Patricia M. Loveland

Glucuronides in bile of rainbow trout (Salmo gairdneri) injected with [3H]aflatoxin B1 and the effects of dietary β-naphthoflavone

Rainbow trout Salmo gairdneri were fed a diet containing the mixed-function oxidase system inducer, beta-naphthoflavone or were fed a control diet. For the two respective diets, as much as 50 and 12% of an i.p.-injected dose of [3H]aflatoxin B1 was recovered in the bile. The major product in the bile of beta-naphthoflavone-fed trout was an aflatoxicol-M1 glucuronide, whereas the major product in the control bile was an aflatoxicol glucuronide.

Quantitative carcinogenesis and dosimetry in rainbow trout for aflatoxin B1 and aflatoxicol, two aflatoxins that form the same DNA adduct

Two exposure protocols were used to establish complete dose-response relationships for the hepatic carcinogenicity and DNA adduction in vivo of aflatoxin B1 (AFB1) and aflatoxicol (AFL) in rainbow trout. By passive egg exposure, AFL was taken up less well than AFB1, but was more efficiently sequestered into the embryo itself, to produce an embryonic DNA binding curve that was linear with carcinogen dose and with a DNA binding index three-fold greater than AFB1. Both aflatoxins produced the same phenotypic response, predominantly mixed hepatocellular/cholangiocellular carcinoma. Tumor responses as logit [incidence] vs. In [dose] were parallel-offset, non-linear responses showing a three-fold greater carcinogenic potency for AFL at all doses examined (i.e. 3 times more AFB1 than AFL required to produce an equivalent liver tumor incidence). By molecular dosimetry analysis (logit [incidence] vs. In [DNA adducts]), the two data sets were coincident, indicating that, per DNA adduct formed in vivo in total embryonic DNA, these two aflatoxins were equally efficient in tumor initiation. By dietary fry exposure, both carcinogens produced linear DNA binding dose responses in liver, but with an AFL target organ DNA binding index only 1.14 times that of AFB1 by this exposure route. The tumor dose-response curves also did not exhibit the three-fold difference shown by embryo exposure, but were closely positioned non-linear curves. Since the DNA binding indices differed by only 14%, the resulting molecular dosimetry curves for AFL and AFB1 by dietary exposure were similar to the tumor response curves. These results indicate that differing exposure routes produced differing relative carcinogenicity estimates based on doses applied, as a result of protocol-dependent differences in AFL and AFB1 pharmacokinetic behaviors, but that potency comparisons based on molecular dose received were similar for the two protocols. By comparison with standard DNA adducts produced in vitro using the dimethyloxirane-produced 8,9-epoxides of AFB1 and AFL, we conclude that > 99% of AFL-DNA adducts produced in vivo were identical to those produced by AFB1. Thus similar molecular dosimetry responses should be expected under all exposure protocols in which the two parent carcinogens do not exhibit differing toxicities to the target organ.

Molecular dosimetry in fish : quantitative target organ DNA adduction and hepatocarcinogenicity for four aflatoxins by two exposure routes in rainbow trout

Rainbow trout, a species highly sensitive to aflatoxins, was used to investigate the relative carcinogenicities of four structurally related aflatoxins in terms of their target organ DNA binding characteristics. Tritiated syntheses were carried out, DNA binding dose-response curves were established, and liver DNA binding indices were calculated for the four aflatoxins following a 2-week dietary fry exposure protocol. The results indicated that adduct levels increased linearly with dietary dose concentration, with relative DNA binding indices of 20.7, 20.3, 2.35, and 2.22 x 10(3) (pmoles aflatoxin mg-1 DNA)/(pmoles aflatoxin g-1 diet) for aflatoxin B1 (AFB1), aflatoxicol (AFL), aflatoxin M1 (AFM1), and aflatoxicol M1 (AFLM1), respectively. A similar protocol used over 7200 trout fry averaging 1.2 g initial body weight to establish full carcinogen dose-response curves for each aflatoxin, along with a single-dose estimate of DNA binding index within the tumor study animals. Owing to trout sensitivity a total of 180 micrograms or less of each aflatoxin was required. Data analyzed on logit incidence vs. Ln dose coordinates generated four curves which were modeled as parallel in slope over most or all dose ranges studied. By this analysis, relative tumorigenic potencies were: AFB1 1.00; AFL 0.936; AFM1 0.086; and AFLM1 0.041. When data were plotted as logit incidence vs. Ln adducts (effective dose received), all aflatoxin adducts described the same dose-response curve; that is, they were equally tumorigenic, except those from AFLM1, which were 2-3 fold less potent. Therefore, by these molecular dose studies, differences in tumorigenicity among the four dietary aflatoxins are largely or entirely accounted for by differences in uptake and metabolism leading to DNA adduction, rather than any inherent differences in tumor initiating potency per DNA adduct.

Application of matrix solid-phase dispersion in the determination of dibenzo[a,l]pyrene content of experimental animal diets used in a large-scale tumor study

A method utilizing matrix solid-phase dispersion (MSPD) was developed for isolation and determination of dibenzo[a,l]pyrene (DBP) in experimental rainbow-trout diets used in a large-scale carcinogenesis study. A 0.5 g sample of moist ration containing 0-225 ppm DBP (dry basis) was mixed with 2 g C18 sorbent and benzo[a]pyrene internal standard was added to the mixture. Extraction and clean-up were accomplished in a single step by extracting the sample mixture with hexane-benzene 4:1 from a cartridge containing 2 g Florisil. DBP was quantified by HPLC on a C5 bonded phase column with fluorescence detection. Mean analytical recovery of DBP from control diet spiked at three concentration levels was 101 to 107% with relative standard deviations of 1 to 7%. The limit of detection of DBP was equivalent to 0.014 ppm in the ration. Application of the method to verification of DBP levels in trout rations from the carcinogenesis study is described. Control ration (0 ppm DBP) was screened for possible DBP contamination and none was found. This is the first report on analysis of DBP in experimental animal diets.

Monocarboxylic and dicarboxylic acids from Pseudotsuga menziesii bark

Abstract The benzene-soluble, n -hexane-insoluble extract from the bark of Pseudotsuga menziesii (Mirb.) Franco was found to contain a number of n -fatty acids and α,ω-dicarboxylic acids ranging in chain length from 16 to 28 and 16 to 24 carbons, respectively.

Metabolism and dna-binding in vivo of aflatoxin B, in medaka (Oryzias Latipes)☆

1. The medaka (Oryzias latipes), a small aquarium fish, was shown to possess the capacity to rapidly activate AFB1 in vivo at 25 degrees C to intermediates that bind to DNA. 2. The dose-response for in vivo AFB1-DNA binding was linear over the range 70-550 micrograms AFB1/kg body weight. 3. Maximum binding occurred within the first 24 hr after i.p. injection of [3H]AFB1, followed by a rapid loss of adducts. 4. Aflatoxicol (AFL) and unreacted AFB1 were found by HPLC analysis to be the major products excreted into water after AFB1 exposure, with excretion of AFL as early as 2 min after AFB1 injection. 5. These studies show that medaka possess enzymatic systems similar to rainbow trout (Salmo gairdneri) for biotransformation of AFB1 to the epoxide and to other phase I and phase II metabolites.