Multi-walled carbon nanotubes (MWCNTs), dispersed in suspensions consisting mainly of individual tubes, were used for intratracheal instillation and inhalation studies. Rats intratracheally received a dose of 0.2 mg, or 1 mg of MWCNTs and were sacrificed from 3 days to 6 months. MWCNTs induced a pulmonary inflammation, as evidenced by a transient neutrophil response in the low-dose groups, and presence of small granulomatous lesion and persistent neutrophil infiltration in the high-dose groups. In the inhalation study, rats were exposed to 0.37 mg/m(3) aerosols of well-dispersed MWCNTs (>70% of MWCNTs were individual fibers) for 4 weeks, and were sacrificed at 3 days, 1 month, and 3 months after the end of exposure. The inhalation exposures delivered less amounts of MWCNTs into the lungs, and therefore less pulmonary inflammation responses was observed, as compared to intratracheal instillation. The results of our study show that well-dispersed MWCNT can produce pulmonary lesions, including inflammation.

Fullerene (carbon sixty [C(60)]) has potential industrial and medical applications. In the future, people working in or residing near manufacturing facilities may be exposed to C(60). Therefore, quantitative data on long-term C(60) clearance from the lungs are required. To estimate the clearance rate and deposition fraction of C(60) from inhalation exposure, the C(60) burden in the lungs, liver, and brain of rats was determined after intratracheal instillation and inhalation. Male Wistar rats were intratracheally instilled with different concentrations of a C(60) suspension prepared with Tween 80 (geometric mean [GM] of particle diameter based on number, 18-29 nm; geometric standard deviation [GSD] of particle diameter, 1.5; and doses, 100, 200, and 1000 micrograms per body) or exposed to a C(60) aerosol prepared with nebulizer (GM of particle diameter based on number, 96 nm; GSD of particle diameter, 2.0; and exposure level, 120 μg/m(3)). C(60) burden in the lungs, liver, and brain was determined at various time points (1 h to 6 months) by a newly developed sensitive high-performance liquid chromatography-ultraviolet absorptiometry combined with extraction and concentration of C(60) from the organs. C(60) clearance was evaluated using a 2-compartment model: fast clearance after deposition on lung surface and slow clearance after retention in the epithelium. The detection limit of our analysis method was 8.9 ng/g tissue. Pulmonary C(60) burden decreased with time and depended on the C(60) concentration administered. The concentration of C(60) in the liver and brain was below the detection limit: 8.9 ng/g tissue. The half-life of intratracheally instilled C(60) was 15-28 days. The deposition mass fraction of inhaled C(60) was 0.14. Mode evaluation revealed that most instilled particles could be eliminated by the fast clearance pathway. This finding is consistent with the transmission electron microscopy finding that many particles were present in alveolar macrophages.

A sensitive method for the determination of ultratrace organotin species in seawater is described. The merits and demerits of derivatization methods using Grignard reagent or sodium tetraethylborate (NaBEt4) were evaluated in terms of derivatization efficiency, applicability to the programmed temperature vaporization (PTV) method, and procedural blanks. The sensitivity of the gas chromatography/inductively coupled plasma mass spectrometry (GC/ICPMS) was improved by more than 100-fold by operating the shield torch at normal plasma conditions, compared with that obtained without using it. The absolute detection limit as tin reached subfemtogram (fg) levels. Furthermore, the detection limit in terms of relative concentration was improved 100-fold by using the PTV method, which enabled the injection of a large sample volume of as much as 100 microL without loss of analyte. When the organotin species in seawater were extracted into hexane with a preconcentration factor of 1000 after ethylation with NaBEt4 and a 100 microL aliquot of the extract was injected into the GC, the instrumental detection limit in relative concentration reached 0.01 pg/L in original seawater. Sources of contamination of organotin species during the sample preparation were examined, and a purification method of NaBEt4 was developed. Finally, the method was successfully applied to open ocean seawater samples containing organotin species at the level of 1-100 pg/L.

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