethanol is used as a solvent which is not chemically dangerous and easily accessible in every laboratory. As an adsorbent, poly (HEMA-GMA) polymeric cryogels previously synthesized in the literature have been modified using nicotinamide. The modification of poly(HEMA-GMA) with nicotinamide is the first in the literature. Removal of chlordane in alcohol medium has been accomplished exploiting the alcoho-phobic interaction, which was the first indication in our previous study. Structural analysis of poly(HEMA-GMA)-Nic was performed using Fourier transform infrared spectroscopy (FT-IR) and elemental analysis methods. Scanning electron microscopy (SEM) was used to understand the surface morphology of cryogels. Surface area and cavity volume calculations were determined by applying N2 adsorption method and swelling test. The interaction time and maximum adsorption capacity were identified as 5 minutes and 64.61 mg chlordane/g cryogel for 300 mg/L chlordane concentration and 108.818 mg chlordane/g cryogel for 800 mg/L chlordane concentration during the adsorption experiments. Cyclohexane, toluene, chloroform, dichloromethane, acetone, and acetonitrile were used as solvent to observe the solvent effect on adsorption of chlordane onto the polymeric material. As expected, the removal of chlordane was performed with the highest adsorption performance in cyclohexane with the lowest dielectric constant.

🔖

Bu Makaleye Atıf Yap

KÖSE, K., AKVERAN, G. A., EROL, K., KÖSE, D. A. (2018). Nicotinamide-Modified poly(HEMA-GMA)-Nic Cryogels for Removal of Pesticides. Journal of the Turkish Chemical Society Section A: Chemistry, Cilt: 5 - Sayı: 2, 941–952. https://ajindex.com/articles/781435

📄 Tam Metin PDF Okuyucu

📄

PDF görüntüleyici hazırlanıyor...

Kaynakça (15)

  1. Xiao P, Mori T, Kondo R. Biotransformation of the organochlorine pesticide trans-chlordane by wood-rot fungi. New biotechnology. 2011;29(1):107-15
  2. Dearth MA, Hites RA. Highly chlorinated dimethanofluorenes in technical chlordane and in human adipose tissue. Journal of the American Society for Mass Spectrometry. 1990;1(1):99-103
  3. Hirano T, Ishida T, Oh K, Sudo R. Biodegradation of chlordane and hexachlorobenzenes in river sediment. Chemosphere. 2007;67(3):428-34
  4. Eitzer BD, Mattina MI, Iannucci‐Berger W. Compositional and chiral profiles of weathered chlordane residues in soil. Environmental toxicology and chemistry. 2001;20(10):2198-204
  5. Ouyang Y, Ou L-T, Sigua G. Characterization of the pesticide chlordane in estuarine river sediments. Journal of environmental quality. 2005;34(2):544-51
  6. Taguchi S, Yakushiji T. Influence of termite treatment in the home on the chlordane concentration in human milk. Arch Environ Con Tox. 1988;17(1):65-71
  7. Janouskova E, Krbuskova M, Rehurkova I, Klimova M, Prokes L, Ruprich J. Determination of chlordane in foods by gas chromatography. Food chemistry. 2005;93(1):161-9
  8. Council NR. An assessment of the health risks of seven pesticides used for termite control. 1982
  9. Combarnous Y. Endocrine Disruptor Compounds (EDCs) and agriculture: The case of pesticides. Comptes Rendus Biologies. 2017;340(9):406-9
  10. Yadav IC, Devi NL, Li J, Zhang G, Breivik K. Possible emissions of POPs in plain and hilly areas of Nepal: implications for source apportionment and health risk assessment. Environmental pollution. 2017;220:1289-300
  11. Goldner WS, Sandler DP, Yu F, Hoppin JA, Kamel F, LeVan TD. Pesticide use and thyroid disease among women in the Agricultural Health Study. American journal of epidemiology. 2010;171(4):455-64
  12. Shindell S, Ulrich S. Mortality of workers employed in the manufacture of chlordane: an update. Journal of occupational medicine: official publication of the Industrial Medical Association. 1986;28(7):497-501
  13. MacMahon B, Monson RR, Wang HH, Zheng T. A second follow-up of mortality in a cohort of pesticide applicators. Journal of occupational medicine: official publication of the Industrial Medical Association. 1988;30(5):429-32
  14. Everett CJ, Matheson EM. Biomarkers of pesticide exposure and diabetes in the 1999–2004 National Health and Nutrition Examination Survey. Environment international. 2010;36(4):398-401
  15. Wu X, Lam JC, Xia C, Kang H, Xie Z, Lam PK. Atmospheric concentra