Skin transferability of phthalic acid ester plasticizers and other plasticizers using model polyvinyl chloride sheets.

The transferability of phthalic acid esters (PAEs) and other plasticizers, from model polyvinyl chloride (PVC) sheets to the skin of 11 subjects was assessed by measuring the amount of substance transferred using PVC sheets containing PAEs and alternative plasticizers of different types and contents. For all subjects, the transferred amount, from sheets containing 28 wt% PAE or from mixed sheets containing 14 wt% each of di (2-ethylhexyl) phthalate (DEHP) and other PAE, was greater than that from sheets containing 15 wt% each of PAE or alternative plasticizer only. A comparison of the transferability of five types of PAE showed that transfer tended to occur more readily as the n-octanol-water partition coefficient increased, suggesting that PAE hydrophobicity affected its transferability. The transferability of the alternative plasticizers di(2-ethylhexyl) terephthalate and 1,2-cyclohexane dicarboxylic acid diisononyl ester showed a similar trend; however, the transferred amount tended to be higher from model PVC sheets containing 28 wt% PAE or mixed with DEHP. The transferability of PAEs and alternative plasticizers was higher for certain subjects, suggesting individual differences in the transferability of chemicals to the subject's skin surface and is the presence of a group of people comparatively more susceptible to such transfer.

Analysis of glycols, glycol ethers, and other volatile organic compounds present in household water-based hand pump sprays.

The aim of this investigation is to clarify the types and concentrations of VOCs present in various commercial household water-based hand pump spray products used in Japan, and to estimate their average concentrations in indoor air when the spray product is used. We selected glycol and glycol ethers as the main target compounds, as these chemicals were detected at high frequencies and concentrations in a national survey of Japanese indoor air pollution. The extraction of these chemicals using graphite carbon cartridges was examined, with good recoveries and reproducibilities being obtained. Eighteen chemicals were analyzed in 54 commercial products and 8 chemicals were detected. More specifically, dipropylene glycol (DPG) was present in 44 samples (1.1 × 101-1.8 × 104 µg/mL); propylene glycol (PG) was present in 22 samples (1.5 × 101-2.9 × 104 µg/mL); diethylene glycol monoethyl ether (DGMEE) was found in 15 samples (trace amount-1.9 × 103 µg/mL); diethylene glycol (DEG) was present in 9 samples (1.0 × 101-2.4 × 103 µg/mL); 1,3-butandiol (13BG) was found in 5 samples (trace amount-7.4 × 103 µg/mL); 2-ethyl-1-hexanol (2E1H) was detected in 5 samples (3.2 × 10-1-4.4 × 101 µg/mL); diethylene glycol monobutyl ether (DGMBE) was present in 4 samples (2.1 × 101-7.1 × 101 µg/mL); and 3-methoxy-3-methylbutanol (MMB) was found in 2 samples (2.4 × 101-4.7 × 102 µg/mL). In addition, the average concentrations of these chemicals in indoor air were estimated using their maximum concentrations observed in the spray product. The estimated average concentrations of the chemicals in indoor air were determined to range between 1.0 × 10-2 and 1.0 mg/m3, with the exception of 2E1H and DGMBE. Furthermore, the estimated average concentrations of PG, 13BG, and DGMEE in indoor air were comparable to or higher than those reported in a national survey of Japanese indoor air pollution. It therefore appeared that household water-based hand pump sprays may contribute to the presence of these chemicals in indoor air. In contrast, estimated average concentrations of 2E1H in indoor air were low, its concentrations observed in a national survey of Japanese indoor air pollution are likely due to the use of plasticizers and paints.

Particle size distribution of aerosols sprayed from household hand-pump sprays containing fluorine-based and silicone-based compounds.

Japan has published safety guideline on waterproof aerosol sprays. Furthermore, the Aerosol Industry Association of Japan has adopted voluntary regulations on waterproof aerosol sprays. Aerosol particles of diameter less than 10 µm are considered as "fine particles". In order to avoid acute lung injury, this size fraction should account for less than 0.6% of the sprayed aerosol particles. In contrast, the particle size distribution of aerosols released by hand-pump sprays containing fluorine-based or silicone-based compounds have not been investigated in Japan. Thus, the present study investigated the aerosol particle size distribution of 16 household hand-pump sprays. In 4 samples, the ratio of fine particles in aerosols exceeded 0.6%. This study confirmed that several hand-pump sprays available in the Japanese market can spray fine particles. Since the hand-pump sprays use water as a solvent and their ingredients may be more hydrophilic than those of aerosol sprays, the concepts related to the safety of aerosol-sprays do not apply to the hand pump sprays. Therefore, it may be required for the hand-pump spray to develop a suitable method for evaluating the toxicity and to establish the safety guideline.

[Polyploidy induction by spherical size standard polystyrene particles in a Chinese hamster cell line CHL].

To investigate relationships between particle (as a model of aggregates) size in a nanomaterial test suspension and its cytotoxicity, a series of eleven sizes of polystyrene (PS) particles were tested in the cytotoxicity test and the chromosome aberration test by using a Chinese hamster cell line CHL. The PS particles were spheres with defined diameters ranging from 0.1 to 9.2 µm. A series of eight sizes of particles with diameters ranging from 0.92 to 4.45 µm showed stronger cytotoxicity than the others. There was a marked difference in cytotoxicity between the 4.45- and 5.26-µm particles. The 0.92- to 4.45-µm particles did not induce structural chromosome aberrations but induced a high frequency of polyploidy in the chromosome aberration test. The 5.26-µm particles showed very weak induction of polyploidy. The incorporation of the 4.45-µm particles into CHL cells was observed by scanning electron microscopy (SEM). Some cells incorporated more than 10 particles. The semi-quantitative measurement of incorporation of particles into cells was performed by flow cytometry with a parameter of side scattered light (SSC) intensity. It showed that CHL cells preferably incorporated the 4.45-µm particles to the 5.26-µm particles. These findings suggest that CHL cells may have a kind of size-recognition ability and incorporate a particular size of particles. The particles may prevent a normal cytokinesis resulting in polyploidy induction. Nanomaterials also may show size-dependent toxicity. Data on particle (or aggregate) size distribution in the test suspension should be provided to evaluate properly the results of toxicity tests of nanomaterials.

Analysis of isothiazolinone preservatives in polyvinyl alcohol cooling towels used in Japan.

Recently, cases of contact dermatitis that were related to the use of polyvinyl alcohol (PVA) cooling towels containing isothiazolinone preservatives were reported in Japan. The aim of this investigation was to analyze the concentrations of five different isothiazolinone compounds present in PVA towels and to assess the effectiveness of washing in removing the preservatives from new towels prior to being used for the first time. Twenty-seven PVA towels were used in this study. Two groups (i.e., laboratory-simulation and volunteer) of washing experiments were conducted to evaluate the effect of washing procedures. Qualitative and quantitative analyses were performed by LC/MS/MS, which detected 2-methyl-4-isothiazolin-3-one (MI) and 5-chloro-2-methyl-4-isothaizolin-3-one (CMI) in 23 samples (MI: 0.29-154 µg g-wet(-1), CMI: 2.2-467 µg g-wet(-1)), 2-n-octyl-4-isothiazolin-3-one (OIT) in one sample (478 µg g-wet(-1)). The compounds 4,5-Dichloro-2-n-octyl-4-isothiazolin-3-one (2Cl-OIT) and 1,2-benzisothiazolin-3-one (BIT) were not detected in all samples. We confirmed the presence of residual MI, CMI, and OIT in the washed towels, and the residual-to-original content ratio of OIT was higher than that of MI and CMI in PVA towels, due to the higher hydrophobicity of OIT than MI and CMI. A concern has been raised about the occurrence of contact dermatitis being caused by the use of PVA towels. It is suggested that a detailed description of isothiazolinone preservatives in PVA towels and an effective washing procedure for the removal of these preservatives should be provided by the manufacturer. Further, alternative non-sensitizing preservatives might be considered for the manufacture of PVA cooling towels in the future.

[Examination of identification test of certain aromatic amines originating from azo colorants in textile and leather products using high performance liquid chromatography].

Azo colorants that generate primary aromatic amines (PAAs) have been recently deliberated as a controlled harmful substance by the "Act on the Control of Household Products Containing Harmful Substances" in Japan. Therefore, we examined an identification test for 22 kinds of PAAs originating from the azo colorants in commercial textile products and leather products using high performance liquid chromatography (HPLC). When a PAAs standard solution containing 2,4-xylidine and 2,6-xylidine was analyzed using the condition according to EN14362-1:2012 at 240 nm as a basic condition, we observed enough separation for all the PAAs to identify. However, in the some sample solutions, the peaks of several PAAs were overlapped with the interference peaks, and their identifications were difficult. In these cases, some PAAs were able to identify by alteration to suitable wavelength. Furthermore, the retention time of almost PAAs and interference peaks were changed by using acetonitrile as the organic solvent in eluent or phenyl type column. These modifications were helpful for identification of PAA which was overlapped to interference substances by the basic condition. Thus, we suggest the HPLC condition for an identification test is in accordance to that described in EN14362-1:2013. And we propose that the HPLC condition can be modified as necessary.

[Characterization of cases contravening of regulations regarding primary aromatic amines originating from azo dyes in commercial textile products and leather products in European Union].

Contraventions of regulations regarding primary aromatic amines (PAAs) originating from azo dyes in commercial textile products and leather products in European Union (EU), notified in the period between 2006 and 2012 were collected from the Rapid Alert System for non-food consumer products (RAPEX), were characterized. Various types of products (clothes, footwear, bedding, etc.) and their raw materials (cotton, silk, viscose, leather, etc.) were reported to have contravened the regulations. The contravention frequencies for products made in China and India were higher than those for other countries. Ten percentage of the country in which the reported products were produced was unknown. The notification frequencies for benzidine and 4-aminoazobenzene were higher than those for other PAAs. Contravention of regulations regarding benzidine, 4-aminoazobenzene, and 3,3'-dimethoxybenzidine were notified every year. Contraventions of regulations regarding five PAAs--classified as IARC group 1--were notified one or several times. Since the scale of the survey conducted in Japan were small compared with RAPEX, it is necessary that many kinds and number of products should be surveyed in Japan. In addition, it is also necessary to pay attention to 4-aminoazobenzene, while it has not been detected in the previous studies conducted in Japan.

Effect of secondary particle size of nickel oxide nanoparticles on cytotoxicity in A549 cells.

The effect of nanoparticle type, shape, as well as primary and secondary particle size on toxicity remains poorly characterized. In this study, suspensions of nickel oxide (NiO) nanoparticles with the same primary particle size (< 50 nm) but different secondary particle sizes were prepared, and their cytotoxicity was investigated. A planetary ball mill wet nanopulverizer with zirconium milling balls of decreasing sizes (φ: 0.5, 0.1, and 0.05 mm) yielded NiO nanoparticles of decreasing mean particle size (310.4 ± 6.7, 172.0 ± 2.8, and 102.0 ± 0.5 nm). Stock solutions were diluted to various concentrations in 10% heat-inactivated fetal bovine serum containing minimum essential medium, and shown to have the same primary particle size, but different secondary particle sizes. Tests with A549 cells revealed that cytotoxicity increased with increasing secondary particle size: milling ball diameter φ 0.05 mm (IC50: 148 µg/mL) < φ 0.1 mm (IC50: 83.5 µg/mL) < φ 0.5 mm (IC50: 33.4 µg/mL). Uptake experiments indicated that the intracellular amount of Ni increased with increasing secondary particle size. In summary, the present findings show that differences in secondary particle size affected the cytotoxicity of NiO suspensions, which could be ascribed at least in part to differences in the amount of NiO taken up by the cells.

[Investigation and Improvement of Techniques That Affect the Amount of Dispersal during Preparation of Anticancer Drugs].

Many healthcare workers who handle anticancer drugs are at risk for occupational exposure. However, there are no established permissible limits for occupational exposure to anticancer drugs; thus, in this study, we aimed to search for and improve procedures that have a greater impact on the amount of spatter for handling anticancer drugs in vials, which are frequently used, based on the quantitative evaluation of the amount of exposure. We used sodium riboflavin phosphate (FMN) as a simulated anticancer drug and measured the amount of FMN dispersed to the handling area by the wiping method and the amount of FMN dispersed in both gloves using high-performance liquid chromatography with fluorescence detection (HPLC-FL). In this study, it was suggested that the overall amount of dispersal in the preparation process was affected by the different methods of injecting the drug solution into the infusion bottles and whether recapping. It was also found that the variation in the amount of dispersal differed depending on the selected preparation technique. It was suggested that the amount of dispersal could be reduced by selecting an appropriate dissolution method for multiple vials, recapping, an appropriate method for injecting the drug into the infusion bottle, and properly preparing the internal pressure of the infusion bottle. The results of this study suggest that there are some techniques and procedures in the preparation process of vials that have a significant effect on the amount of dispersal, and that proper implementation of these techniques can contribute to the reduction of dispersal.

Quantitative comparison of anticancer drug dispersal before and after introducing appropriate preparation procedures during anticancer drug preparation.

BACKGROUND: In Japan, engineering controls for preparing injectable anticancer drugs are inadequate and compliance with appropriate preparation procedures is vital. In this study, we evaluated the effects of adherence to appropriate anticancer drug formulation and packaging procedures on reducing anticancer drug dispersal in clinical practice, especially in Japan. METHODS: We quantitatively evaluated the effectiveness of implementing procedures that were experimentally verified to help reduce the amount of anticancer drug dispersed during preparation based on procedures described in the "Anticancer Drug Preparation Manual." The target facilities were four regional hub hospitals in the Kanto area. Contamination of sheets and gloves with 5-fluorouracil (5-FU) and gemcitabine (GEM) in a safety cabinet during formulation was evaluated using wipe tests. Subsequently, the proper preparation procedure was shown on a video, training was provided, and the wipe tests were repeated. RESULTS: Forty-one and 39 pharmacists were engaged in drug preparation before and after intervention, respectively. 5-FU had the highest dispersal per prepared vial on the sheet before intervention. The dispersal amount per prepared vial decreased significantly (P = 0.01) after intervention. The amount of GEM dispersed before and after intervention did not differ significantly. However, the percentage of sheets below the detection limit after intervention was 62%, increasing from 46% before intervention. The amount dispersed on gloves was not significantly reduced by proper preparation technique. Although not explicitly noticeable and quantifiable, pharmacists must consider that a significant amount of anticancer drug is dispersed on gloves despite following appropriate preparation procedures. CONCLUSIONS: Quantitative amounts of anticancer drugs dispersed in the preparations of 5-FU and GEM were found in our study. The difference in the amount of contamination before and after intervention was significantly reduced only for the contamination of sheets with 5-FU. There was no decrease in the amount of glove contamination. There was also no difference between medical facilities. Despite following appropriate preparation procedures, dispersed amounts cannot be maintained below the detection limit, indicating the need for a combination of education and engineering controls.

Analysis of phthalic acid diesters, monoester, and other plasticizers in polyvinyl chloride household products in Japan.

The aim of this study was to determine the concentrations of six phthalic acid diesters (PAEs) [di(2-ethylhexyl) phthalate (DEHP), di-n-butyl phthalate (DBP), butyl benzyl phthalate (BBP), diisononyl phthalate (DINP), di-n-octyl phthalate (DNOP), and diisodecyl phthalate (DIDP)], two non-phthalic plasticizers [di(2-ethylhexyl) adipate (DEHA), 2,2,4-trimethyl-1,3-pentanediol diisobutylate (TMPDIB)], and mono 2-ethylhexyl phthalate(MEHP) in polyvinyl chloride (PVC) household products that children often places in their mouths and/or contact with their skin (41 products, 47 samples) in Japan. The detection frequencies of the studied compounds were as follows: DEHP (79 %), DINP-2 (13 %), DINP-1 (11 %), DBP (8.5 %), DEHA (8.5 %), DIDP (4.3 %), and DNOP (2.1 %). Concentrations of these compounds ranged from 0.021 % to 48 %. BBP and TMPDIB were not detected in the all samples. Most samples contained DEHP and DINP at high concentrations over 0.1 %. High concentrations of PAEs were detected in PVC household products that appear appealing to children and can possibly be licked and chewed by them. Di(2-ethylhexyl) terephtalete, diisononyl 1,2-cyclohexanedicarboxylic acid, acetyl tributyl citrate, and di(2-ethylhexyl) 4-cyclohexene-1,2-dicarboxylate used as substitute plasticizers were also detected in several samples. MEHP was present in 70 % of the samples, with concentrations ranging from trace amounts to 140 µg/g. The ratios of MEHP against DEHP were 6.2 × 10(-4) to 1.6 × 10(-1) %. MEHP in the household products investigated in this study was most probably an impurity in DEHP. The high concentrations of PAEs detected in products that children often place in their mouth reveal the importance of replacing plasticizers in common household products, and not just children's toys, with safer alternatives.

Analysis of primary aromatic amines originated from azo dyes in commercial textile products in Japan.

The purpose of this study was to clarify the actual condition of 26 types of carcinogenic primary aromatic amines (PAAs) originated from azo dyes in commercial textile products in Japan. In the case of textiles made of various fibers of various colors, the fibers were separated by color and analyzed. A total of 86 textile products (117 samples) were analyzed. Twenty-one kinds of PAAs were detected in the samples and almost all the PAAs were detected at low concentrations. However, the concentrations of benzidine, 3,3'-dimethoxybenzidine, and 2,4-diaminotoluene (56-440 µg g⁻¹) in placemats made of cotton were found to exceed EU regulation limits of 30 µg g⁻¹. Although such placemats do not always come into contact with the user's skin, it is thought that they should be handled more carefully. Finally, 7 products (8 samples) contained PAAs at concentrations that exceeded the regulation limits. Two sample preparation methods (with and without solvent extraction) were performed on the same sample in order to compare the PAAs in samples in which it is difficult to separate the component materials, such as a cotton fabric that contained polyester fibers. In a comparison of the results obtained from the two methods, it was observed that the concentrations and/or kinds of PAAs detected in the samples were different. It was therefore thought that textile products that present this particular challenge should be analyzed by both methods.

[Comparative study of Acid extraction tests of metal products containing lead].

The international standard ISO 8124-3: 1997 "Safety of toys -Part 3: Migration of certain elements" and "Interim Enforcement Policy for Children's Metal Jewelry Containing Lead- 2/3/2005" by the U.S. Consumer Product Safety Commission (CPSC) to control the amount of eluted lead from metal accessories cannot be simply compared, because the acid extraction methods and the limit values are different from each other. Therefore acid extraction tests based on the ISO standard and the CPSC policy were conducted and the amounts of eluted lead from small metal products were compared between both tests. There was less eluted lead in the ISO method than in the CPSC method. Moreover, the amount of eluted lead in the ISO method did not even reach that of the first elution in the CPSC method. It became clear that the acid extraction test of the ISO standard was not as good as that of the CPSC policy, because of the difference in test conditions. In 16 small metal products, seven products were unsuitable for the ISO standard and 14 products were unsuitable for the CPSC policy; however, all these products were originally inapplicable to the ISO standard and the CPSC policy. The calculation grounds of the limit values were also different between the ISO standard and the CPSC policy. The standardization of an acid extraction test that simulates the lead elution to gastric juice is required so as to prevent adverse health effects in children due to their accidental ingestion of small metal products containing lead.

Analytical method for tributyltin and triphenyltin contained in household products-preparing for the revision of authorized analytical method-.

In preparing for the revision of the authorized analytical method for tributyltin (TBT) and triphenyltin (TPT), which are banned from using according to the "Act on the Control of Household Products Containing Harmful Substances", an examination was conducted on the detection method of these substances using gas chromatography/mass spectrometry (GC/MS), after derivatizing them (ethyl-derivatizing method and hydrogen-derivatizing method). Ethyl-derivatized compounds had stability, which enabled the detection of TPT with a higher sensitivity. In addition, a preparation suitable for the following analytical objects was established: (1) textile products, (2) water-based products (such as water-based paint), (3) oil-based products (such as wax), and (4) adhesives. Addition-recovery experiments were conducted using the prescribed pretreatment method, when each surrogate substances (TBT-d27, TPT-d15) were added and the data were corrected, good recovery rates (94.5-118.6% in TBT, and 86.6-110.1% in TPT) were obtained. When TBT and TPT in 31 commercially available products were analyzed based on the developed analytical method, an adhesive showed 13.2 microg/g of TBT content, which exceeded the regulatory criterion (1 microg/g as tin). Next, when the same products with different manufacturing date were analyzed, TBT (10.2-10.8 microg/g), which exceeded the regulatory criterion, was detected in 4 products among 8 products, and simultaneously, a high concentration (over 1000 microg/g) of dibutyltin (DBT) was detected. It was suggested that TBT as an impurity of DBT remained, and the manufacturer chose the voluntary recall of the product. The new method is considered sufficiently applicable as a revised method for the conventionally authorized method.

[Determination of organotin compounds in water soluble paints and adhesives by GC-MS].

The use of tributyltin (TBT) and triphenyltin (TPT) in some household products are prohibited by "Act on the Control of Household Products Containing Harmful Substances" in Japan. In this study, methods for determination of TBT and TPT in water soluble paints and adhesives were developed by GC-MS. These compounds in paints and adhesives, which were mainly composed of vinyl acetate, urethane and acryl resins, and chloroprene rubber, were firstly extracted with HCl-acetone, and then extracted with hexane. On the other hand, the adhesive composed of natural rubber was firstly dispersed in water before acidification. The organotins were extracted with hexane from this solution and then these compounds were extracted with acetonitrile from hexane extract. These extracts were purified by a florisil cartridge column after ethyl-derivation with sodium tetraethylborate, and analyzed by GC-MS. The quantifications using deuterated compound of both organotins as surrogate standard were conducted, and good results were obtained. The recoveries were 81 to 118% and the coefficients of variation were 0.83 to 4.3% (TBT and TPT added; 5 microg/g). The method quantification limits were 0.0090 to 0.025 microg/g, which were lower than those of an official method. These methods were applied to monobutyltin (MBT), dibutyltin (DBT), monophenyltin (MPT), and diphenyltin (DPT). DBT and DPT in paints and adhesives were quantified, except for DPT in natural rubber. These methods were applied to commercial products. DBT was detected at low concentrations (t.r.-0.19 microg/g) in some paint samples, while TBT and TPT were not detected in all samples.

Evaluation of the sensitization potential of volatile and semi-volatile organic compounds using the direct peptide reactivity assay.

The purpose of this study was to evaluate the sensitization potential of 82 compounds classified as volatile and/or semi-volatile organic compounds using the direct peptide reactivity assay (DPRA), given that these chemical compounds have been detected frequently and at high concentrations in a national survey of Japanese indoor air pollution and other studies. The skin sensitization potential of 81 of these compounds was evaluable in our study; one compound co-eluted with cysteine peptide and was therefore not evaluable. Twenty-five of the evaluated compounds were classified as positive. Although all glycols and plasticizers detected frequently and at high concentrations in a national survey of Japanese indoor air pollution were negative, hexanal and nonanal, which are found in fragrances and building materials, tested positive. Monoethanolamine and 1,3-butanediol, which cause clinical contact dermatitis, and several compounds reported to have weak sensitization potential in animal studies, were classified as negative. Thus, it was considered that compounds with weak sensitization potential were evaluated as negative in the DPRA. Although the sensitization potential of the formaldehyde-releasing preservative bronopol has been attributed to the release of formaldehyde (a well-known contact allergen) by its degradation, its degradation products-bromonitromethane and 2-bromoethanol-were classified as positive, indicating that these degradation products also exhibit sensitization potential. The compounds that tested positive in this study should be comprehensively assessed through multiple toxicity and epidemiological studies.

[Serious product accidents due to the chemical substances used in household products in fiscal years 2007 and 2008].

The revised consumer product safety law was enforced in 2007. Then, the collection and publication system of the information of product accidents was newly included. Serious product accidents due to the chemical substances used in household products had 32 cases in fiscal years 2007 and 2008. These household products were a desk mat, a sectional bed, a spray-type adhesive, a paint and an adhesive for table tennis rackets. The safety measure of the household product was explained based on the law for the control of household products containing harmful substances.

A novel candidate compound with urethane structure for anticancer drug development.

Diethyl-4,4'-methylenebis(N-phenylcarbamate) (MDU) is a urethane compound that we originally synthesized, along with three other compounds, to investigate how polyurethane is hydrolysed. We tested the four compounds for cytotoxicity in two Chinese hamster cell lines (CHL and V79) and a human cancer cell line (HeLa S3). MDU showed the strongest cytotoxicity in all the cell lines with an IC50 of around 0.1 microg/ml. We further investigated MDU for its ability to induce chromosome aberrations (CAs) and micronuclei (MN) in CHL cells. MDU induced around 100% polyploid cells at 0.5 microg/ml after 24- and 48-h treatment in the CA test and a significantly increased frequency of micronuclei, polynuclear cells, and mitotic cells in the MN test, suggesting that it may induce numerical CAs. MDU's ability to cause mitotic arrest in CHL cells was greater than that of taxol and colchicine. Based on a COMPARE analysis using JFCR39, a panel of cancer cell lines, we predicted MDU to be a tubulin inhibitor. We confirmed this possibility in nerve growth factor-stimulated PC12 cells as well as in HT1080 cells, in which MDU exhibited the activity to inhibit tubulin polymerization. MDU is simpler in structure than existing anticancer drugs taxol and vincristine and can be synthesized relatively easily. Here we offer MDU as a potential new type of anticancer drug, stable even at room temperature, and inexpensive.

Hepatotoxicity and Drug/Chemical Interaction Toxicity of Nanoclay Particles in Mice.

Nanomaterials are relatively new and unconventional materials with many useful properties, but their effects on biological systems are poorly understood. Nanoclay is a general term for layered mineral silicate nanoparticles that are ideally suited for use in clay-based nanocomposites. The potential biological hazards of nanoclays have not been addressed, however. Therefore, we investigated the in vivo effects and drug interactions of nanoclays. In mice, administration of nanoclay particles via the tail vein led to acute liver injury. Co-administration of nanoclay and carbon tetrachloride, paraquat, or cisplatin resulted in both liver and kidney injury. Our findings thus indicate that nanoclay particles are potentially hepato- and nephrotoxic.

In vitro induction of polyploidy and chromatid exchanges by culture medium extracts of natural rubbers compounded with 2-mercaptobenzothiazole as a positive control candidate for genotoxicity tests.

We tested extracts of custom-made natural rubber samples for cytotoxicity using V79 cells and for chromosome aberration (CA) induction using CHL cells in compliance with the Japanese guidelines for basic biological tests of medical materials and devices. The samples were formulated with a high level of 2-mercaptobenzothiazole (MBT) (A); a low level of MBT (B); or zinc dibutyldithiocarbamate (ZDBC) (C). In the CA test, MBT induced mainly polyploidy, including endoreduplication, and ZDBC induced structural CAs. In the cytotoxicity test, culture medium extracts of A, B, and C suppressed colony formation to 50% of the control value at 53.1%, 94.3%, and >100%, respectively. Culture medium extracts of sample A induced polyploidy and structural CAs in the absence of an exogenous metabolic activation system (S9 mix), but at lower concentrations in its presence, indicating the existence of other leachable promutagens. The extracts of sample B induced structural CAs at the highest concentration and only with S9 mix. Sample C was negative. The facts suggest that sample A may be a candidate for a positive control for genotoxicity tests. The high frequency of polyploidy induced by sample A was not predicted by MBT, suggesting the usefulness of the test for safety evaluation of medical devices. Numerical CAs induced by MBT and sample A are discussed.