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Biomedical subjects

H Babich

Publications and source records attributed to H Babich.

At least 37 records · Page 2Linked to original sources

In vitro cytotoxicity of 1,4-naphthoquinone derivatives to replicating cells.

The acute cytotoxicities of a series of alkyl-1,4-naphthoquinones (NQ) and of 2-hydroxy-3-alkyl-1,4-NQs, as well as some amino derivatives, were evaluated with the neutral red cytotoxicity assay, using BALB/c mouse 3T3 fibroblasts. As compared to the unsubstituted 1,4-NQ: (i) Substitution at the 2 position reduced toxicity, with the extent of reduction following the sequence, hydroxyl >> dimethylamino >> C1-C5 alkyl group. (ii) Substitution with C2-C5 alkyl groups at position 3 enhanced toxicity. As noted with the n-alkyl-1,4-NQs, increasing the chain length of the 2-hydroxy-3-alkyl-1,4-NQs did not appreciably change potency of the test agent. (iii) Substitution with amino groups at position 3 had little effect on cytotoxicity. Some differences in cytotoxicity of specific test agent were noted between the 3T3 fibroblasts and isolated rat hepatocytes, as reported in the literature.

3T3 Cells↗

In vitro cytotoxicity of methylated phenylenediamines.

The acute cytotoxicities of methylated phenylenediamines (PDs) were evaluated with the neutral red assay, using BALB/c 3T3 mouse fibroblasts as the bioindicators. When the test agents were grouped according to their degree of methylation, good correlations were noted between their in vitro cytotoxicity and their in vivo myotoxicity to experimental animals, as well as to their in vitro autoxidation rates. For test agents of comparable methylation, the sequence of potency was ring-methylated p-PD > N-methylated p-PD >> N-methylated o-PD > N-methylated m-PD.

Animals↗

In vitro response of the brown bullhead catfish cell line, BB, to aquatic pollutants.

Established cell lines from brown bullhead catfish (BB) and rainbow trout (RTG-2) and primary cultures of cells derived from gill, fin, and gonad tissues from brown bullhead catfish were evaluated for use as bioindicators in the neutral red cytotoxicity assay. The BB and RTG-2 cells were compared after a 1 day exposure to chlorinated pesticides and after a 6-day exposure to various polycyclic aromatic hydrocarbons. The BB cells were more sensitive to both classes of chemicals. The sequence of toxicity for the BB cells was 4,4'-DDD. 4,4'-DDT greater than aldrin, 4,4'-DDE and 7,12-dimethylbenz(a)anthracene (DMBA) greater than 3-hydroxybenzo(a)pyrene (3-OH-B(a)P) greater than benzo(a)pyrene (B(a)P). For the RTG-2 cells, the sequence was aldrin greater than 4,4'-DDD greater than 4,4'-DDT greater than 4,4'-DDE and 3-OH-B(a)P greater than DMBA greater than B(a)P. The BB cells were also sensitive to benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(a)anthracene, and trans-7,8-dihydro-7,8-dihydroxybenzo(a)pyrene. The responses of BB and RTG-2 cells were compared with those of primary cultures after a 1 day exposure to B(a)P. After 1 day of exposure, the RTG-2 cells and primary cultures were more sensitive than the BB cells to B(a)P. Apparently, after 1 day of incubation the RTG-2 and primary cells metabolized greater amounts of B(a)P to cytotoxic metabolites, than did the BB cells. However, by 6 days of incubation, the BB cells were more sensitive to B(a)P than were the RTG-2 cells. A 6-day exposure to B(a)P was not performed with the primary cell cultures.

Animals↗

In vitro cytotoxicity studies with the fish hepatoma cell line, PLHC-1 (Poeciliopsis lucida).

The PLHC-1 fish hepatoma cell line (Poeciliopsis lucida) was used in the neutral red assay to evaluate the acute cytotoxicities of direct-acting (alkylbenzenes, phthalate diesters, and pesticides) and metabolism-mediated (benzo[a]pyrene) toxicants. The sequence of cytotoxic potencies for the alkylbenzenes and phthalate diesters appeared to be a direct function of their hydrophobicity (as described by logarithmic octanol/water partition coefficients). The organochlorine pesticides (alachlor and p,p'-methoxychlor) were more cytotoxic than the organophosphorus pesticides (EPN, diazinon, and malathion). The PLHC-1 cell line apparently maintained sufficient xenobiotic-metabolizing capacity, as the hepatoma cells were able to metabolize benzo[a]pyrene to cytotoxic intermediates. Xenobiotic-metabolizing capacity was temperature dependent, with enzymatic activity increasing as the temperature was increased from 28 to 34 to 37 degrees C, was inducible by Aroclor 1254 (a chemical inducer of cytochrome P450-dependent monooxygenase activity), and was reduced by EPN (an inhibitor of P450 activity).

7-Alkoxycoumarin O-Dealkylase↗

Cytotoxicity of T-2 toxin and its metabolites determined with the neutral red cell viability assay.

The neutral red (NR) cell viability assay was used with various cell types of human origin to quantitate the potency of T-2 mycotoxin and its metabolites. The human melanoma SK-Mel/27 cell line was the most sensitive, with a midpoint cytotoxicity value of 2.8 ng of T-2 per ml. With the human hepatoma cell line, HepG2, the sequence of potency for a series of mycotoxins was T-2 greater than HT-2 greater than T-2 triol greater than T-2 tetraol.

Animal Testing Alternatives↗

Cytotoxic effects of food additives and pharmaceuticals on cells in culture as determined with the neutral red assay.

The acute cytotoxicity of butylated hydroxytoluene and butylated hydroxyanisole to cultured human dermal fibroblasts, keratinocytes, melanocytes, and melanoma tumor cells was determined with the neutral red assay. For all cell types, butylated hydroxytoluene proved to be more cytotoxic than butylated hydroxyanisole. The neutral red assay is a rapid, economical, semiautomated assay that can be used with a variety of cell types in culture to provide quantitated data that can be used to rank test agents according to their potencies.

Animals↗

Rapid chemosensitivity assay with human normal and tumor cells in vitro.

Neutral red assay, as an index of cytotoxicity, has been applied to predictive screening of chemotherapeutic agents. Human hepatoma and melanoma tumor cells and normal melanocytes, keratinocytes, and fibroblasts were incubated for 2, 24, and 48 h with graded concentrations of cis-platinum (0.1 to 80 microM), doxorubicin (0.01 to 100 microM), and 5-fluorouracil (1 to 1000 microM). Cells were most sensitive after 48 h. Tumor cells, based on 50% toxicity values, were 2-4 times more sensitive than the normal cells, except for cis-platinum, where only melanoma cells, as compared to normal melanocytes, showed a marked difference in cytotoxic response. Methotrexate (1 to 10 microM) toxicity could be reversed in the presence of 100 microM of leucovorin. This sensitive, rapid, and economical assay is suitable for preclinical screening and drug development.

Antineoplastic Agents↗

In vitro cyto- and genotoxicity of organomercurials to cells in culture.

The sequence of cytotoxic effects for a series of mercury compounds to the BG/F epithelioid cells derived from fin tissue of bluegill sunfish was phenyl mercuric chloride greater than methyl mercuric chloride greater than ethyl mercuric chloride much greater than mercuric chloride. This sequence of in vitro cytotoxicity was similar to that observed in a 48-h LC50 in vivo acute toxicity assay with rainbow trout. Using induction of micronuclei as an indicator of genetic damage, the organomercurials, but not mercuric chloride, were noted to be clastogenic to the BG/F cells.

Animals↗

Effect of methylazoxymethanol acetate on bluegill sunfish cell cultures in vitro.

An epithelioid cell line derived from fin tissue of bluegill sunfish (designated BG/F) exhibited early indications of cell transformation upon exposure to methylazoxymethanol acetate (MAM acetate). Such changes included the induction of polyploidy, increased colony-forming efficiency, loss of contact inhibition, and formation of transformed foci. Unlike later transformation characteristics observed with mammalian cells, the MAM acetate-treated BG/F cells could not be propagated under conditions of anchorage independence in soft agar. Incubation of BG/F cells with N-methyl-N'-nitro-N-nitrosoguanidine, followed by exposure to 12-O-tetradecanoylphorbol-13-acetate, was not observed to cause cell transformation under the experimental conditions. The controls of a fibroblastic cell culture derived from gill tissue of bluegill sunfish showed spontaneous transformation after 6 months of passage, similar to the transformation observed in the experimental MAM acetate treated gill cultures.

Animals↗

Arsenic-selenium interactions determined with cultured fish cells.

A fibroblastic cell line derived from gill tissue (designated BG/G) and an epithelioid cell line derived from fin tissue (designed BG/F) of bluegill sunfish (Lepomis macrochirus) were used as the bioindicators in toxicity experiments. The neutral red in vitro cytotoxicity assay served as the endpoint. In both cell lines the sequence of observed cytotoxicity was arsenite greater than arsenate greater than selenite greater than selenate, with each cell type exhibiting comparable ranking of midpoint toxicity (NR50) concentrations. Antagonistic interactions were noted between combinations of arsenics and seleniums. Thus, selenate and selenite (at nontoxic levels) reduced, but did not eliminate, the acute cytotoxicities of arsenate and, to a lesser extent, of arsenite.

Animals↗

Acute cytotoxicities of polynuclear aromatic hydrocarbons determined in vitro with the human liver tumor cell line, HepG2.

The neutral red in vitro cytotoxicity assay was adapted for use with the human hepatocellular tumor cell line HepG2 to detect the cytotoxic potencies of polynuclear aromatic hydrocarbons (PAHs). Using benzo[a]pyrene (B[a]P) as the representative PAH, it was determined that a 3-day exposure was the most suitable for detecting cytotoxic potency and that preexposure to 5 micrograms/ml Arochlor enhanced the sensitivity of the HepG2 cells to the toxicant. Such enhanced sensitivity probably reflected increased metabolic conversion of the B[a]P to active metabolites after culturing the cells in the presence of Arochlor. This was shown by a 3-fold increase in the activity of 7-ethoxycoumarin deethylase, an indicator of mixed-function oxygenase activity. Furthermore, a reduction in sensitivity to B[a]P occurred when the cells were cultured in the presence of alpha-napthoflavone, an inhibitor of aryl hydrocarbon hydroxylase activity. When Arochlor-induced cells were transferred to medium lacking Arochlor, the level of 7-ethoxycoumarin deethylase quickly declined to basal levels. Arochlor-induced cells were also able to detect the cytotoxic potencies of benzo[k]fluoranthene, benzo[b]-fluoranthene, chrysene, benzo[a]anthracene pyrene, phenanthrene, and fluoranthene, whereas fluorene, anthracene, acenaphthene, and acenaphthylene were not cytotoxic.

7-Alkoxycoumarin O-Dealkylase↗

Structure-activity relationships for diorganotins, chlorinated benzenes, and chlorinated anilines established with bluegill sunfish BF-2 cells.

The bluegill sunfish (Lepomis macrochirus) BF-2 cell line, propagated at 34 degrees C, served as target for evaluation of the acute toxicities of various classes of aquatic pollutants, using the neutral red cytotoxicity assay. For a series of chlorinated benzenes and anilines, the sequence of cytotoxicity was dependent on the degree of chlorination and on their hydrophobicity, as described by their logarithmic octanol/water partition coefficients (log P values). With increasing numbers of chlorine atoms in the ring structure or with increasing log P values, greater cytotoxicity was observed. For a series of diorganotins, the sequence of cytotoxicity was dependent on the length of the carbon chain and upon their hydrophobicity, as described by Hansch pi parameters. Thus, increasing the chain length or increasing the Hansch pi parameter resulted in greater cytotoxicity. Similar structure-activity relationships for these classes of test agents have been previously established using acute toxicity LC50 assays with aquatic species. The ability of the neutral red in vitro cytotoxicity assay, with cultured fish cells as the bioindicators, to mimic the acute toxicity data obtained from the LC50 assays suggests its utility as a tool for preliminary screening (tier I testing) of aquatic pollutants.

Aniline Compounds↗

In vitro cytotoxicity of heavy metals, acrylamide, and organotin salts to neural cells and fibroblasts.

The cytotoxicity of neurotoxic agents was determined for a series of brain-derived cell types and compared with their toxic effects on BALB/c 3T3 fibroblasts, using the neutral red assay. Ranking of toxicants according to their potencies was the same for all cells tested and was in the order of methylmercury greater than cadmium greater than mercury greater than zinc greater than acrylamide. For a series of di- and triorganotins the ranking order was dibutyl greater than diphenyl greater than dibenzyl greater than dipropyl greater than diethyl greater than dimethyltin and triphenyl greater than tribenzyl greater than trimethyltin, respectively. The test was sensitive enough to detect structure activity relationships between the degree of toxicity and the hydrophobic characteristics of the agents tested.

Acrylamides↗

Fathead minnow FHM cells for use in in vitro cytotoxicity assays of aquatic pollutants.

The suitability of the fathead minnow (FHM) epithelial cell line for use as the target (indicator) system in in vitro cytotoxicity assays was evaluated using several endpoints. The organometal diethyltin dichloride served as the representative test agent. The concentration of diethyltin dichloride which resulted in a midpoint toxicity was 3.5 microM in a 3-day cell growth assay, 3.8 microM in the 24-hr neutral red assay, and 16.5 microM in a 4-hr cell detachment assay. The neutral red assay was used to compare the relative sensitivities of the FHM cells (exposed at 34 degrees C) with those of bluegill sunfish (BF-2) cells, a fibroblastic cell culture (exposed at 26 degrees C), in the presence of different classes of test agents frequently occurring as aquatic pollutants. For both fish species the sequence of potencies of the test agents was in the order of organometals greater than pesticides approximately equal to polychlorinated biphenyls greater than polynuclear aromatic hydrocarbons greater than phenolics. Overall, the FHM cells were more sensitive than were the BF-2 cells. However, there was a better correlation between the in vitro cytotoxicity data for the BF-2 cell culture and LC50 data for bluegill sunfish than between similar data for the FHM cell line and fathead minnows.

Animals↗

Polycyclic aromatic hydrocarbon in vitro cytotoxicity to bluegill BF-2 cells: mediation by S-9 microsomal fraction and temperature.

The in vitro cytotoxicities of various polycyclic aromatic hydrocarbons (PAHs) to bluegill sunfish BF-2 cells were determined with the neutral red assay, which was modified by the incorporation of an S-9 microsomal fraction. Whereas the PAHs per se were weakly cytotoxic, the presence of the S-9 fraction in the incubation mixture increased the cytotoxicity of many of the PAHs, presumably due to the formation of active metabolites. In addition, the cytotoxicity of the PAHs (whether in the absence or presence of the S-9 microsomal fraction) was potentiated if the 6 h exposure was at 37, rather than at 26 degrees C.

Animals↗

In vitro cytotoxicity of organic pollutants to bluegill sunfish (BF-2) cells.

BF-2 cells, an established cell line derived from bluegill sunfish, (Lepomis macrochirus), were exposed to 18 organic toxicants, with cytotoxicity being assayed by the neutral red (NR) technique. Based on the concentration of toxicant that reduced lysosomal uptake of neutral red by 50% (NR50), the rank order of cytotoxicity was methyl mercury greater than pentachlorophenol greater than 2,3,5,6-tetrachlorophenol greater than 2,3,5-trichlorophenol greater than 2,3-dinitrotoluene greater than 2,4,6-trichlorophenol greater than 2,4-dichlorophenol greater than 2,4-dichlorotoluene greater than 6-chloro-3-hydroxytoluene greater than o-chlorotoluene greater than 4-chlorophenol greater than 2-chlorophenol, 2,4-dimethylphenol greater than 2,4-dinitrophenol greater than 4-nitrophenol greater than 3-methylphenol greater than phenol greater than toluene. Published in vivo LC50 values were identified for 11 of the 18 test agents and, with the exception of 2,4-dinitrophenol, there was a good correlation between the in vitro cytotoxicity of the test agents and their in vivo waterborne acute toxocity. The potencies of the substituted phenolics and chlorinated toluenes as determined by the in vitro cytotoxicity assay correlated strongly with their log octanol/water partition coefficients (log P). However, the toxicity of 2,3-dinitrotoluene in vitro, and apparently also in vivo, was not a function of its log P value.

Animals↗