Subcellular distribution of adriamycin in the liver and tumor of 3LL-bearing mice

A comparison of adriamycin and mAMSA. II. Studies with V79 and human tumour multicellular spheroids

Multicellular spheroids were used to compare the two chemotherapeutic agents adriamycin (ADM) and 4'[(9-acridinyl)-amino] methanesulphon-m-anisidide (mAMSA). Chinese hamster cells, V79 379A, a human small cell lung carcinoma, designated ME/MAR, and a human melanoma xenograft, HX117, were grown as spheroids (200 or 400 micron in diameter) and treated with either drug for 1 h, at 37 degrees C, in air. Cytotoxicity was assayed using both cell survival and growth delay. Both drugs were highly toxic towards V79 but showed less activity toward the human tumour single cell suspensions; ADM was more effective towards HX117 and ME/MAR than mAMSA. When grown as spheroids, the cells developed marked resistance to both drugs. In all cases, cytotoxicity was drug dose and spheroid size dependent. The response of HX117 spheroids to both drugs was similar. In contrast, ADM was more effective toward 200 micron diameter ME/MAR spheroids, and mAMSA showed greater activity than ADM against V79 spheroids. Both endpoints gave qualitatively equivalent results, and a comparison of the two showed relatively long growth delays for a given level of cell kill, for both drugs and with all three cell lines. The greater cytotoxicity of ADM toward ME/MAR spheroids is consistent with the clinical finding that ADM has a use in the treatment of small cell carcinoma of the lung, while mAMSA has not demonstrated any activity in the treatment of lung cancer.

Cellular pharmacology and antitumor activity of N-(p-azidobenzoyl)-daunorubicin, a photoactive anthracycline analogue

We have previously utilized N-(p-azidobenzoyl)daunorubicin (NABD), a photoactive analogue of daunorubicin (DNR), to identify unique anthracycline-binding polypeptides in rodent tissues and in tumor cells. Using cultured P388 tumor cells, we have now compared the cellular pharmacology and antitumor activity of NABD with that of DNR. Although rapidly accumulated by cells, the intracellular concentration of NABD was less than 20% that of DNR at steady-state levels. The cellular uptake of both drugs by P388 cells was dependent on extracellular drug concentration in the medium and on temperature. The rapid efflux of NABD and DNR from P388 cells in drug-free medium was reduced at lowered temperature (0 degrees C). Cytofluorescence microscopy demonstrated that NABD was predominantly localized in the cytoplasm, in contrast to the nuclear localization of DNR. NABD produced dose-dependent inhibition of [3H]thymidine (IC50 = 10.0 microM) and [3H]uridine (IC50 = 1.60 microM) incorporation in P388 cells to a lesser degree than DNR ([3H]thymidine, IC50 = 0.15 microM and [3H]uridine, IC50 = 0.70 microM). Continuous exposure to NABD inhibited P388 cell proliferation with an IC50 of 0.27 microM, compared with an IC50 of 0.017 microM for DNR. NABD is a pharmacologically active, photoactive analogue of DNR, which possesses properties different from those of the parent drug but similar to those of other anthracycline analogues. Photoaffinity labeling studies with NABD may identify important cytoplasmic constituents which interact with this type of anthracycline and perhaps with the anthracycline antibiotics in general.

Toxic effects of chemicals: difficulties in extrapolating data from animals to man

This review attempts an analysis of the major components which make it extremely difficult to extrapolate toxicological data obtained with chemicals from animals to man. A first problem concerns the use of doses to express the unit of comparison across animal species; the dose is a parameter exogenous to the body and when a chemical enters the body concentrations should be utilized. There is in fact evidence that for several chemicals equal doses in different animal species do not mean equal concentrations in blood or tissues. Concentrations of chemicals should be measured for extrapolation purposes as close as possible to the site of the toxic effect. A second problem regards the fact that several chemical are transformed in the body into other chemical species--sometimes few and sometimes many--and some of these species (active metabolites) display biological activity in some cases higher than different from or antagonistic to those of the parent compounds. Some of these metabolites are highly reactive and therefore bind to body components, particularly macromolecules such as proteins and nucleic acids. There is evidence that metabolism is quantitatively and/or qualitatively different in various animal species. A third problem concerns the difference in various animal species in the biological substrates on which chemicals exert their toxic effects. Equal concentrations of chemicals and their metabolites do not mean equal toxic effects across animal species because endogenous metabolic processes, cell permeability, enzymes, and receptors are not necessarily the same in animals and man. To overcome these difficulties there is a need for closer integration of different disciplines in the toxicological evaluation of chemicals. A scientific rather than a routine approach in toxicology is emphasized.