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| 1 | A review of liquid chromatography in environmental pesticide analysis显示文摘 | D. Barceló | 1988 | Chromatographia1988，，10： | 1 |
| 2 | Logical foundations of relational data exchange显示文摘 | Barceló P | | 0，，01： | 1 |
| 3 | Environmental protection agency and other methods for the determination of priority pesticides and their transformation products in water显示文摘 | Barceló D | | 0，，： | 1 |
| 4 | Logical foundations of relational data exchange显示文摘 | Barceló P | | 0，，01： | 1 |
| 5 | Plantwaterrelationsasaffectedbyheavymetalstress:areview显示文摘 | BarcelóJ PoschenriederC | 1990 | JPlantNutr1990，13，： | 1 |
| 6 | Diffusion-weighted whole-body MR screening显示文摘 | Vilanova JC Barceló J | 2008 | Eur J Radiol2008，67，： | 1 |
| 7 | Determination of Phenolic Compounds in Water and Waste Water显示文摘 | Puig D Barceló D | 1996 | Trends in Analytical Chemistry1996，15，8： | 1 |
| 8 | Are red leaves photosynthetically active?显示文摘 | F. Pomar A. Ros Barceló | 2007 | Biologia Plantarum2007，，4： | 1 |
| 9 | Diffusion-weighted whole-bodyMR screening显示文摘 | Vilanova JC Barceló J | 2008 | Eur J Radiol2008，67，3： | 1 |
| 10 | Are red leaves photosynthetically active?显示文摘 | F. Pomar A. Ros Barceló | 2007 | Biologia Plantarum2007，，4： | 1 |
| 11 | Sample handling and analysis of allelochemical compounds in plants显示文摘 | Eljarrat E Barceló D | | 0，，10： | 1 |
| 12 | Strengths and limitations of immunoassays for effective and efficient use for pesticide analysis in water samples:A review显示文摘 | Hennion M-C Barceló D | 1998 | Anal Chim A cta1998，362，： | 1 |
| 13 | Quantitative analysis of polychlorinated n-alkanes in environmental samples显示文摘 | Eljarrat E BarcelóD | 2006 | Trends in Analytical Chemistry2006，25，： | 1 |
| 14 | Determinationof39polybrominateddiphenylethercongenersinsedimentsamplesusingfastselectivepressurizedliquidextractionandpurification显示文摘 | delaCalA EljarratE BarcelóD | 2003 | JournalofChromatographyA2003，1021，1： | 1 |
| 15 | Phytoremediation:principles and perspectives显示文摘 | Barceló J Poschenrieder C | 2003 | Contributions to Science2003，2，3： | 1 |
| 16 | Determination and stability of pesticides in freeze-dried watersamples by automated on-line solid-phase extraction followedby liquid chromatography with diode-array detection显示文摘 | FERRER I BARCELó D | 1996 | Journal of Chromatography A1996，，737： | 1 |
| 17 | Quantitative analysis of polychlorinated n -alkanes in environmental samples显示文摘 | E. Eljarrat D. Barceló | 2006 | Trends in Analytical Chemistry2006，，4： | 1 |
| 18 | Quantitative analysis of polychlorinated alkanes in environmental samples显示文摘 | Eljarrat E Barceló D | 2006 | Trends Anal Chem2006，25，： | 1 |
| 19 | Diffusion-weighted whole-body MR screening显示文摘 | Vilanova JC Barceló J | | 0，，3： | 1 |
| 20 | Formation of iodo-trihalomethanes, iodo-haloacetic acids, and haloacetaldehydes during chlorination and chloramination of iodine containing waters in laboratory controlled reactions显示文摘Iodine containing disinfection by-products(I-DBPs) and haloacetaldehydes(HALs) are emerging disinfection by-product(DBP) classes of concern. The former due to its increased potential toxicity and the latter because it was found to be the third most relevant DBP class in mass in a U.S. nationwide drinking water study. These DBP classes have been scarcely investigated, and this work was performed to further explore their formation in drinking water under chlorination and chloramination scenarios. In order to do this, iodo-trihalomethanes(I-THMs),iodo-haloacetic acids(I-HAAs) and selected HALs(mono-HALs and di-HALs species, including iodoacetaldehyde) were investigated in DBP mixtures generated after chlorination and chloramination of different water matrices containing different levels of bromide and iodide in laboratory controlled reactions. Results confirmed the enhancement of I-DBP formation in the presence of monochloramine. While I-THMs and I-HAAs contributed almost equally to total I-DBP concentrations in chlorinated water, I-THMs contributed the most to total I-DBP levels in the case of chloraminated water. The most abundant and common I-THM species generated were bromochloroiodomethane, dichloroiodomethane, and chlorodiiodomethane. Iodoacetic acid and chloroiodoacetic acid contributed the most to the total I-HAA concentrations measured in the investigated disinfected water. As for the studied HALs, dihalogenated species were the compounds that predominantly formed under both investigated treatments. | Cristina Postigo Susan D.Richardson Damia Barceló | 2017 | Journal of Environmental Sciences2017，29，8： | 4 |
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