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1.
J Chromatogr A ; 1047(1): 69-76, 2004 Aug 20.
Artigo em Inglês | MEDLINE | ID: mdl-15481461

RESUMO

Six laboratories from four different countries participated in the first European interlaboratory comparison exercise within the framework of the "Fate and toxicity of allelochemicals (natural plant toxins) in relation to environment and consumer" (FATEALLCHEM) European Union Project. The study, organized between November 2002 and March 2003, involved the analyses of seven benzoxazinone derivatives in two standard solutions and one purified extract of root material. Results are reported from the first phase of the study that examined the variability associated with different detection methods and different laboratories. The analytical strategies were based on liquid chromatography (LC) with diode array detection, LC coupled to mass spectrometry (MS) and LC coupled to tandem MS. When data from all laboratories were pooled, the relative standard deviation values ranged from 2 to 14% for the determination of target compounds in standard solutions, and between 19 and 47% for the analysis in root material. Comparison of the three detection techniques leads to the conclusion that MS approaches are the most accurate and precise techniques for the determination of benzoxazinone derivatives at ng/microL level in plant material.


Assuntos
Benzoxazinas/análise , Cromatografia Líquida/métodos , Plantas/química , Cromatografia Líquida/normas , Europa (Continente) , Laboratórios
2.
Chemosphere ; 54(8): 1217-24, 2004 Feb.
Artigo em Inglês | MEDLINE | ID: mdl-14664851

RESUMO

Analyses of triolein-containing semipermeable membrane devices (SPMDs) have sometimes been impeded by interferences caused by impurities endemic to triolein that codialyze with the analytes. Oleic acid and methyl oleate have been the most troublesome of these impurities because of their relatively high concentrations in triolein and because significant residues of both can persist even after size exclusion chromatographic (SEC) fractionation. These residues have also been blamed for false-positive signals during bioindicator testing of SPMD dialysates. To prevent these problems, a simple, cost-effective procedure was developed for purifying triolein destined for use in SPMDs: the bulk triolein is repeatedly (6x) partitioned against methanol. Tests of the procedure show that 14C-oleic acid is completely removed from the triolein. After SEC fractionation, dialysates of standard-size SPMDs made with the purified triolein contain less than 5 microg of methyl oleate as compared to sometimes more than 500 microg for dialysates (also after SEC) of SPMDs made with unpurified triolein. Gas chromatographic analyses with flame ionization and electron capture detection show that the purification treatment also greatly reduces the number and size of peaks caused by unidentified contaminants in the triolein. Microtox basic assay of dialysates of SPMDs shows that those made with the purified triolein have lower acute toxicities than dialysates of SPMDs made with unpurified triolein. Yeast estrogen screen (YES) testing of SPMDs fabricated with unpurified and purified triolein demonstrates that the purification process removes all background estrogenic activity.


Assuntos
Monitoramento Ambiental/métodos , Membranas Artificiais , Trioleína/isolamento & purificação , Bioensaio/métodos , Cromatografia em Gel , Diálise , Monitoramento Ambiental/instrumentação , Estrogênios não Esteroides/farmacologia , Ácido Oleico/química , Ácido Oleico/isolamento & purificação , Permeabilidade , Testes de Toxicidade/métodos , Trioleína/farmacologia , Trioleína/toxicidade , Leveduras/efeitos dos fármacos , Leveduras/crescimento & desenvolvimento
3.
Chemosphere ; 50(7): 871-901, 2003 Feb.
Artigo em Inglês | MEDLINE | ID: mdl-12504127

RESUMO

Little is known about the environmental fate of adjuvants after application on the agricultural land. Adjuvants constitute a broad range of substances, of which solvents and surfactants are the major types. Nonionic surfactants such as alcohol ethoxylates (AEOs) and alkylamine ethoxylates (ANEOs) are typically examples of pesticide adjuvants. In view of their chemical structure this paper outlines present knowledge on occurrence, fate and effect on the aquatic and terrestrial environment of the two adjuvants: AEOs and ANEOs. Both AEOs and ANEOs are used as technical mixtures. This implies that they are not one single compound but a whole range of compounds present in different ratios. Structurally both groups of substances have a mutual core with side chains of varying lengths. Each of these compounds besides having the overall ability to distribute between different phases also possesses some single compound behaviour. This is reflected in the parameters describing the fate e.g. distribution coefficient, leaching, run-off, adsorption to soil, degradation and effects of these substances. The adsorption behaviour of ANEOs in contrast to AEOs is particularly variable and matrix dependent due to the ability of the compound to ionise at environmentally relevant pH. Probably because the compounds exceeds high soil adsorption and are easily degradable which is reflected in the low environmental concentrations generally found in monitoring studies. The compounds generally possess low potency to both terrestrial and aquatic organisms. The major environmental problem related to these compounds is the ability to enhance the mobility of other pollutants in the soil column.


Assuntos
Praguicidas/química , Poluentes do Solo/análise , Tensoativos/química , Poluentes Químicos da Água/análise , Adsorção , Agricultura , Animais , Biodegradação Ambiental , Concentração de Íons de Hidrogênio , Praguicidas/análise , Praguicidas/metabolismo , Medição de Risco , Solo , Poluentes do Solo/metabolismo , Relação Estrutura-Atividade , Tensoativos/análise , Tensoativos/metabolismo , Poluentes Químicos da Água/metabolismo
4.
J Chromatogr A ; 957(1): 27-36, 2002 May 24.
Artigo em Inglês | MEDLINE | ID: mdl-12102309

RESUMO

A new LC-MS-MS method for analysis of rainwater has been developed and validated for 53 pesticides, degradation products of pesticides and selected nitrophenols. The method was used to monitor the concentration of pesticides in rainwater at one location near Roskilde, Denmark from February 2000 to August 2000. Sampling was done in periods of up to 4 weeks using a cooled wet-only sampler. Water samples were extracted by solid-phase extraction on Oasis HLB columns. The analysis of the extracts was performed by LC-MS-MS with electrospray ionization. All samples were analysed in negative and in positive ionization mode, respectively for acidic and neutral compounds. All analyses were done in the selected reaction monitoring mode in order to obtain a better signal-to-noise ratio. The method has been validated for the following parameters: recovery, detection limit, uncertainty and linearity. Atrazine, terbuthylazine, isoproturon, mechlorprop and (2-methyl-4-chlorophenoxy)acetic acid were measured at concentrations above 0.100 microg/l, mainly during the period of agricultural use. Nitrophenols were measured at high concentrations all year with peaks in the cold season (February-March).


Assuntos
Cromatografia Líquida de Alta Pressão/métodos , Praguicidas/análise , Chuva , Espectrometria de Massas por Ionização por Electrospray/métodos , Poluentes Químicos da Água/análise , Dinamarca , Reprodutibilidade dos Testes
5.
Environ Toxicol Chem ; 20(7): 1570-8, 2001 Jul.
Artigo em Inglês | MEDLINE | ID: mdl-11434300

RESUMO

The fate of esfenvalerate was investigated by sampling and chemical analysis after spraying of an artificial pond (25 g a.i./ha) and in the laboratory with [14C]esfenvalerate by trapping of 14CO2 and fractionation of the sediment. The effects were investigated on pelagic communities in enclosures in a natural lake and in the laboratory on surface (Cymatia coleoptrata) and sediment (Chironomus riparius) insects. The latter were used in sediment-plus-water and in water-only tests, measuring effects on emergence and mortality. The measurements in the artificial pond indicated exposure concentrations in the surface microlayer, water column, and sediment of 0.4 microgram/L, 0.05 microgram/L, and 9 micrograms/kg dry weight, respectively, two weeks after application. The degradation studies showed a limited mineralization (26.5%) of [chorophenyl-14C]esfenvalerate during 112 d. Part of the substance was transformed to water-soluble compounds (18.1%) or compounds attached to fulvic acids (26.2%), humic acids (14.2%), or nonextractable sediment constituents (8.8%). The formulated product Sumi-Alpha 5 FW caused 100% mortality to Cymatia coleoptrata after surface application of 0.13 g a.i/ha. Effects on zooplankton were recorded at 0.005 microgram/L of esfenvalerate. The 96-h median lethal concentration for first-instar larvae of Chironomus riparius was 0.13 microgram/L, whereas the delayed emergence lowest-observed-effect concentration was 0.8 microgram/L.


Assuntos
Inseticidas/toxicidade , Piretrinas/toxicidade , Poluentes Químicos da Água/toxicidade , Agricultura , Animais , Biodegradação Ambiental , Chironomidae , Besouros , Sedimentos Geológicos , Inseticidas/análise , Larva/crescimento & desenvolvimento , Nitrilas , Dinâmica Populacional , Piretrinas/análise , Piretrinas/metabolismo , Testes de Toxicidade , Poluentes Químicos da Água/análise , Poluentes Químicos da Água/metabolismo , Zooplâncton
6.
Chemosphere ; 41(4): 595-601, 2000 Aug.
Artigo em Inglês | MEDLINE | ID: mdl-10819228

RESUMO

The method of partial order ranking has been used within the environmental area for a variety of purposes as an attractive way of handling complex information. However, the environmental data are often associated with a significant degree of uncertainty. In this investigation the general nature of the influence from data uncertainty on the partial order ranking is analyzed. A Monte Carlo type analysis is performed in which a series of randomly formed data are used to test the influence of data uncertainty. The partial order ranking is interpreted, where the results are transferred to a one-dimensional ranking scale taking into account that not all elements are ranked with the same certainty. A simple general robustness parameter (E) in form of the expected number of comparisons for each ranking element is defined and correlated to the uncertainty analysis results. A simple equation relates E to the number of elements and the number of parameters, respectively. The magnitude of the ranking uncertainty is shown to increase rapidly when the E value decreases below 4-5 comparisons per element. When the E value exceeds 5 the ranking uncertainty becomes nearly constant and independent on the actual E value.


Assuntos
Monitoramento Ambiental , Modelos Estatísticos , Método de Monte Carlo , Medição de Risco , Gestão da Segurança , Xenobióticos
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