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Change of embryotoxic susceptibility to di-n-butyltin dichloride in cultured rat embryos.

Di-n-butylin dichloride (DBTCl), which is commonly used as heat and light stabilizer for polyvinyl chloride (PVC) plastics, is a teratogen in vivo. In the present study, the toxic effects were investigated of DBTCl on cultured rat embryos during three different stages of organogenesis. Rat embryos explanted on gestational day (GD) 8.5, GD 9.5, and GD 11.5 were cultured for 68, 46, and 48 h and were exposed to a range of DBTCl concentrations for the first 24, 46, and the last 46 h of culture, respectively. Significant decreases in the placental diameter at > or = 10 ng/ml and in the number of somite pairs and the morphological score at 30 ng/ml were noted in embryos cultured from GD 8.5. Significant decreases in the yolk sac diameter and the crown-rump length at 100 ng/ml, in the number of somite pairs at > or = 50 ng/ml, and in the morphological score at > or = 30 ng/ml were found in embryos cultured from GD 9.5. No adverse effects on these parameters were detected in embryos cultured from GD 11.5 even at 300 ng/ml. Dysmorphogenesis in embryos cultured from GD 8.5, GD 9.5, and GD 11.5 was observed at > or = 10, > or = 50, and 300 ng/ml, respectively. Incomplete turning and craniofacial defects in embryos cultured from GD 8.5 and GD 9.5 and defects of the forelimb buds and tail in embryos cultured from GD 11.5 were frequently observed. These results show that in vitro exposure to DBTCl interferes with normal development of embryos during three different stages of organogenesis and that susceptibility to the embryotoxicity, including the dysmorphogenic potential of DBTCl, varies with developmental stage.

Animals↗

Suppression of uterine decidualization as a cause of implantation failure induced by triphenyltin chloride in rats.

In our previous study, triphenyltin chloride (TPTC1) was found to induce implantation failure, as preimplantation embryonic loss, in rats. In this study, the effects of TPTC1 on the uterine function, as a cause of implantation failure, were determined using pseudopregnant rats. Female rats were given TPTC1 by gastric intubation at 3.1, 4.7, and 6.3 mg/kg on pseudopregnant day (PPD) 0 to PPD 3 and the decidual cell response was induced on PPD 4. The uterine weight on PPD 9 served as an index of uterine decidualization. A significant decrease in the uterine weight, which indicates suppression of the uterine decidualization, was detected at 4.7 and 6.3 mg/kg. In our previous study, these doses induced a significant increase in implantation failure in female rats given TPTC1 on gestational day (GD) 0 to 3. The ovarian weight and number of corpora lutea in the TPTC1-treated groups were comparable to that of the controls. A significant decrease in serum progesterone levels after administration of TPTC1 was found at 4.7 and 6.3 mg/kg. These findings suggest that implantation failure due to TPTC1 may be mediated via the suppression of uterine decidualization and correlated with the reduction in serum progesterone levels.

Animals↗

Effects of gamma-sterilization on butyltin homogeneity and content in sediments: a GC-ICP-MS study.

A GC-ICP-MS method based on extraction and alkylation of butyltins with sodium tetraethylborate was used to quantitatively assess the fate of these analytes in solutions and sediments following exposure to gamma-irradiation. The effects of a 2.5 Mrad sterilization dose on three butyltin species in both methanolic calibration solutions and in sediment matrices were investigated. Although significant losses of tributyltin (TBT, 90%), dibutyltin (DBT, 100%) and monobutyltin (MBT, 80%) were detected in standard solutions prepared in methanol following gamma-irradiation, no species inter-conversion occurred. Some degradation of TBT (38%) and DBT (32%) but no significant change in MBT content was found using a spiked sediment CRM HISS-1. Conversion DBT to MBT in spiked HISS-1 was deduced. Much smaller degradation of TBT (16% loss) and 10% loss of DBT by conversion to MBT (14% gain) was registered using a sediment blend of PACS-2 and HISS-1 (SOPH). Despite some initial losses of TBT and DBT due to irradiation, better than 2% RSD in both TBT and DBT concentrations measured in twelve different bottles of blended sediment SOPH were obtained, indicating the material may be considered homogeneous for these analytes. Results from a long-term five-year stability study of PACS-2 show that all three butyltins are stable during storage at 4 degrees C followed with 2.5 Mrad minimum dose of gamma-irradiation sterilization treatment.

Gamma Rays↗

Traceability of environmental chemical analyses: can theory match practice?

According to the ISO definition, the traceability concept basically implies that measurement data are linked to stated references through an unbroken chain of comparisons, all with stated uncertainties. This concept may be quite clear in theory, but we may wonder how it may be applicable to complex chemical measurements such as environmental chemical analyses in practice. This paper discusses this issue, giving some examples of drawbacks that are being faced in different environmental sectors (water, sediment, soil, biota and particulate atmospheric samples).

Environmental Monitoring↗

Monitoring dibutyltin and triphenyltin in fresh waters and fish in the United States using micro-liquid chromatography-electrospray/ion trap mass spectrometry.

There is a growing body of evidence that toxic organotins are making their way into terrestrial and aquatic mammals including humans. In the United States, one possible route of environmental exposure to organotins (specifically dibutyltin and triphenyltin) is via fresh surface waters and fish taken from those waters. A unique methodology was used for quantitative and speciation of the organotins. This green-chemistry method combines two extraction techniques (solid-phase extraction for waters; hexane/tropolone extraction for fish) with micro-liquid chromatography-electrospray/ion trap mass spectrometry (micro-LC-ES/ITMS) as the detection method. A small survey looking for organotins in fresh surface waters across the United States, and fish from those waters, was conducted. Various concentrations of dibutyltin and triphenyltin were detected in fresh water, ranging from nondetect to 2 ppb, and nondetect to 6 ppb, respectively. In fish dibutyltin and triphenyltin were detected from nondetect to 200 ppb, and nondetect to 400 ppb, respectively.

Animals↗

Analysis of commercial plastination agents.

S3, S6 and S10 are the most commonly used agents for tissue plastination. Surprisingly, their chemical structures are not known. We therefore decided to fully characterize these products by standard analytical methods: multinucleus magnetic resonance, infrared spectroscopy and size exclusion chromatography. These experiments have shown that Biodur S10 is a polydimethylsiloxane with a molecular weight of 27,200 and silanol functionalities, Biodur S6 is tetraethoxysilane, and Biodur S3 is a mixture the main component of which is dibutyltindilaurate.

Chromatography, Gel↗

Lethal and sub-lethal selectivity of fenbutatin oxide and sulfur to the predator Iphiseiodes zuluagai (Acari: Phytoseiidae) and its prey, Oligonychus ilicis (Acari: Tetranychidae), in Brazilian coffee plantations.

Lethal concentration (LC) has been widely used to estimate pesticide toxicity. However, it does not consider the sub-lethal effects. Therefore we included the instantaneous rate of increase in association with LC to estimate population-level effects of the acaricides fenbutatin oxide and sulfur on the predator Iphiseiodes zuluagai and its prey, the phytophagous southern red mite, Oligonychus ilicis. The predator was 32.84x and 17.20x more tolerant to fenbutatin oxide and sulfur, respectively, than its prey, based on LC50 estimates obtained from acute concentration-mortality bioassays. The instantaneous rate of population growth in both mite species decreased with increasing acaricide concentration. Both acaricides provided effective control of O. ilicis at their recommended concentrations, but sulfur drastically compromised the predator populations quickly leading them to extinction due to the low reproductive potential of this species compared with its prey.

Acari↗

Impact of triphenyltin acetate in microcosms simulating floodplain lakes. I. Influence of sediment quality.

Floodplain lakes in the Rhine-Meuse delta of the Netherlands vary considerably in levels of sediment-bound toxicants. Microcosm experiments were done to compare the ecological impact of the fungicide triphenyltin acetate (TPT) between test systems with clean or polluted sediments (10 microcosms each). Differences in sediment quality affected the structure of the aquatic communities that developed in the microcosms. Initially, a faster growth of the macrophyte Elodea nuttallii was observed on the polluted sediments, which contained not only toxicants but also higher organic matter and nutrient levels. Dynamics of TPT concentrations in the overlying water were very similar between the two types of test system. Higher levels of TPT, however, were found in the sediment compartment of the clean sediment systems containing a smaller macrophyte biomass. TPT was very persistent in the sediments. In both test systems representatives of several taxonomic groups showed clear responses to a single application of TPT, although benthic Nematoda were not affected. Although a few differences in the intensity and/or duration of TPT-related population responses were observed between the two types of test system, the background pollutants in the polluted sediment hardly affected the overall sensitivity of the aquatic community to the additional chemical stressor TPT.

Animals↗

Impact of triphenyltin acetate in microcosms simulating floodplain lakes. II. Comparison of species sensitivity distributions between laboratory and semi-field.

The study objectives were to shed light on the types of freshwater organism that are sensitive to triphenyltin acetate (TPT) and to compare the laboratory and microcosm sensitivities of the invertebrate community. The responses of a wide array of freshwater taxa (including invertebrates, phytoplankton and macrophytes) from acute laboratory Single Species Tests (SST) were compared with the concentration-response relationships of aquatic populations in two types of freshwater microcosms. Representatives of several taxonomic groups of invertebrates, and several phytoplankton and vascular plant species proved to be sensitive to TPT, illustrating its diverse modes of toxic action. Statistically calculated ecological risk thresholds (HC5 values) based on 96 h laboratory EC50 values for invertebrates were 1.3 microg/l, while these values on the basis of microcosm-Species Sensitivity Distributions (SSD) for invertebrates in sampling weeks 2-8 after TPT treatment ranged from 0.2 to 0.6 microg/l based on nominal peak concentrations. Responses observed in the microcosms did not differ between system types and sampling dates, indicating that ecological threshold levels are not affected by different community structures including taxa sensitive to TPT. The laboratory-derived invertebrate SSD curve was less sensitive than the curves from the microcosms. Possible explanations for the more sensitive field response are delayed effects and/or additional chronic exposure via the food chain in the microcosms.

Animals↗