Vol. 28, No. 11, November 1977
FERTILITY A:-':lJ STERILITY COp:'I-Tight 1977 The Arnerican Fertility Society
Printed in U.S.A.
COMP ARATIVE STUDIES OF THE ETHYNYL ESTROGENS USED IN ORAL CONTRACEPTIVES: EFFECTS WITH AND WITHOUT PROGESTATIONAL AGENTS ON PLASMA CORTISOL AND CORTISOL BINDING IN HUMANS, BABOONS, AND BEAGLES* JOSEPH W, GOLDZIEHER, M,D.t C. BRANDON CHENAULT, M.D. ARMANDO DE LA PENA, M.S. TAZEWELL S. DOZIER DUANE C. KRAEMER, D.V.M., PH.D.:!: Southwest Foundation for Research and Education, San Antonio, Texas 78284
Ethynylestradiol and mestranol, in doses ranging from 50 to 100 pg/day, were given to women in 21-day cycles; baboons and beagle dogs received 1 and 4 pg/kg/day in a similar regimen. After a number of such cycles, megestrol acetate, norethindrone acetate, or dl-norgestrelwas given concomitantly. Plasma cortisol and percentage binding of cortisol were determined, and the level of free cortisol was calculated. Over this dosage range the effect of the two kinds of estrogen was indistinguishable. In women, 100 pg/day produced slightly higher levels of total plasma cortisol than 50 pg/day, but no other dose-related differences were seen in any of the three species. Estrogen caused a rise in total cortisol.(implying an increased synthesis of trans cortin by the liver) in humans and baboons; in the beagle, total cortisol fell transiently. In all three species, the percentage binding of cortisol increased during estrogen administration. There was avery slight, statistically demonstrable increase in total and free cortisol levels in humans and baboon, none in dogs. Of the three progestational compounds, norethindrone acetate and norgestrel produced a slight decrease in total cortisol, whereas megestrol had no effect in humans. The free cortisol was unaltered by these compounds. In both the baboon and the dog, the response was complex, and different from that seen in human subjects. The dog appears to be an inappropriate surrogate for man in the study of these hormonal effects. The validity of the baboon with respect to this progestin-induced effect requires further study; however, its response to estrogens is similar to that of man.
Unconjugated corticosteroids are present in blood in at least three forms: as free steroid, as steroid weakly bound to albumin, and as steroid tightly bound to a specific globulin called transReceived May 23, 1977; revised July 5, 1977; accepted July 12, 1977. *Clinical studies supported by Contract csd/2821, Office of Population, United States Agency for International Development; animal studies supported by Contract HD-2-2723, Center for Population Research, National Institute for Child Health and Human Development, United States Public Health Service. tReprint requests: Joseph W. Goldzieher, M.D., Southwest Foundation for Research and Education, P.O. Box 28147, 8848 W, Commerce Street, San Antonio, Tex. 78284. :j:Present address: Institute of Comparative Medicine, and Department of Veterinary Physiology and Pharmacology, Texas A & M University College of Veterinary Medicine, College Station, Tex. 77843.
cortin or corticosteroid-binding globulin (CBG). The complex equilibrium between these forms can be expressed by a set of six differential equations. I Experiments in vivo 2 • 3 and in vitro4 have suggested that CBG diminishes or abolishes the activity of corticosteroids by preventing their access to the cellular site of action. 5 This has led to belief that only the free steroid is biologically active. However, Keller et al,2 have shown that bound steroid readily acts upon rat liver cells, and subsequent experiments by Rosner and Hochberg3 are also consistent with this observation. Thus, it is no longer possible to say that only unbound corticosteroid is biologically active: some tissues may permit CBG-bound steroid to initiate cellular responses. Hyperestrogenic states such as pregnancy substantially increase the level of total plasma cor-
1182
I
Vol. 28, No. 11
COMPARATIVE STUDIES OF ETHYNYL ESTROGENS
tisol. Much ofthis elevation is due to an increased level of CBG and its associated cortisol, but the unbound plasma cortisol is also increased by a factor of about 2 to 3. Why this situation does not consistently produce a clinically observable hypercorticoid state has not been satisfactorily explained. Estrogen therapy, or the use of estrogen-containing steroidal contraceptives, also increases the total plasma cortisol. 4 • 5 There are conflicting reports as to whether there is also an increase in unbound cortisol. Bulbrook et al. 6 found a free cortisol level of 1.08 /Lg/dl in control subjects as against 1.16 /Lg/dl in oral contraceptive users, a difference which was not statistically significant. Burke 7 found the median free cortisol level in 13 oral contraceptive users to be significantly above the control median, but 11 of the 13 values were still within the normal range. Others have made generally similar observations which are consistent with reported increases in urinary free cortisol excretion. Doe et al. 8 administered 200 /Lg/day of ethynylestradiol for 14 days, and found that the free cortisol level increased from 1.40 ± 0.40 to 2.31 ± 0.72 /Lg/dl. Wajchenberg et al. 9 administered 2000 /Lg/day for 10 days to 10 subjects; the unbound cortisol increased from 5.4 ± 0.6 to 10.2 ± 0.4 /Lg/dl. The progestational agents in oral contraceptives, with the exception of the estrogenic compound norethynodrel, are said not to alter the total plasma cortisol, the percentage binding, or the level of free hormoneY)' 11 However, Pekkarinen and Pulkkinen l2 appear to have noted a difference between megestrol acetate and norethindrone acetate. Clearly, in a study of the effects of contraceptive steroids on adrenal function, both the total and the unbound plasma cortisol levels must be measured. Such measurements also reveal the effect of these steroids on CBG synthesis, an important hepatic function. Different species show different responses to estrogens in this respect; indeed, there are differences even within the nonhuman primates, for the rhesus monkey does not respond to estrogen with increased CBG synthesis, whereas the green monkey (Cercopithecus aethiops sabeus) and the baboon do. If experimental animals are to be used to model the biologic effects of steroidal agents, it is essential to select a species whose reaction resembles that of man. For this reason, experiments in beagle dogs and baboons were initiated to evaluate the effects of ethynylestradiol and mestranol, at different dose levels, with or without concomitant administration of certain progestational compounds. The
1183
experimental protocol was similar to that used previously in human subjects. I:!
MATERIALS AND METHODS
Details of the investigational design have been published. 13 Briefly, normal adult female volunteers were assigned randomly (as far as possible) to treatment with oral doses of 50 or 80 /Lg of ethynylestradiol or 50, 80, or 100 /Lg of mestranol daily in the usual 21-day contraceptive regimen. The women taking the lowest estrogen dose were protected with an intrauterine device (IUD), which upset random assignment to this group. After six cycles of therapy, the subjects in each of the five groups were divided into three subsets which received, in addition to the same dose of estrogen, a progestational agent consisting either of norethindrone acetate (2.5 mg/day), megestrol acetate (2 mg/day), or dl-norgestrel (0.5 mg/day). This combination was administered for an additional six cycles. Blood sampling for various endocrine and metabolic studies was always carried out toward the end of the treatment cycle. A group of women using only IUDs was sampled in the same way, as a control population. Inbred beagle dogs of an average weight of 6.9 kg were assigned randomly to oral treatment regimens consisting of 1 or 4 /Lg/kg/day of ethynylestradiol or mestranol for 21 days, followed by 7 days without drug, to simulate the human regimen. This program was used for four cycles, after which each of the four groups was subdivided into three, and one of the three progestational agents (norethindrone acetate, 1 mg/day; megestrol acetate, 1 mg/day; or dl-norgestrel, 0.5 mg/day) was given together with the estrogen for an additional four cycles. The treatment was then discontinued, and the animals were studied once again 3 months later. Blood samples were obtained before treatment; during the last week of treatment cycles 1, 2, 4, 5, 6, and 8; and once again 3 months after the end of treatment. A similar design was used for the study of adult female baboons, weighing 13.6 kg on the average. A total of 60 beagles and 60 baboons was used. There were two replications of each protocol in each species to randomize time- and seasondependent biases. In addition, entry of the 30 animals in each replicate into the experiment was staggered for logistical reasons. This further randomizes the effect of any methodologic variance. The animals were assigned to the
GOLDZIEHER ET AL.
1184
various drug-dose groups by a computer-generated random allocation. Pills containing the various dose levels of ethynylestradiol, mestranol, norethindrone acetate, megestrol acetate, or dl-norgestrel were prepared by Wyeth Laboratories, Philadelphia, Pa., with precise quality control to ensure homogeneous bioa vailabili ty. Blood samples were obtained from baboons under minimal Sernylan tranquilization. No sedation was required for sampling the beagles. Plasma samples were deep-frozen immediately. Cortisol was determined by our modification of the co~petitive protein-binding technique,14. 15 and protein binding by the equilibrium dialysis method of Forest et a1. 16 After completion of the investigations, all data were transferred to computer tapes and verified. To initiate statistical analysis, it was necessary to determine whether or not the data conformed to a normal distribution, so that the appropriate (parametric, nonparametric) methods could b.e applied. Data for each replicate and each expenmental condition (species, drug, dose, cycle of use) were statistically analyzed by computer, and no sets were found which violated the normal distribution. The next task was to compare by ttest each experimental point (species, cycle, dose) for the two estrogens, to determine whether the type of estrogen, at equal dosage, produced any difference in any of the variables we measured. Percentage binding was studied after arc sin transformation. A similar set of analyses was then performed to compare different doses of the same estrogen, by species and by cycle, for each of these variables. In cases where no differences were observed between types and/or doses of estrogen, it was considered legitimate to combine treatment groups, thereby increasing sample size. Next, a three-way analysis of variance examined the effects of estrogen dose, cycle of use, effect of the added progestational compound, interaction between estrogen dose and cycle number, interaction between estrogen dose and type of progestational agent, and interaction of estrogen, cycle number, and progestational agent. Finally, an analysis for (3-error was carried out to estimate the likelihood of missing real differences (i.e., false negatives). RESULTS
Total Plasma Cortisol Human Subjects. Women using an IUD served
November 1977
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as one control population. The mean total cortisol (TC) value of this group was 13.3 ± 7.7 p,g/dl SD (n = 147), with a range from 10.6 to 17.2 p,g/dl. Estrogen administration to the test group caused a rapid rise in TC levels which appeared to plateau after one cycle of treatment (Fig. 1). A statistical comparison between similar dose levels of ethynylestradiol (EE) and mestranol (ME) was performed on the TC levels at cycle 6 (completion of estrogen treatment) as well as on the sum of all TC measurements at cycles 1, 3, and 6. The values were extremely close (Table 1). The differences, ifreal, are trivial and would require very large sample sizes for proof. It may be concluded that the effect of similar doses of these two estrogens, over the range examined, is indistinguishable. For subsequent analyses, the data from the groups receiving the 50-p,g ME and 50-p,g EE doses were combined, as were the 80-p,g ME and 80p,g EE data. The effect of the dose of estrogen on TC is also shown in Figure 1. There was a slight difference after the first cycle of treatment: 50 p,g = 29.4 p,g/dl, 80 p,g = 32.3 p,g/dl, and 100 p,g = 35.8 p,g/?l. Compared with the variance (the standard deVIation ranged from ±10.3 to ±14.7p,g/dl), these differences are very small, and insignificant clinically. They are also not significant statistically unless all of the values for cycles 1, 3, and 6 at each dose level are combined. In this case, there is still no difference between the TC levels for 50 and 80 p,g/day (n = 130 and 186, respectively). The (3-error for this comparison is 0.39. However, the difference between the effect of 80 p,g/day (33.1 ± 10.5 p,g/dl [n = 186]) and 100 p,g/ day (35.8 ± 10.0 [n = 79]) was statistically significant (p < 0.05), and the difference between the 50- and 100-p,g levels was significant (p < 0.01). It is concluded that there is a very slight, statis-
Vol. 28, No. 11
COMPARATIVE STUDIES OF ETHYNYL ESTROGENS
1185
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r GOLDZlEHER ET AL.
1186
TABLE 2. Total Plasma Cortisol Levels, by Cycle, for All Estrogen Regimens Combined, in Baboons and Beagles" Baboons Treatment cycle
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cant. The TC level remained at the same elevation throughout the phase of estrogen therapy. Upon the addition of progestin, there was a further statistically significant rise, followed by a consistent decline, and a return to a level not significantly different from the initial value by cycle 8. Three cycles without treatment produced no further significant fall in the total plasma cortisol level. Thus, a prompt and stable rise was produced by estrogen; superimposition of progestins caused a biphasic response consisting of an elevation, followed by a rapid decline to pretherapy levels. There was no significant difference between the three progestins. Beagles. Once again, analysis showed no statistically significant difference between estrogens, by type or by dose, on the TC level, which is very low in this species (Table 2). As with the baboon data, the TC levels are displayed for the groups of animals destined to receive a particular progestational agent, without regard to the type or dose of estrogen administered (Fig. 2, bottom). 70
November 1977 The initial TC levels of the three sets were very similar (3.3, 4.7, and 4.9 j.tg/dl); the expanded ordinate scale must be kept in mind. Initiation of estrogen therapy produced a decrease in TC in the first cycle which was statistically significant. This was followed by a gradual rise to pretreatment levels or above, by the last estrogen cycle. The addition of norethindrone acetate (A) caused a further, statistically significant, rise in TC (4.0 to 6.0 j.tg/dl) which persisted throughout treatment. The absolute rise is, of course, relatively small. Pretreatment values were restored after 3 months without treatment. Norgestrel (B) appeared to have no effect on the elevated TC level; interestingly, this elevation did not revert entirely to normal by the end of the study. Megestrol acetate (C) caused a prompt and sustained decrease in TC (5.2 to 3.4 j.tg/dl) which also persisted into the post-treatment period.
Cortisol Binding Human Subjects. The percentage cortisol binding (PCB) in the IUD subjects averaged 87.6% ± 1.9%, and the initial value for all test subjects averaged 88.4% ± 2.8% (n = 160). By the end of the first cycle, PCB had risen to 92.7% ± 1.5% and remained at this level throughout the entire treatment. There was no difference between ethynylestradiol and mestranol, or between estrogen doses, and no progestational effect was observed. Animal Studies. The level of PCB in the two species is shown in Figure 3. It is slightly higher in the baboon than in the dog (83.3% ± 2.2% versus 80.9% ± 3.8%). The reaction to estrogen is similar in the two species. The dose or type of estrogen made no significant difference in the degree of binding, suggesting that a maximal effect was obtained with all four regimens. Binding
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1187
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Human Subjects. The level of free plasma cortisol (FC) in the IUD population averaged 1.7 ± 1.0 JLg/dl (n = 147); the pretreatment value for the test group was 1.9 ± 0.9 JLg/dl (n = 160). As is shown in Table 3, there was no difference between the effect of ethynylestradiol and mestranol at equal doses, and there was no dose-related effect over the range studied. Even when all of the data for cycles 1, 3, and 6 for both estrogens were combined, the FC level at 50 JLg/day (2.4 ± 1.2 JLg/dl, n = 130) did not differ from that at 80 JLg/day (2.4 ± 0.9 JLg/dl, n = 186) nor from that at 100 JLg/day(2.6 ± 0.9 JLg/dl,n = 79). Theeffectofestrogen (Table 4; Fig. 4) was already maximal by the end of the first cycle, having risen from 1.9 ± 0.9 JLg/dl to 2.5 ± 0.9 JLg/dl (n = 150, P < 0.01). The values at cycle 3 (2.5 ± 1.1 JLg/dl, n = 137), cycle 6 (2.3 ± 1.0 JLg/dl, n = 108), and cycle 12 (2.3 ± 1.0 JLg/dl, n = 103) were not significantly different. The effect of the various progestational compounds on the estrogen-stimulated level ofFC was examined statistically for each estrogen at each TABLE 4. Free Plasma Cortisol Levels, by Cycle, for All Estrogen Regimens Combined, in Human Subjects, Baboons, and Beagles Treatment cycle
Human subjects
Treatment cycle
pgldl
0 1 3 6 12
H3 2.5 2.5 2.3
± ± ± ±
0.9 0.9 1.1 1.0
2.3 ± 1.0
Baboons pgldl
0 1 2 4 5 6 8 11
7.2 8.2 7.0 7.6 7.7 5.7 6.7 8.7
± 0.4 ± 0.3 ± 0.4 ± 0.2 ± 0.2 ± 0.3 ± 0.5 ± 0.7
Beagles pgldl
-0.82 0,63 0.56 0.90 0.96 1.0 0.96 0.94
± 0.18 ±-O.07 ± 0.01 ± 0.04 ± 0.24 ± 0.10 ± 0.16 ± 0.14
GOLDZIEHER ET AL.
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BABOON B
November 1977 nificant decline appeared during the first two cycles of estrogen treatment; this reverted to normal levels by the end of the fourth cycle. The addition of progestational compounds had no significant effect.
DISCUSSION
o
o
I
2
456
8
CYCLE FIG. 4. Free plasma cortisol.
dose level, and the FC level at cycle 6 was compared with that at cycle 12. No significant differences between the estrogen regimens were observed. When the data from all of the regimens were combined, the FC levels for those destined to receive norethindrone acetate (2.4 ± 1.0 /Lg/dl, cycle 6) did not change significantly with treatment (2.1 ± 0.7 /Lg/dl, cycle 12). Similarly, there was no effect of treatment with norgestrel (2.2 ± 0.9 /Lg/dl versus 2.2 ± 1.0 /Lg/dl) , nor with megestrol acetate (2.2 ± 0.9 /Lg/dl versus 2.6 ± 1.1 /Lg/dl. It is clear that the effects of the progestational compounds on total cortisol and percentage binding compensate one another so that the net effect of each progestational compound on free cortisol is negligible. Animal Studies. As is shown in Table 3, there was no difference between ethynylestradiol and mestranol at either dose level, and there was no difference between the effects of 1 /Lg/kg versus 4 /Lg/kg on FC: The data were therefore combined, as shown in Table 4 and Figure 4, which also shows the human data. The six cycles of estrogen treatment in women are graphed to compare with four cycles in the experimental animals, and cycle 12 in humans is compared with cycle 8 in the animals. Baboon FC levels rose significantly in the first cycle of estrogen treatment, then fell significantly at once, to return to base line levels. There was no further change during estrogen treatment, and none in the first cycle of progestin treatment. In the second progestin cycle, FC fell significantly below control levels, rose again by the end of treatment, and rebounded significantly above control levels 3 months after discontinuation of treatment. There was no difference in the effect of the three progestational agents, and all showed a similar pattern. In the beagle, the levels of FC were extremely low under control conditions. A statistically sig-
Both human subjects and baboons showed an increase in total plasma cortisol upon the administration of estrogens. The effect is known to be prompt, and stabilizes within the 1st month. The increase in TC levels in humans from 13 to 30 /Lg/dl, on the average, is very similar to that reported by others 6, 12. 17,18 and is proportionally somewhat greater than that in baboons. The latter species, however, already had a stress-induced elevation of total cortisol (43 /Lg/dl) at the start of the study, and comparisons are therefore difficult. The dog, on the other hand, showed an entirely different response, with a decrease during the first two cycles of estrogen treatment and a significant elevation above base line only at the end of the fourth estrogen cycle. In none of the three species could a difference between the two kinds of estrogen, at the same dosage, be demonstrated. This is consistent with our previous studies on human target tissues (endometrium, hypothalamic-pituitary system I3 ,19) but differs from the results of animal assays (for a review, see reference 20) and from the report by Schwartz and Hammerstein lO on the transcortin-binding capacity of hypoestrogenic human subjects given various estrogens or contraceptive preparations. These careful studies, on a very small number of patients (four per dose), showed that mestranol had 64% as much activity as ethynylestradiol, with 95% confidence limits of 39% to 86%. Care was taken to ensure similar bioavailability of the compounds; furthermore, normal women given commercial contraceptive formulations differing in the type, but not the dose, of estrogen used gave similar results. The reasons for the difference between our results and those of Schwartz and Hammerstein 10 are difficult to identify, since the type of subject and the techniques used, as well as the event measured, were different. Possibly the use of hypoestrogenic women permitted the dose-response curves to fall in a region where differences could be discriminated. There was no difference in the effect produced by different dose levels of these estrogens in baboons or beagles, and only a small, statistically demonstrable, difference between 50 and
Vol. 28, No. 11
COMPARATIVE STUDIES OF ETHYNYL ESTROGENS
100 jLg/day in human subjects. This finding is consistent with observations on albumin, ceruloplasmin, haptoglobin, and orosomucoid, which show a dose-response relationship which begins to plateau at about 50 jLg/day (roughly equivalent to 1 jLg/kg). Much larger doses have been shown to have greater effects, and higher levels, of course, are seen in pregnancy. The type and dose of estrogen made no difference in the percentage of cortisol bound, which increased from 88% to 93% within the first cycle in human subjects, and stabilized at this level. In the baboon, a rise from 83% to 87%, on the average, required two cycles of treatment. The effects in the beagle were similar, which is remarkable in view of the concomitant decrease in total plasma cortisol. It must be recalled, however, that the circulating cortisol levels in this species are very low to begin with,21 and the relationship of numerical changes to physiologically significant events is uncertain. The unbound cortisol undoubtedly accounts for the major share of the biologic activity of this steroid. In keeping with studies on combination type oral contraceptives, we found a small, but statistically significant, increase in human free plasma cortisol (1.8 ± 0.9 jLg/dl to 2.5 ± 0.9 jLg/dl) in the first cycle; the level remained stable thereafter, and was independent of the dose or type of estrogen administered, confirming our other observations on the relative potency of the two estrogen types and on the plateau of the dose-response curve. The degree of change is less than that seen by Doe et aLB in late pregnancy, using 200 jLg/day, and by Lindholm and Schultz-Moller,18 using doses similar to ours. Many of the treatment values overlap the normal range. The baboon showed only a transient rise in FC in the first cycle, after which the values returned to the normal range for the duration of estrogen treatment. In the beagle, the levels were extremely small to begin with (0.8 ± 0.2 jLg/dl), and changes of a few tenths of a microgram per decaliter are extremely difficult to interpret. The effect of progestational compounds on plasma cortisol dynamics is complex. Some of the 19-norsteroids are contaminated with minute but biologically important quantities of ethynyl estrogens, and others, such as norethynodrel, have intrinsic estrogenic properties. The metabolic conversion of these compounds to estrogens has also been suggested and apparently discounted. Some plasma proteins, such as albumin, may be decreased, while others, such as ceruloplasmin,
1189
may be increased. Moreover, the results of various investigations differ: Ylostalo et al,22 and Dale and Spivey23 observed effects of medroxyprogesterone acetate on albumin, total protein, and (X- and f3globulins at high doses, while Settlage et al,24 found no change with 10 mg/day. Pekkarinen and Pulkkinen 12 found a higher TC with megestrol acetate plus ethynylestradiol than with lynestrenol or norethindrone acetate plus ethynylestradiol. Schwartz and Hammerstein,IO on the other hand, found no effects of megestrol, norgestrel, norethindrone, or norethindrone acetate on the transcortin-binding capacity of hypo estrogenic subjects. In our studies, both norethindrone acetate and norgestrel decreased TC, whereas megestrol acetate had no effect in human subjects. In the baboon, all three progestins first increased, then decreased, TC; in the beagle, norethindrone acetate produced an increase, norgestrel had no effect, and megestrol acetate caused a decrease. In this instance, species differences are quite clear. None ofthe three progestins altered the slightly elevated level of FC in human subjects, and no effect could be detected on the very low level of FC in beagles. In the baboon, all three compounds produced a biphasic change in FC, consisting of a substantial drop in the second estrogen-pIus-progestin cycle, with a return almost to the normal FC level after two more cycles. Since these results are the product of replicate experiments carried out sequentially in a few animals at a time, it is extremely unlikely that they are a random event or the result of a methodologic flaw. The fall in FC occurred just after a cycle in which TC rose to a value higher than that produced by estrogen alone; i.e., the free cortisol, which did not rise along with the TC and percentage binding, was now dropping to subnormal levels as the TC was returning to the estrogen-induced plateau. Within the next two cycles, the TC dropped toward the control level while the FC rose almost to the pretreatment level. The significance and relationship of these changes is obscure, but it is important to note that neither change is observed in human subjects. Thus, while the baboon liver responds to estrogens with synthesis of CBG, as does that of man, the response to synthetic progestins differs from that of man; this must be taken into account in selecting appropriate animal models for pharmacologic studies. On the other hand, the beagle, which has a low plasma cortisol level to begin with, does not respond to estrogen with an increased
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GOLDZIEHER ET AL.
synthesis of CBG and an elevation of TC; in fact, TC falls rather than rises, while the FC is transiently depressed as well. Clearly, the hepatic response to estrogen, with respect to the synthesis of CBG, is very different from that of man. The response to added progestins also differs, for megestrol acetate produced a drop in TC in contrast to the response in humans, where no change was observed, and norethindrone acetate produced a rise, as contrasted to the fall in humans. Some of this may be a dose-related phenomenon, since it has been shown that compounds closely related to megestrol, such as chlormadinone acetate, are far more slowly metabolized by the dog than by man, in effect vastly increasing their potency. It may be concluded that the beagle is an inappropriate surrogate for man in the study of estrogenic effects on liver protein synthesis; it has already been shown to be inappropriate for studies of the metabolism and peripheral effects of 17acetoxy progestins. 25 The baboon appears to be a suitable model for estrogenic effects, but some effects of progestational compounds differ from those observed in man, and this matter will have to be elucidated before the validity of the experimental model in this context can be determined. Acknowledgments. We wish to express our appreciation for the expert technical assistance of Mr. C. Celaya, Mr. I. Gomez, Mr. D. Garg, anq Ms. J. Mandel, and for the quality-controlled tablets of ' the various steroids prepared by Wyeth Laboratories.
REFERENCES 1. Paterson JYF: The rate constants for the interaction of cortisol and transcortin, and the rate of dissociation of transcortin-bound cortisol in the liver. J Endocrinol 56: 551, 1973 2. Keller N, Richardson VI, Yates FE: Protein binding and the biological activity of corticosteroids: in vivo induction of hepatic and pancreatic alanine aminotransferases by corticosteroids in normal and estrogen-treated rats. Endocrinology 84:49, 1969 3. Rosner W, Hochberg R: Corticosteroid-binding globulin in the rat: isolation and studies of its influence on cortisol action in vivo. Endocrinology 91:626, 1972 4. Metcalf MG, Beaven DW: Plasma-corticosteroid levels in women receiving oral contraceptive tablets. Lancet 2: 1095, 1963 5. Williamson OH, Moody LO: Plasma cortisol after one to sixty cycles of oral contraception. J Reprod Med 5:19, 1970 6. Bulbrook RD, Herian M, Tong D, Hayward JL, Swain MC, Wang DY: Effect of steroidal contraceptives on levels of plasma androgen sulphates and cortisol. Lancet 1:628, 1973
November 1977 7. Burke CW: Biologically active cortisol in plasma or oestrogen-treated and normal subjects. Br Med J 2:798, 1969 8. Doe RP, Dickinson P, Zinneman HH, Seal VS: Elevated nonprotein-bound cortisol (NPC) in pregnancy, during estrogen administration and in carcinoma of the prostate. J Clin Endocrinol Metab 29:757,1969 9. Wajchenberg BL, Fazia AIM, Costa AA, Borges R, Nogueira 0: Effect of estrogen administration on plasma cortisol fractions in normal and panhypopituitary females. Metabolism 23:337,1974 10. Schwartz V, Hammerstein J: The oestrogenic potency of various contraceptive steroids as determined by their effects on transcortin-binding capacity. Acta Endocrinol (Kbh) 76:159, 1974 11. Barbosa J, Seal VS, Doe RP: Anti-estrogens and plasma proteins. II. Contraceptive drugs and gestagens. J Clin Endocrinol Metab 36:706, 1973 12. Pekkarinen A, Pulkkinen MO: The levels of free and conjugated 17-hydroxy corticosteroids (17-0HCS) in the plasma of users of oral contraceptives. Ann Chir Gynaecol Fenn 588:105, 1969 13. Goldzieher JW, Maqueo M, Chenault CB, Woutersz TB: Comparative studies of the ethynyl estrogens used in oral contraceptives. I. Endometrial response. Am J Obstet Gynecol 122:615, 1975 14. Pegg PJ, Keane PM: The simultaneous estimation of plasma cortisol and transcortin binding characteristics by a competitive protein binding technique. Steroids 14:705, 1969 15. de la Pena A, Goldzieher JW: Practical determination of total plasma cortisol by use of competitive protein binding. Clin Chern 20:1376, 1974 16. Forest MG, Rivarola MA, Migeon CJ: Percentage binding of testosterone, androstenedione and dehydroisoandrosterone in human plasma. Steroids 12:323, 1968 17. Briggs M, Briggs M: Plasma hormone concentrations in women receiving steroid contraceptives. J Obstet Gynaecol Br Commonw 79:946, 1972 18. Lindholm J, Schultz-Moller N: Plasma and urinary cortisol in pregnancy and during estrogen-gestagen treatment. Scand J Clin Lab Invest 31:119, 1973 19. Goldzieher JW, de la Peria A, Chenault CB, Cervantes A: Comparative studies of the ethynyl estrogens used in oral contraceptives. III. Effect on plasma gonadotropins. Am J Obstet Gynecol 122:625, 1975 20. Edgren RA, Sturtevant FM: Potencies of oral contraceptives. Am J Obstet Gynecol 125:1029, 1976 21. Plager JE, Knopp R, Slaunwhite WR Jr, Sandberg AA: Cortisol binding by dog plasma. Endocrinology 73:353, 1963 22. Ylostalo P, Vehaskari A, Kauppila A, Reinila M: Effects of high-dose medroxyprogesterone given for endometrial carcinoma on serum proteins. Ann Chir Gynaecol Fenn 63:86,1974 23. Dale E, Spivey SH: Serum proteins of women utilizing combination oral or long-acting injectable progestational contraceptives. Contraception 4:241, 1971 24. Settlage DF, Nakamura RM, Davajan V, Kharma K, Mishell DR Jr: A quantitative analysis of serum proteins during treatment with oral contraceptive steroids. Contraception 1:101, 1970 25. Hill R, Dumas K: The use of dogs for studies of toxicity of contraceptive hormones. Acta Endocrinol [Suppl 185] (Kbh) 75:74, 1974