Cumulative CAMAG Bibliography Service CCBS

Our CCBS database includes more than 11,000 abstracts of publications. Perform your own detailed search of TLC/HPTLC literature and find relevant information.

The Cumulative CAMAG Bibliography Service CCBS contains all abstracts of CBS issues beginning with CBS 51. The database is updated after the publication of every other CBS edition. Currently the Cumulative CAMAG Bibliography Service includes more than 11'000 abstracts of publications between 1983 and today. With the online version you can perform your own detailed TLC/HPTLC literature search:

  • Full text search: Enter a keyword, e.g. an author's name, a substance, a technique, a reagent or a term and see all related publications
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      64 244
      Quantitative TLC determination of chlorophylls in spuce needles under mind pollution conditions
      D. HEIMLER*, M. MICHELOZZI, V. BODDI, (*Dip. die Sci. del Suolo e Nutriz. della Piauto, Univ. degli Studi di Firenze, Piazzale delle Cascine 28, Firence, Italy)

      Chromatographia 28, 148-150 (1989). TLC of chlorophyll a and b on cellulose layers with petrol ether - isopropanol 98:2 in the dark. Quantification by densitometry at 410 nm for chlorophyll a and at 452 nm for b. Detection limit 50 ng. The calibration curves were linear in the range of 50-200 ng (r=0.997 for a and 0.995 for b). TLC provides a rapid and simple method for monitoring vegetation damage.

      Classification: 30b
      66 043
      (Quantitative HPTLC of polyaromatic hydrocarbons)
      W. FUNK, J. BECKER, V. GLÜCK, (FH Giessen-Friedberg, Dept. Techn. Public Health Serv., Wiesenstrasse 14, D-W-6300 Giessen, Germany)

      Merck Spectrum 1991, 24-28. HPTLC of indenopyrene, benzofluoroanthene, benzopyrene, fluoroanthene, benzoperylene on silica (impregnated with 4 g caffeine in 96 g dichloromethane) at -20°C with dichloromethane as eluent. Quantification by in-situ fluorimetry.

      Classification: 5b
      69 169
      (Determination of mipcin in ground water by thin-layer chromatography
      L. LI (Li Long), R. GAO (Gao Riqun), Y. LIU (Liu Yugu), (Tongji Univ. of Med., Wuhan, 430030 P.R. China)

      Pest. (Nongyao) 31, 31-32 (1992). TLC of mipcin (= o-cumenylmethylcarbamate) on silica with acetone – ethyl acetate 1:1. Detection by spraying with 1% potassium iodide – ethanol 5:2. Quantification by densitometry at 400 nm.

      Classification: 29c
      75 127
      Quantitative analysis of alachlor and atrazine in polymeric microcapsules determined by reverse-phase high-performance thin-layer chromatography
      O.D. DAILEY, jr.*, R.M. JOHNSON, (*USDA, ARS, Southern Reg. Res. Cent., P.O. Box 19687, New Orleans, Louisiana 70179, USA)

      J. Liquid Chromatogr. 18, 873-885 (1995). HPTLC on RP-18 silica with methanol - water 85:15 and 70:30. Quantification by densitometry at 200 nm for alachlor and at 220 nm for atrazine.

      Classification: 29d
      77 041
      Analysis of hydroxy-PAH by thin layer chromatography and OPLC
      K TYRPIEN, (Inst. for Chemical Processing of Coal, Zamkowa Street 1, 41-803 Zabrze, Poland)

      J. Planar Chromatogr. 9, 203-207 (1996). TLC and OPLC of hydroxy derivatives of polycyclic aromatic hydrocarbons (1-naphthol, 2-naphthol, 2,3-dihydroxynaphthalene, 2,7-dihydroxynaphthalene, 1,3-dihydroxynaphthalene, 1,5-dihydroxy-naphthalene, 9-hydroxyphenanthrene, 1-hydroxypyrene) on RP-18 with acetonitrile - water 1:1 or 3:2 and methanol - water 3:1 for planar chromatography and acetonitrile - water 3:2 for OPLC. Visualization under UV 254 and 365 nm; the plates were then sprayed with fast blue B salt solution and observed again under UV 365 nm.

      Keywords: environmental
      Classification: 5b, 37
      93 081
      Detection of antibiotic substances in municipial waste water treatment facilities
      CH. WEINS* (*Staatliches Institut für Gesundheit und Umwelt des Saarlandes, D-66117 Saarbrücken, Germany)

      CBS 85, 10-11 (2000) HPTLC-AMD of water samples on silica gel with 33-step gradient from acetonitrile - ammonia to dichloromethane and dichloromethane - acetic acid to n-hexane. Detection via Chrom Biodip (Merck) by dipping in bacteria solution (Bacillus subtilis) followed by incubation at 30 °C over night and spraying with MTT-tetrazolium salt reagent followed by incubation at 30 °C for 5-30 min. Visual evaluation.

      Classification: 28a, 37
      97 052
      Determination of amitrol in water by AMD
      E. PLASS, A. Kinast (*Bayer Industry Services GmbH&Co. OHG, Bayer Chemistry Park, Building C 601, 41538 Dormagen, Germany. ernst.plass.ep@bayerindustry.de

      CBS 96, 2-5 (2006). AMD-HPTLC of amitrol in water samples, on LiChrospher silica gel pre-washed by immersion for 8 h in 1 % formic acid in methanol and drying over night in a desiccator. Development with a 18-step gradient from methanol (saturated with ammonia) to tert. butylmethyl ether over 50 mm. Detection by exposure to HCl vapor followed by dipping into a solution of 0.2 g Bratton - Marshall reagent (N-(1-naphtyl)ethylenediaminedihydrochloride) in 100 mL methanol - dichloromethane 1:4. Visual evaluation. Quantitative determination by absorbance measurement at 490 nm. LOD is 1 ng/spot. Linearity is given in the range of 1 - 10 ng amitrol.

      Classification: 29d
      102 081
      Application of SPE-HPLC-DAD and SPE-TLC-DAD to the determination of pesticides in real water samples
      T. TUZIMSKI (Faculty of Pharmacy, Department of Physical Chemistry, Medical University, Lublin, Poland, tomasz.tuzimski@am.lublin.pl)

      J. Sep. Sci. 31, 3537-3542 (2008). After solid phase extraction of water samples HPTLC of clofentezine (1), neburon (2), chlorfenvinphos (3), lenacyl (4), trifluralin (5), thiram (6), procymidone (7), flufenoxuron (8), tralkoxydim (9), propaquizafop (10), and dinoseb (11) on silica gel with ethyl acetate – n-heptane 2:8, 3:7, 4:6, or 7:3 as mobile phase. Quantitative determination by absorbance measurement between 200 and 600 nm. Selectivity regarding matrix was given. Linearity was 0.1-1.5 µg/spot for (1), 0.2-1.0 µg/spot for (2), 0.5-1.0 µg/spot for (3), 0.2-1.0 µg/spot for (4), 0.3-9.0 µg/spot for (5), 0.2-1.0 µg/spot for (6), 2.0-11.0 µg/spot for (7), 0.1-2.0 µg/spot for (8), 0.3-1.0 µg/spot for (9), 0.1-1.0 µg/spot for (10), and 0.2-1.0 µg/spot for (11). The limits of detection and quantification were 0.23 and 0.70 µg/spot for (1), 0.06 and 0.18 µg/spot for (2), 0.16 and 0.49 µg/spot for (3), 0.04 and 0.12 µg/spot for (4), 0.06 and 0.18 µg/spot for (5), 0.16 and 0.49 µg/spot for (6), 0.65 and 1.92 µg/spot for (7), 0.10 and 0.31 µg/spot for (8), 0.07 and 0.22 µg/spot for (9), 0.06 and 0.17 µg/spot for (10), and 0.08 and 0.24 µg/spot for (11). The optimal wavelenght for quantification was 278 nm for (1), 249 nm for (2), 247 nm for (3), 273 nm for (4), 277 nm for (5), 281 nm for (6), 208 nm for (7), 268 nm for (8), 284 nm for (9), 245 nm for (10), and 366 nm for (11). Advantages of the technique over the HPLC method are highlighted.

      Classification: 29