Differential distribution of splice variants of estrogen receptor beta in human testicular cells suggests specific functions in spermatogenesis.

A growing number of estrogen receptor beta (ER beta) splice variants are reported. Several of these have been discovered in testis, but with few exceptions little is known about their cellular localization. The aim of this study was to identify and elucidate the mRNA expression pattern of the different ER beta splice variants in human testicular cells. Northern analysis was performed on whole testis and fractions enriched in germ cells from untreated men and from estrogen-treated men undergoing sex change surgery. Probes were constructed in order to systematically screen for and identify various ER beta splice variants. Several ER beta bands were observed in the human testis, in which splice variants constituted the major part of total ER beta transcripts. Interestingly, only two ER beta wild-type transcripts were detected. These seem to be virtually absent from the haploid germ cells and are probably mainly located in somatic cells and/or primary spermatocytes. Several novel ER beta deletion variants were found in high levels in the haploid germ cell fractions and were nearly absent in testicular cells from the estrogen-treated men. The cell-dependent distribution raises the question whether splice variants may have specific functions in spermatogenesis, and whether the differential splicing of ER beta is regulated in a cell-specific manner.

Mechanisms involved in the induction of apoptosis by T-2 and HT-2 toxins in HL-60 human promyelocytic leukemia cells.

T-2 and HT-2 toxins belong to a group of mycotoxins that are widely encountered as natural contaminants known to elicit toxic responses in hematopoietic cells. In the present study, HL-60 cells were used to characterize the apoptotic effects of T-2 and a major metabolite, HT-2, and to examine the mechanisms involved. Apoptotic cells were identified microscopically by chromatin condensation and nuclear fragmentation, by flow cytometric analysis, and by DNA gel electrophoresis. T-2 and HT-2 induced concentration-dependent apoptosis after 24 h in HL-60 cells, starting at concentrations of 3.1 and 6.25 ng/ml respectively. An increased number of apoptotic cells could be observed 4-6 h after exposure to 12.5 ng/ml of toxin. Little cytotoxicity (plasma membrane damage) was observed even after exposure to concentrations of toxins (25-50 ng/ml) inducing apoptosis in 60-100% of the cells. The apoptotic process was almost completely blocked in the presence of the general caspase inhibitor zVAD.fmk. In contrast, no or only minor effects were observed with the more specific caspase inhibitors DEVD.CHO, IETD.fmk, and DEVD.fmk. As judged by Western blotting, the levels of several procaspases (-3, -7, -8, -9, but not -12) were reduced 3-6 h after exposure to toxin. Substantial increases in the presumed active form(s) of caspase-8 and -9 were observed. Furthermore, poly(ADP-ribose) polymerase (PARP) was already markedly cleaved 3 h after toxin treatment, indicative of active caspase-3 and -7. No or only minor changes in Bcl-2, Bcl-XL and Bax levels were observed. BAPTA-AM and ZnCl2 blocked the degradation of procaspases, the fragmentation of PARP, and the induction of apoptosis. In summary, both T-2 and HT-2 induced apoptosis, with T-2 being somewhat more potent than HT-2. The divalent calcium concentration, [Ca2+], appears to be involved in the activation of several caspases, resulting in DNA fragmentation, chromosomal condensation, and nuclear fragmentation.

Seasonal changes in spermatogenic activity and in plasma levels of FSH, LH and testosterone, and the effect of immunization against inhibin in the male silver fox (Vulpes vulpes).

The cellular composition of the silver fox testis assessed by DNA flow cytometry and histological analysis exhibited marked circannual alterations. The proportion of haploid cells increased from late October to the breeding season in February, while that of diploid cells decreased and that of tetraploid cells fluctuated during the same period. Towards the end of March these changes were reversed. The seasonal variations in testicular histology paralleled the changes in distribution of cells from the different DNA populations. In August, 69% of the tubules contained spermatogonia as the only type of germ cell, while the remaining 31% also contained a few primary spermatocytes. In late October more than 50% of the tubules contained spermatocytes, and during the period of further activation from early December-February the seminiferous epithelium included round and/or elongated spermatids as well. In February, all tubules contained complete associations of germ cells, whereas in late March tubules with spermatogonia only and spermatogonia together with a few spermatocytes reappeared. In May, only such tubules could be found indicating total regression. Plasma concentrations of FSH and LH increased from early November, both gonadotrophins reaching maximum levels in December or early January, and then both declined during the second part of January, immediately prior to the actual breeding season. LH values showed a few smaller peaks in the beginning of June, whereas FSH levels were generally low until the next period of testicular reactivation. Testosterone concentrations were also low during most of the year but rose in November and December to reach a peak in January and a second peak in June. In animals immunized against inhibin the distribution of haploid, diploid and tetraploid cells did not deviate to any great extent from that in the controls, except in March when the immunized males had a markedly lower proportion of tetraploid cells, and in May, when they had a distinctly higher proportion of haploid cells. These findings were partly reflected by the histology. In the immunized animals, plasma FSH levels started to increase at approximately the same time but peaked higher and remained elevated almost 1 month longer than in the controls, whereas both the rise and decline in LH levels generally coincided with the variations in these animals, but the values were mostly higher. The testosterone profiles were similar to those in the controls except that the maximum values were also usually higher.

Expression of Bcl-2 family proteins and spontaneous apoptosis in normal human testis.

We investigated the frequency of spontaneous apoptosis and expression of the Bcl-2 family of proteins during normal spermatogenesis in man. Testicular tissue with both normal morphology and DNA content was obtained from necro-donors and fixed in Bouin's solution. A TdT-mediated dUTP end-labelling method (TUNEL) was used for the detection of apoptotic cells. Expression of apoptosis regulatory Bcl-2 family proteins and of p53 and p21(Waf1) was assessed by immunohistochemistry. Germ cell apoptosis was detected in all testes and was mainly seen in primary spermatocytes and spermatids and in a few spermatogonia. Bcl-2 and Bak were preferentially expressed in the compartments of spermatocytes and differentiating spermatids, while Bcl-x was preferentially expressed in spermatogonia. Bax showed a preferential expression in nuclei of round spermatids, whereas Bad was only seen in the acrosome region of various stages of spermatids. Mcl-1 staining was weak without a particular pattern, whereas expression of Bcl-w, p53 and p21(Waf1) proteins was not detected by immunohistochemistry. The results show that spontaneous apoptosis occurs in all male germ cell compartments in humans. Bcl-2 family proteins are distributed preferentially within distinct germ cell compartments suggesting a specific role for these proteins in the processes of differentiation and maturation during human spermatogenesis.

Nucleotide excision repair in rat male germ cells: low level of repair in intact cells contrasts with high dual incision activity in vitro.

The acquisition of genotoxin-induced mutations in the mammalian germline is detrimental to the stable transfer of genomic information. In somatic cells, nucleotide excision repair (NER) is a major pathway to counteract the mutagenic effects of DNA damage. Two NER subpathways have been identified, global genome repair (GGR) and transcription-coupled repair (TCR). In contrast to somatic cells, little is known regarding the expression of these pathways in germ cells. To address this basic question, we have studied NER in rat spermatogenic cells in crude cell suspension, in enriched cell stages and within seminiferous tubules after exposure to UV or N-acetoxy-2-acetylaminofluorene. Surprisingly, repair in spermatogenic cells was inefficient in the genome overall and in transcriptionally active genes indicating non-functional GGR and TCR. In contrast, extracts from early/mid pachytene cells displayed dual incision activity in vitro as high as extracts from somatic cells, demonstrating that the proteins involved in incision are present and functional in premeiotic cells. However, incision activities of extracts from diplotene cells and round spermatids were low, indicating a stage-dependent expression of incision activity. We hypothesize that sequestering of NER proteins by mispaired regions in DNA involved in synapsis and recombination may underlie the lack of NER activity in premeiotic cells.

Highly efficient base excision repair (BER) in human and rat male germ cells.

The quality of germ cell DNA is critical for the fate of the offspring, yet there is limited knowledge of the DNA repair capabilities of such cells. One of the main DNA repair pathways is base excision repair (BER) which is initiated by DNA glycosylases that excise damaged bases, followed by incision of the generated abasic (AP) sites. We have studied human and rat methylpurine-DNA glycosylase (MPG), uracil-DNA glycosylase (UNG), and the major AP endonuclease (HAP1/APEX) in male germ cells. Enzymatic activities and western analyses indicate that these enzymes are present in human and rat male germ cells in amounts that are at least as high as in somatic cells. Minor differences were observed between different cellular stages of rat spermatogenesis and spermiogenesis. Repair of methylated DNA was also studied at the cellular level using the Comet assay. The repair was highly efficient in both human and rat male germ cells, in primary spermatocytes as well as round spermatids, compared to rat mononuclear blood cells or hepatocytes. This efficient BER removes frequently occurring DNA lesions that arise spontaneously or via environmental agents, thereby minimising the number of potential mutations transferred to the next generation.

Single-strand breaks, cell cycle arrest and apoptosis in HL-60 and LLCPK1 cells exposed to 1,2-dibromo-3-chloropropane.

We investigated 1,2-dibromo-3-chloropropane (DBCP)-induced DNA damage, cell cycle alterations and cell death in two cell lines, the human leukemia HL-60 and the pig kidney LLCPK1, both of which are derived from potential target sites for DBCP-induced toxicity. DBCP (30-300 micromol/L) caused a concentration-dependent increase in the levels of DNA single-strand breaks in both cell lines as well as in cultured human renal proximal tubular cells. After extended DBCP exposure in LLCPK1 cells (100 micromol/L, 30 h), the level of DNA breaks returned almost to control values. Incubation for 48 h showed a clear reduction of growth with DBCP concentrations as low as 10 micromol/L. Flow cytometric analysis showed that DBCP (1-10 micromol/L) exposure for 24 h caused an accumulation of LLCPK1 cells in the G2/M-phase. In HL-60 cells the accumulation in G2/M-phase was less marked, and at higher concentrations the cells accumulated in S-phase. Flow cytometric studies of HL-60 and LLCPK1 cells exposed to 100-500 micromol/L DBCP showed increased number of apoptotic cells/bodies with a lower DNA content than that of the G1 cells. Microscopic studies revealed that there were increased numbers of cells with nuclear condensation and fragmentation, indicating that apoptosis was the dominant mode of death in these cell lines, following exposure to DBCP. The characteristic ladder pattern of apoptotic cells was observed when DNA from DBCP-treated HL-60 cells and LLCPK1 cells was electrophoresed in agarose. The finding that DBCP can cause an accumulation of cells in G2/M-phase and induce apoptosis in vitro may be of importance for the development of DBCP-induced toxicity in vivo.

Apoptosis in HL-60 cells induced by 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX).

The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX), which is formed during chlorination of drinking water, has been studied with respect to induction of cell death in promyelocytic leukemic HL-60 cells. Cells exposed to MX for 1 h and further incubated for 3 h, revealed no significant increase in the proportion of cells with compromised plasma membrane damage as judged by trypan blue or propidium iodide exclusion. However, flow cytometric studies and microscopic analysis of HL-60 cells after staining with Giemsa or Hoechst 33342, revealed that more than 30% of the cells exposed to 30-100 microM of MX, showed the characteristic morphology and biochemical markers of apoptosis. On the other hand, in cultures exposed to 300 microM MX, less than 5% of the cells appeared to be apoptotic (< G1 DNA) 3 h after treatment, which is similar to control values. Microscopic analysis of Hoechst 33342-stained cells revealed that they were 'arrested' in the early stages of chromatin condensation, but these cells eventually became necrotic. Some decrease in the percentage of cells in S-phase was observed 3 h after exposure to MX (10, 30 and 100 microM), but the induced cell death was not markedly cell stage specific. The characteristic ladder pattern of apoptotic cells was observed when DNA isolated from MX-exposed HL-60 cells was electrophoresed in agarose. The apoptotic process could also be detected by analysis with alkaline filter elution (AE), as a decrease in the total DNA recovered; and by single cell gel electrophoresis, as a decrease in the average number of cells/comets observable on each slide. With the protocols used no apparent increase in values in the normalized area above the curve (NAAC) (alkaline elution) or tail moments (single cell gel electrophoresis (SCGE)) were detected, indicating that apoptotic cells are not necessarily a confounding factor when assaying for genotoxicity with these techniques.

Paracetamol inhibits cell cycling and induces apoptosis in HL-60 cells.

We investigated the effects of paracetamol on cell cycle and cell death in cultured HL-60 cells. Paracetamol (0.1-3.0 mM) caused a dose-dependent inhibition of cell proliferation. Inhibition of DNA synthesis was observed at as low concentrations as 0.03 mM. When HL-60 cells were exposed to paracetamol (0.1-1.0 mM), flow cytometric analysis showed that cells accumulated in the G1/S phase, and then slowly proceeded through the S-phase. Exposure to 2.0-3.0 mM paracetamol, on the other hand, resulted in a reduction of the number of cells in S-phase and G2/M phase, and a concurrent increase in cells/bodies with a lower DNA content than that of the G1 cells. Microscopic studies revealed increased numbers of cells with nuclear condensation and fragmentation, indicating that apoptosis was the dominating mode of death in this cell line after exposure to paracetamol. However, when DNA from paracetamol-treated cells were electrophoresed in agarose, no clear ladder pattern characteristic for apoptotic cells was observed. This was most likely a result of secondary necrosis which followed incomplete apoptosis. Within 5-10 hr after start of paracetamol exposure, a marked downregulation of both c-myc and bcl-2 mRNA was observed. In conclusion, the present results show that exposure to high non-therapeutic concentrations of paracetamol cause cell cycle arrest and apoptosis in HL-60 cells in S-phase.

A comparative study of chemically induced DNA damage in isolated human and rat testicular cells.

Testicular cells prepared from human organ transplant donors or from Wistar rats were used to compare 15 known reproductive toxicants with respect to their ability to induce DNA damage, measured as single-strand DNA breaks and alkali labile sites (ssDNA breaks) with alkaline filter elution. The compounds tested included various categories of chemicals (i.e., pesticides, industrial chemicals, cytostatics, and mycotoxins) most of which are directly acting genotoxicants (i.e., reacting with DNA either spontaneously or via metabolic activation). In addition, a few indirect genotoxic and nongenotoxic reproductive toxicants were included. Six of the chemicals induced no significant levels of ssDNA breaks in human and rat testicular cells; methoxychlor (10 to 100 microM, human and rat), benomyl (10 to 100 microM, human and rat), thiotepa (10 to 1000 microM, human and rat), cisplatin (30 to 1000 microM, human; 100 to 1000 microM, rat), Cd2+ (30 to 1000 microM, human; 100 to 1000 microM, rat), and acrylonitrile (30 to 1000 microM, human; 30 to 300 microM, rat). Four chemicals induced significant levels of ssDNA breaks in testicular cells from both species: styrene oxide (> or = 100 microM, rat and human), 1,2-dibromoethane (EDB) (> or = 100 microM, rat; 1000 microM human), thiram (> or = 30 microM, rat; > or = 100 microM, human), and chlordecone (300 microM, rat; > or = 300 microM, human). Finally, five chemicals induced ssDNA breaks in one of the two species. Four chemicals induced significant ssDNA breaks in rat testicular cells only: 1,2-dibromo-3-chloropropane (DBCP) (> or = 10 microM), 1,3-dinitrobenzene (1,3-DNB) (> or = 300 microM), Cr6+ (1000 microM), and aflatoxin B1 (> or = 100 microM), the last two of these produced only a minor positive response. One chemical, acrylamide, induced a marginal increase in ssDNA breaks in human at 1000 microM, but not in rat testicular cells. Although based on a limited number of donors, the data indicate a close correlation between the induction of DNA damage in human and rat testicular cells in vitro. For some chemicals, however, there appears to be differences in the susceptibility to chemically induced ssDNA breaks of isolated testicular cells from the two species. The data indicate that the parallel use of human and rat testicular cells provides a valuable tool in the assessment of human testicular toxicity.

Expression of CYP2B1 in freshly isolated and proliferating cultures of epithelial rat lung cells.

Bronchiolar Clara cells and alveolar type 2 cells of the lung are known to express relatively high levels of P450 enzymes compared to other pulmonary cells. Populations of enriched type 2 cells and Clara cells were isolated from rat lung by a procedure including lung perfusion, protease digestion, centrifugal elutriation, and differential attachment. Alveolar macrophages were removed by lavage. The purity of the type 2 cell-enriched population was approximately 90%, and the purity of the Clara cell-enriched population was 40-50%. Both type 2 cells and the cells of the Clara cell-enriched population proliferated in culture. CYP2B1 mRNA was expressed approximately to the same level in type 2 cells and the Clara cell-enriched population. The mRNA levels remained roughly constant for both cell types throughout the culture period, except for an early transient reduction. The apoenzyme level of CYP2B1 was 2-3 times higher in freshly isolated cells of the Clara cell-enriched population than in the type 2 cells. Both epithelial cell types showed decreased level of CYP2B1 apoenzyme in culture. The differences in the CYP2B1 mRNA and apoenzyme expression levels in freshly isolated cells and cultured cells suggest the existence of a post-transcriptional regulatory mechanism for CYP2B1 expression in lung cells. The characterization of specific functions of lung cells in culture, such as P450 gene expression, provides necessary information for the use of the cells in in vitro pulmonary toxicology.

DNA strand breaks in testicular cells from humans and rats following in vitro exposure to 1,2-dibromo-3-chloropropane (DBCP).

Preparations of testicular cells from human organ transplant donors and from Wistar rats were compared with respect to their composition of the different testicular cell types, their ability to metabolize 1,2-dibromo-3-chloropropane (DBCP), and their relative sensitivity to induction of DNA single strand breaks and alkali labile sites (ssDNA breaks) after treatment with DBCP, 4-nitroquinoline N-oxide (4-NQO), and X rays. Flow cytometric and microscopic analysis demonstrated that the interindividual variation in the composition of testicular cell types was considerably greater in the human tissue than in that from rats. The in vitro metabolic activation of DBCP (50 to 250 microM), measured as radiolabel covalently bound to macromolecules, was three-fold faster in rat testicular cells compared to human testicular cells. X rays (1 to 10 Gy) and 4-NQO (0.5 to 2.5 microM) induced ssDNA breaks to a similar extent in both human and rat testicular cells as measured by single cell get electrophoresis (SCGE) and alkaline filter elution. In contrast, 1,2-dibromo-3-chloropropane (DBCP) (3 to 300 microM) caused no significant DNA damage in human testicular cells, whereas in rats there was a clear concentration-dependent increase in ssDNA breaks. The data show that, compared to rats, testicular cells from humans are less efficient in activating DBCP to metabolites binding covalently to macromolecules. However, from the rate of covalent binding observed one would expect a significant degree of DBCP-induced ssDNA breaks in the human testicular cells. The low level of DBCP-induced ssDNA breaks in human testicular cells could indicate that different reactive DBCP metabolites are involved in binding to cellular macromolecules compared to DNA damage, or that different rates of DNA repair exist in human and rat testicular cells.

The use of isolated lung cells in in vitro pulmonary toxicology: studies of DNA damage, apoptosis and alteration of gene expression.

Isolated lung cells constitute a valuable system for studying mechanisms involved in chemically induced toxicity in the lung. Different lung cells isolated from various species may be studied. Bronchiolar Clara and alveolar type 2 cells produce important lung-specific proteins, hold a major role in the metabolism of xenobiotics and serve as progenitor cells for other lung cell types. They are possible target cells in lung carcinogenesis. Alveolar macrophages play an important role in lung defence and in inflammatory responses. In the present study we have characterised chemically induced DNA damage, apoptosis, changes in cell cycle progression, transformation and alterations in gene expression in these specific lung cells isolated from rat, rabbit and human. Major differences between the cell types and the various species in the induction of DNA damage by chemicals were found, as measured by the 32P-postlabelling and alkaline filter elution techniques. Benzo(a)pyrene and hydrogen fluoride were found to induce apoptosis in the isolated cells as measured by microscopical analysis and flow cytometry. The function of various important tissue- or cell type specific proteins (CYP 2B1, Clara cell protein) and/or cellular signal transduction pathways constitute important targets that may be affected by exposure to toxic compounds. Using immunological and molecular techniques the differential expression of specific proteins/RNAs and their activity can be studied. Among other proteins, c/ebp is involved in the regulation of transcription at the end of signal pathways. The protein is differentially expressed in rat lung cells and thus could be suitable for studying differential toxic effects in various lung cells. In humans, bronchoalveolar lavage (BAL) fluid from human volunteers can be readily obtained and examined after exposure to different chemical compounds. An increase in the percentage of CD3-positive cells (T-lymphocytes) was found after exposure to hydrogen fluoride. The number of certain cell types and cytokines may be used to estimate the degree of inflammatory reaction. In conclusion, the use of in vitro data including the use of specific, primary human lung cell types may contribute considerably to the quality of risk assessment, together with in vivo data from animals and man.

In vitro toxicity of 1,2-dibromo-3-chloropropane (DBCP) in different testicular cell types from rats.

1,2-Dibromo-3-chloropropane (DBCP)-induced toxicity was studied in rat germ cells from different stages of spermatogenesis, separated by centrifugal elutriation, and in Sertoli cells prepared from sexually mature and immature animals. The in vitro metabolic activation of 50 to 250 microM DBCP, measured as covalent binding of 14C-DBCP to macromolecules, was highest in round spermatids, lowest in Sertoli cells and elongating/elongated spermatids, and intermediate in spermatocytes. High concentrations of DBCP (> or = 250 microM) caused a decrease in oxygen consumption and mitochondrial rhodamine 123 uptake, indicating an effect on mitochondrial function. Altered Sertoli cell function, measured as detachment of germ cells in Sertoli-germ cell cocultures, was evident at DBCP concentrations > or = 300 microM. DBCP-induced DNA damage occurred at much lower concentrations (10 to 30 microM) when compared to effects on mitochondrial function and Sertoli cell function. The extent of single strand DNA breaks and alkali-labile sites (ssDNA breaks) measured by the alkaline filter elution technique and the single cell gel electrophoresis assay, were greatest in the round spermatids > spermatocytes = Sertoli cells > elongating/elongated spermatids. The study demonstrates that various testicular cell types show differences in their rates of activation of DBCP to metabolites that bind to macromolecules. DNA is a more sensitive intracellular target in DBCP-induced testicular toxicity than mitochondria. Round spermatids appear to be more susceptible to DBCP-induced ssDNA breaks than spermatocytes, elongating/elongated spermatids, or Sertoli cells.

Effects of acetaminophen and hydroxyurea on spermatogenesis and sperm chromatin structure in laboratory mice.

High doses of acetaminophen (400 mg/kg) or hydroxyurea (200 mg/kg) given intraperitoneally daily for 5 d caused reduction in relative testicular weight in mice (B6C3/F1/BOM M). Testicular atrophy of several tubules was seen in the hydroxyurea-treated mice 5 d after the last exposure, whereas acetaminophen did not lead to such changes. Exposure to acetaminophen caused neither a depletion of glutathione in the testis nor a marked increase in covalent binding. In contrast, significant decreases in the incorporation of thymidine into the testis were observed during the first 3 h following a single treatment with acetaminophen (100 to 400 mg/kg) or hydroxyurea (100 to 200 mg/kg). In mice treated with acetaminophen (400 mg/kg) or hydroxyurea (200 mg/kg) daily for 5 d, flow cytometric analysis revealed large reductions in one of the tetraploid populations of testicular cells (mostly early pachytene spermatocytes) on days 5 and 10. Changes in the populations of the various spermatid stages occurred later; thus, both compounds appeared to cause a delay in spermiogenesis. Indications of abnormal chromatin structure were seen in an increased frequency of vas deferens sperm on days 27 and 33 after the last exposure, when measured as increased susceptibility towards DNA denaturation in situ. In conclusion, high doses of acetaminophen or hydroxyurea inhibit DNA synthesis in the testis. The present data indicate that this leads to reduced testicular weight, a reduction in the number of early pachytene spermatocytes, changes in the proportions of the various spermatid stages, and an apparent alteration in sperm chromatin structure.

Effect of n-3 and n-6 fatty acids on proliferation and differentiation of promyelocytic leukemic HL-60 cells.

Promyelocytic leukemic HL-60 cells were incubated with different fatty acids. Arachidonic acid (AA; 20:4, n-6) and eicosapentaenoic acid (EPA; 20:5, n-3) were the most potent inhibitors of proliferation in a dose-dependent way. Retinoic acid (RA) was used as a positive control. Inhibitors of cyclooxygenase and lipoxygenase or addition of antioxidants did not influence the effect of EPA or AA on cell proliferation. Increased capacity to generate superoxide anions after phorbol ester treatment and a reduced serglycin messenger RNA level in cells treated with AA or EPA indicated that these fatty acids induced differentiation in HL-60 cells similar to that induced by RA. However, down-regulation of the c-myc mRNA level, also typical for differentiation with RA in HL-60 cells, was not observed in cells incubated with AA or EPA. Flow cytometric analyses showed that in cultures incubated with AA or EPA, the proportion of cells in the G1 phase of the cell cycle increased. Similar effects were observed with RA. By flow cytometry and light scatter analyses it could be shown that AA made 8% of the cells apoptotic and 7% necrotic. The corresponding numbers were 21% and 10% for RA-treated cells, and 19% and 32% for EPA-treated cells. The present study shows that AA and EPA reduce the proliferation rate of HL-60 cells. This is mediated by mechanisms independent of eicosanoids or lipid peroxidation products and is due to effects both on apoptosis/necrosis and cell differentiation.

Comparison of rat and chick limb bud micromass cultures for developmental toxicity screening.

This study compares the responses of rat and chick limb bud micromass cultures to chemical treatment. Eight chemicals, of diverse structure, potency and mechanism, were tested, using two endpoints: extractable alcian blue stain as a measure of differentiation to chondrocytes, and extractable neutral red stain as an index of proliferation. Each chemical reduced differentiation and proliferation in a concentration-related manner. IC(50)s, concentrations that reduced staining by 50%, ranged from 10 nm (colchicine) to 4 mm (acetazolamide). Rat and chick responses to acetazolamide, colchicine and diazepam were indistinguishable. For diphenhydramine and sulphisoxazole, concentration-response curves were very similar, but rat IC(50)s were half that of chick. For two chemicals, concentration-response slopes were markedly steeper for chick; in the case of beta-aminopropionitrile, IC(50)s were similar, but rat cultures were three-fold more sensitive than chick to cytosine arabinoside. 6-Aminonicotinamide gave a U-shaped response curve, for both endpoints and both species, so IC(50)s may be misleading, but the IC(50) for proliferation was lower for chick (0.6 mum) than rat (4 mum). In vivo and in vitro parameters for validation of developmental toxicity screens are contentious. Diphenhydramine apart, these chemicals can be teratogenic in vivo, although their 'hazard' can be debated. An IC(50)-proliferation/IC(50)-differentiation ratio > 2 has been suggested to predict specific developmental toxicity. Only sulphisoxazole and 6-aminonicotinamide had significantly different IC(50)s for proliferation and differentiation, with ratios of 4.4 (both species), and 10.4 for rat and 1.9 for chick, respectively. All other ratios were close to 1. The general consistency of this ratio, and the concentration-responses, in the two species suggests that the chick is a viable alternative to laboratory mammals, but the predictive ability of micromass remains to be determined.

Effects of ochratoxins A and B on prechondrogenic mesenchymal cells from chick embryo limb buds.

Prechondrogenic mesenchymal cells from the limb buds of 4-day chick embryos were cultured together with either ochratoxin A (OA) or ochratoxin B (OB) for 6 days. Both toxins inhibited the accumulation of cartilage proteoglycans and general protein synthesis in a concentration-related manner. The IC50 was 1.9 microM for OA and 6.2 microM for OB. Incubating the micromass with OA for periods ranging from 2 h up to 6 days did not produce any metabolites, indicating that OA was the proximal toxic compound in these studies. Neither preincubation with OB nor simultaneous exposure to non-toxic concentrations of OB together with various concentrations of OA influenced the toxicity of OA. The data indicate that interference of OA with general protein synthesis, both in vivo and in vitro, is an important mechanism underlying OA-induced embryotoxicity.