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Fresenius compounds

Minganti V, Capelli R, Depellegrini R (1995) Evaluation of different derivatization methods for the multielement detection of Hg, Pb and Sn compounds by gas chromatography-microwave induced plasma-atomic emission spectrometry in environmental samples. Fresenius Journal of Analytical Chemistry, 351 (4-5) 471 77. [Pg.48]

Jacob J, Kaechee W, and Wagstaffe PJ (1984) Polycyclic aromatic compounds of environmental and occupational importance - their occurrence, toxicity and development of high purity certified reference materials. Part I. Fresenius J Anal Chem 317 101-114,... [Pg.106]

Drapp B., Pauluth D., Krause J., Gauglitz G., The application of the phase transition in nematic liquid crystals for the optical detection of volatile organic compounds, Fresenius J Anal Chem, 1999, 364, 121-127. [Pg.236]

Jaklin, J., Krenmayr, P., Varmuza, K. Fresenius Z. Anal. Chem. 331, 1988, 479 185. Polycyclic aromatic compounds in the atmosphere of Finz (Austria) (in German). [Pg.115]

Baumann H, Heumann KG. 1987. Analysis of organobromine compounds and HBr in motorcar exhaust gases with a GC/microwave plasma system. Fresenius Zanal Chem 327 186-192. [Pg.93]

Begerow J, Jermann E, Keles T, et al. 1995. Passive sampling for volatile organic compounds VOCs in air at environmentally relevant concentration levels. Fresenius Journal of Analytical Chemistry 351(6) 549-554. [Pg.254]

T. Kiffmeyer, H. J. Goetze, M. Jursch and U. Lueders, Trace enrichment, chromatographic separation, and biodegradation of cytostatic compounds in surface water. Fresenius Journal of Analytical Chemistry, 1998,361(2), 185-191. [Pg.123]

Junghans, M. and Pretsch, E. (1997) Estimation of partition coefficients of organic compounds local database modeling with uniform-length structure descriptors. Fresenius Journal of Analytical Chemistry, 359, 88-92. [Pg.110]

Domimrose AM, Figge K. 1988. Analysis of organic trace compounds in the atmosphere and the correlation between meteorological situation and concentration of reference substances. Fresenius Z Anal Chem 332 606-611. [Pg.70]

Bentz, J. W. G., M. Fichtner, J. Goschnick, and H.-J. Ache, Depth-Resolved Speciation of Nitrogen Compounds in Environmental Solids, Fresenius J. Anal. Chem.., 349, 205-207 (1994). [Pg.637]

Schall, C., and K. G. Heumann, GC Determination of Volatile Organoiodine and Organobromine Compounds in Arctic Seawater and Air Samples, Fresenius J. Anal. Chem., 346, 717-722... [Pg.722]

Doll, T. E., F. H. Frimmel, M. U. Kumke, and G. Ohlenbusch, Interaction between natural organic matter (NOM) and polycyclic aromatic compounds (PAC) - comparison of fluorescence quenching and solid phase micto extraction (SPME) , Fresenius J. Anal. Chem., 364, 313-319 (1999). [Pg.1221]

Martin-Esteban A (2001) Molecularly imprinted polymers new molecular recognition materials for selective solid-phase extraction of organic compounds. Fresenius J Anal Chem 370(7) 795-802... [Pg.304]

Latumus F, Giese B, Wiencke C, Adams FC (2000) Low-Molecular-Weight Organoiodine and Organobromine Compounds Released by Polar Macroalgae - The Influence of Abiotic Factors. Fresenius J Anal Chem 368 297... [Pg.394]

Zimmerli B, Zimmerman H. 1980. Gas-chromatographic determination of traces of butyltin compounds (tetra-, tri-, di-) in the air. Fresenius Z Anal Chem 304 23-27. (German)... [Pg.174]

Bosetto, M., Arafaioli, P, Ristori, G. G., and Fusi, P. (1995). Formation of melanin-type compounds from L-tryptophan on Ca-saturated and Al-saturated clays. Fresenius Environ. Bull. 4, 369-374. [Pg.97]

Pedersen, G.A. and Larsen, E.H. (1997) Speciation of four selenium compounds using high performance liquid chromatography with on-line detection by inductively coupled plasma mass spectrometry and flame atomic absorption spectrometry Fresenius J. Anal. Chem., 358, 591-598. [Pg.87]

Kleibohmer, W. and Cammann, K. (1989) Separation and determination of organotin compounds by HPLC and fluorimetric detection in micellar systems. Fresenius J. Anal. Chem., 335, 780-784. [Pg.435]

Schwartz, J., Henze, H. and Thomas, F.G. (1995) Voltammetric speciation of butyltin compounds. 1. An adsorptive cathodic stripping method. Fresenius J. Anal. Chem., 352, 474 178. [Pg.438]

Bergmann, K., U. Rohr, and B. Neidhart. 1994. Examination of the different procedural steps in the determination of organotin compounds in water samples. Fresenius J. Anal. Chem. 349 815-819. [Pg.35]

Binde, F. and H.H. Riittinger. 1997. Isolation and determination of dissolved organic sulfur compounds— development of the organic group parameter DOS. Fresenius J. Anal. Chem. 357 411—415. [Pg.235]

Stachel, B., G. Behringer, andU. Schacht. 1994. Determination of organohalogen compounds and organic carbon as sum parameter in electronic waste. Fresenius J. Anal. Chem. 350 375-378. [Pg.237]

Rosenberg, E., V. Kmetov, and M. Grasserbauer. 2000. Investigating the potential of high-performance liquid chromatography with atmospheric pressure chemical ionization-mass spectrometry as an alternative method for the speciation analysis of organotin compounds. Fresenius J. Anal. Chem. 366 400-407. [Pg.351]

Figure 7. A summary of some P—O—alkyl groups. R1 is P-alkyl and R2 is P-O-Alkyl. The compared compounds belong to the sarin (1 alkyl alkylphosphonofluoridates), the tabun (2 dialkylamino alkyl phosphoramidocyanidates), and the dialkyl methylphosphonate (4) families. There are two peaks (1185-1180cm 1 and 1072-1070ctrr1) in the tabun family (2) spectra in addition to the C-O peaks. These peaks are due to the C-N bond. The dialkyl methylphosphonate compounds (4) listed here are symmetric (R2 = R2 ) (Reproduced by Permission of Springer-Verlag from M. T. Soderstrom, R. A. Ketola, Fresenius J. Anal. Chem., 350, 162-167 (1994), ref. 49)... Figure 7. A summary of some P—O—alkyl groups. R1 is P-alkyl and R2 is P-O-Alkyl. The compared compounds belong to the sarin (1 alkyl alkylphosphonofluoridates), the tabun (2 dialkylamino alkyl phosphoramidocyanidates), and the dialkyl methylphosphonate (4) families. There are two peaks (1185-1180cm 1 and 1072-1070ctrr1) in the tabun family (2) spectra in addition to the C-O peaks. These peaks are due to the C-N bond. The dialkyl methylphosphonate compounds (4) listed here are symmetric (R2 = R2 ) (Reproduced by Permission of Springer-Verlag from M. T. Soderstrom, R. A. Ketola, Fresenius J. Anal. Chem., 350, 162-167 (1994), ref. 49)...
Angerer J, Scherer G, Schaller KH, et al. 1991. The determination of benzene in human blood as an indicator of environmental exposure to volatile aromatic compounds. Fresenius J Anal Chem 339(10) 740-742. [Pg.357]

Rieger R, Ballschmiter K (1995), Fresenius J. Anal. Chem. 352 715-724. Semivolatile organic compounds - polychlorinated dibenzodioxins (PCDD), polychlorinated dibenzofurans (PCDF), polychlorinated biphenyls (PCB), hexachlorobenzene (HCB), 4,4 -DDE, and chlorinated paraffins (CP) - as markers in sewers films"... [Pg.299]

T. Daldrup, F. Susanto, and P. Michalke, Combination of TLC, GLC and HPLC for a rapid detection of drugs and related compounds, Fresenius Z. Anal. Chem., 505 413 (1981). [Pg.136]

Braun AM (1995) Oxidative Degradation of Nitrogen-containing Organic Compounds Vacuum-Ultraviolet (VUV) Photolysis of Aqueous Solutions of 3-Amino-5-Methylisoxazole, Fresenius /. Anal. Chem. [Pg.233]

Schall C. and Heumann K. G. (1993) GC determination of volatile organoiodine and organobromine compounds in Arctic seawater and air samples. Fresenius J. Anal. Chem. 346,717-722. [Pg.1975]

Figure 10. Mg -excited ESCA spectra of some lead compound mixtures, acquired in the region of the kinetic energy corresponding to the Pb 4f (4f5/2 and 4f7/2> peak-doublet transitions. The lack of collinearity among the compcsients and mixtures makes the Kalman filter separation not feasible, (a) Pb02+PbS04 (60 40) (b) Pb02+Pb(C03> (60 40) (c) Pb02+Pb(N03)2+Pb(C03) (35 35 30), (d) Pb02++Pb(C03)+Pb(S04) (20 20 60) (c) pure Pb(C03) (f) pure Pb(S04). (From Fresenius J Anal. Chem (1993) 345 490, with permissirai). Figure 10. Mg -excited ESCA spectra of some lead compound mixtures, acquired in the region of the kinetic energy corresponding to the Pb 4f (4f5/2 and 4f7/2> peak-doublet transitions. The lack of collinearity among the compcsients and mixtures makes the Kalman filter separation not feasible, (a) Pb02+PbS04 (60 40) (b) Pb02+Pb(C03> (60 40) (c) Pb02+Pb(N03)2+Pb(C03) (35 35 30), (d) Pb02++Pb(C03)+Pb(S04) (20 20 60) (c) pure Pb(C03) (f) pure Pb(S04). (From Fresenius J Anal. Chem (1993) 345 490, with permissirai).
Comparison of the Kalman filter resolution of the ESCA spectra of some binary and ternary lead compound mixtures after search for the optimal alignment by simplex, steepest descent and simulated annealing. Nr is the number of iterations of the optimisation until convergence n.c. no convergence.(From Fresenius J Anal. Chem (1993) 345 490, with permission). [Pg.105]

Mazan, S., Cretier, G., Gilon, N., Mermet, J. M., Rocca, J. L. Porous graphitic carbon as stationary phase for LC-ICPMS separation of arsenic compounds in water. Anal Chem 2002, 74, 1281-1287. Bissen, M., Frimmel, F. H. Speciation of As(III), As(V), MMA and DMA in contaminated soil extracts by HPLC-ICP/MS. Fresenius J Anal Chem 2000, 367, 51-55. [Pg.264]

Chau YK, Wong PT (1991) Recent developments in speciation and determination of organometallic compounds in environmental samples. Fresenius J Anal Chem 339, 640-645. [Pg.415]

Franke S, Schwarzbauer J, Francke W (1998a) Arylesters of alkylsulfonic acids in sediments. Part III of organic compounds as contaminants of the Elbe river and its tributaries. Fresenius J Anal Chem 360, 580-588. [Pg.420]


See other pages where Fresenius compounds is mentioned: [Pg.405]    [Pg.99]    [Pg.163]    [Pg.428]    [Pg.206]    [Pg.580]    [Pg.99]    [Pg.2759]   
See also in sourсe #XX -- [ Pg.110 ]




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