ANALYTICAL METHODS FOR THE DETERMINATION OF ORGANOTINS IN THE MARINE-ENVIRONMENT

Citation
Am. Caricchia et al., ANALYTICAL METHODS FOR THE DETERMINATION OF ORGANOTINS IN THE MARINE-ENVIRONMENT, International journal of environmental analytical chemistry, 53(1), 1993, pp. 37-52
Citations number
32
Categorie Soggetti
Environmental Sciences","Chemistry Analytical
ISSN journal
03067319
Volume
53
Issue
1
Year of publication
1993
Pages
37 - 52
Database
ISI
SICI code
0306-7319(1993)53:1<37:AMFTDO>2.0.ZU;2-5
Abstract
Analytical procedures for the determination of organotin compounds in sea water, sediments and mussels have been adopted in our laboratory, intercomparison/certification exercises with other European laboratori es giving satisfactory results. The characteristics of the different m ethodologies are discussed, the balance between practical and analytic al aspects leading to the selection of the following procedures. For w ater samples two alternative extraction techniques are used: liquid/li quid extraction (0.3% tropolone in methylene chloride) or liquid/solid extraction (C18- or Carbopack B-loaded extraction tubes). Solid-phase extraction ensures good results and is more suitable in the field, av oiding high volumes of organic solvents and transport of fragile glass ware. Extraction tubes can be easily stored, and problems with the tra nsfer of whole samples to the laboratory, and storage and conservation problems are prevented. For sediments and mussels, sonication (0.05% tropolone in methanol) can be used as the extraction procedure. Final detection is performed by GC (FPD or MS detection) after pentylation. GC-MS is generally necessary to confirm doubtful results in highly pol luted sediments, particularly if high sulphur levels are present. AAS can be used as an alternative detection technique after selective elut ion from the solid-phase tubes without any derivatization. The detecti on limits are in the low-ppt range for water samples and in the low-pp b range for sediments and mussel samples, with a precision generally b etter than 10% for water samples and better than 15% for sediments and mussels.