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Sediment analysis, environmental lead

A sensitive method for primary amines is shown in reaction 2, leading to the corresponding 7V-benzenesulfonyl-/V-trifluoroacetyl derivatives. These can be determined by GC-ECD using SE-30 columns LOD 1-5 pg, which is about 200 times more sensitive than GC-FID. The method was applied for determination of phenethylamine (33) in urine110. This analysis was performed also by LLE into n-pentane, derivatization to the benzenesulfonamide and GC-FPD using a capillary column recoveries of aliphatic primary amines in urine were 91-107%, RSD 0.2-4.5%111,112. Amines in environmental waters and sediments were determined after LLE with dichloromethane, derivatization with benzenesulfonyl chloride and GC-SIM-MS LOD 0.02-2 pg/L of water and 0.5-50 ng/g of sediment113. [Pg.1065]

The potential of ultrasonic extraction for field-based extractions has been put into use in the industrial hygiene and environmental single-element analysis of, for example, lead from glass fibre filter ambient air samples [13,14] or from lead-based paint, urban dust and river sediment [15] hexavalent chromium from coal fly ash and paint chips [16] and strontium from river sediment [17]. Ultrasonic extraction has also proved effective as a prior step in multi-element determinations of heavy metals. [Pg.49]

Although it is beyond the scope of this article to consider detailed collection and sample preparation procedures for environmental samples, here are some general considerations for speciation analysis of air, water, biological material, and soils/sediments. The collection of samples in air has focused upon the determination of hydrides and methylated compounds of elements such as arsenic, lead, mercury, and tin. The sample may be introduced into a preevacuated container, or with a pump. The analytes may be isolated using cryotrapping techniques or adsorbent cartridges. For best results, it is recommended to collect the entire gas sample in a container, coated... [Pg.1082]

The concentrations of organolead compounds found in the different environmental compartments are often in the pgm, ngl , and ng per g levels for air, water, and sediment and biological tissues, respectively. However, inorganic lead forms can simultaneously be present in the same samples at a 1000-fold higher level. For this reason, the instrumentation necessary to carry out lead speciation analysis in real samples requires the isolation, separation, and sensitive detection of the individual organolead species in the presence of thousands of... [Pg.2467]

Organolead compounds are pollutants in air, water, soil, and sediments. The toxicity of organolead species depends on the organic groups bound to the Pb atom. Lead has four stable isotopes ( Pb, Pb, Pb, and Pb) and isotopic analysis of Pb can be used for geological dating and to track environmental processes and sources of Pb species. [Pg.511]

The convention concluded by the International Commission for the Protection of the Elbe (IKSE), the closure of industrial plants, and the improvement in quality of municipal sewage in the upper regions of the Elbe and its tributaries will undoubtedly lead in the future to an improvement of water quality particularly in this region. The same expectations can also be placed in the extension of new environmental technologies. In the same way, an experimental verification of this forecast can only be obtained from a retrospective analysis of different sample types from the Environmental Specimen Bank, for example sediment, freshwater mussels and fish (bream). [Pg.61]


See other pages where Sediment analysis, environmental lead is mentioned: [Pg.5]    [Pg.417]    [Pg.218]    [Pg.309]    [Pg.202]    [Pg.379]    [Pg.216]    [Pg.11]    [Pg.49]    [Pg.580]    [Pg.1541]    [Pg.313]    [Pg.408]    [Pg.87]    [Pg.225]    [Pg.280]    [Pg.247]    [Pg.1304]    [Pg.1305]    [Pg.829]   


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Environmental analysis

Environmental lead

Sediments analysis

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