/ . Embryol. exp. Morph. Vol. 16, 1, pp. 29-39, August 1966 Printed in Great Britain 29 The relationship of chemical structure to teratogenic activity among bisazo dyes: a re-evaluation By J. B. LLOYD 1 & F. BECK2 From the Departments of Biochemistry and Anatomy, University College of South Wales and Monmouthshire INTRODUCTION Although the potency of trypan blue as a teratogenic agent in rodents has been known for almost twenty years the mechanism of its action remains obscure. The dye produces a variety of biological effects (see review by Beck & Lloyd, 1966) and most of these have at some time been suggested as possibly relevant to its teratogenicity. The investigation of such correlations would clearly be assisted by determining whether the biological effects of the dye are individually modified by small changes in its chemical structure, particularly if these changes also result in differences in its teratogenicity. The first teratological study of dyes related to trypan blue was made by Gillman, Gilbert, Spence & Gillman (1951), who obtained negative results in rats with six dyes (methylene blue, trypan red, Sudan IV, Bismarck brown, Niagara blue and sky blue), but gave no experimental details of their investigation. Later Wilson (1955) studied the effects of fourteen dyes on rat gestation by injecting 10 mg of each subcutaneously on each of days 7, 8 and 9 of pregnancy. He obtained large numbers of malformed offspring at term only from trypan blue, while Evans blue, Niagara blue 4B and Niagara sky blue 6B, the four dyes most closely related to trypan blue in structure, were found to be teratogenic but to a far lesser degree. In the same year Tuchmann-Duplessis & Mercier-Parot (1955) reported that azo blue was not teratogenic. Beaudoin & Pickering (1960) tested Niagara blue 2B (see Table 1 for formula) and sixteen specially synthesized compounds resembling all or part of the trypan blue molecule. Each dye was administered by a single injection of 140 mg/kg intraperitoneally into rats on the 8th day of gestation. Only two of these substances produced malformed offspring at term and then in very small numbers. Beaudoin (1961) also tested several dyes against the developing chick, and found that only trypan blue, Evans blue and Niagara blue 4B were more teratogenic than saline. 1 Author's address: Department of Biochemistry, University College of South Wales and Monmouthshire, St Andrews Place, Cardiff, U.K. 2 Author's address: Department of Anatomy, University College of South Wales and Monmouthshire, Newport Road, Cardiff, U.K. 30 J. B. LLOYD &F. BECK A search of the literature indicates therefore that trypan blue is the only dye able to cause a high incidence of foetal malformation, that even slight modification of its formula reduces its teratogenic activity very greatly and that the majority of related dyes are completely inactive. Certain features of this earlier work, however, suggest the need for a re-assessment of the situation. Authenticity and purity of dye samples used Commercially obtained dyestuffs frequently contain large quantities of both inorganic and organic contaminants. The principal inorganic impurity is sodium chloride, which is used in the salting-out stage of manufacture, but which is usually not removed from the final product as it improves the dyeing qualities. Sodium chloride though not, of course, likely to modify the teratogenic properties of a dye, is present in some samples in such large quantities that it displaces dyestuff as the principal component. A recent investigation (Lloyd & Beck, 1963), has shown that among a random sample of bisazo dyes marketed for biological staining the salt content ranged from nil to almost 80 %. It hardly needs to be emphasized that if such dyes were used without purification for teratogenesis experiments, the dose required to elicit a given response would vary within wide limits; the different teratogenic dose-levels reported by various workers for trypan blue may well be a reflexion of this. In addition, paper chromatography has shown that bisazo dyes often contain substantial quantities of coloured impurities (Lloyd & Beck, 1963) and variation between samples in the nature and amount of these impurities has led to much confusion. Indeed it has only recently become apparent (Beck & Lloyd, 1963 a) that the active teratogen in commercial trypan blue is trypan blue itself and that the coloured contaminants do not modify the activity except in so far as they act as diluents. Again paper chromatography frequently reveals a qualitative difiFerence between the principal coloured components of the various manufacturers' samples of dye (Lloyd & Beck, 1963). This calls in question the authenticity of some of the samples available and suggests the need for a chemical test to verify the identity of each sample. Such a test has been devised (Lloyd & Beck, 1964) and its application has confirmed the impression that mislabelling of dyes is not infrequent. One example will suffice to illustrate this point: of six samples of Evans blue obtained for the present investigation only four were authentic, one being trypan blue and another Niagara blue 6B. Clearly, had no check been made on them before determining their teratogenic activity, the results would have been misleading and contradictory. Dosage Most previous workers have confined their investigations to administration of the dyes at a single dose level. Our experience with trypan blue (Beck & Lloyd, 1964) has shown that adequate assessment of teratogenic potency cannot be made in this way because an ' optimum teratogenic dose' exists, below which Chemical structure and teratogenic activity 31 response falls off rapidly and above which embryonic death masks any abnormalities of embryonic development. A strong possibility exists, therefore, that the low incidence of malformed foetuses observed after administration of certain dyes is not the result of a low intrinsic potency but of the administration of a suboptimal dose. Similarly, a high maternal or foetal mortality might indicate a potent teratogen given in too large a dose. The interpretation of intrauterine death Beck & Lloyd (1963 b) have shown that if trypan blue is given at 8-5 days at 50 mg/kg (the optimum teratogenic dose) the primary response is embryonic malformation but that, during the remainder of gestation, many of the more severely affected foetuses die, leading at term to the presence of a relatively small number of malformed young accompanied by evidence of extensive foetal resorption. Consequently if a dye (e.g. Niagara blue 2B; Beaudoin, 1962) induces foetal resorptions but few if any malformed survivors at term, the implication may be that the dye is a potent teratogen inducing malformations which prove lethal before term, a possibility which can be verified by examining treated embryos early in gestation. The above considerations, as well as differences among earlier reports regarding the route and time of administration, the use of single or multiple doses, the definition of abnormality and the presentation of results have led us to investigate the teratogenic activity of four dyes closely related to trypan blue. Compounds of known composition and purity were used, and were applied at several different dose-levels. Time and route of injection were standardized as were the time of killing of the mother and the assessment of malformation among the offspring. In addition, experiments were carried out to determine serum levels of each of the dyes in adult rats at various times after injection. MATERIALS AND METHODS Dyes Table 1 shows the structural formula of trypan blue and the four dyes used in the present investigation. Apart from Evans blue they differ only in the substituents on the biphenyl nucleus; Evans blue and trypan blue are isomers, differing in the positions of the sulphonate groups on the naphthalene rings. Except in the case of Afridol blue, which was especially synthesized by Ciba Clayton Ltd., several commercial samples of each dye were obtained. One of each was selected, having been confirmed as authentic by paper electrophoresis of its reduction products (Lloyd & Beck, 1964), and shown to be reasonably free of coloured impurities by ascending paper chromatography in «-butanol: pyridine:water, 1:5:4 (Lloyd & Beck, 1963). A solution in water was then dialysed against running tap water for several days to remove salt and other diffusible impurities, filtered through sintered glass, and passed through a column 32 J. B. LLOYD & F. BECK of Dowex 50 W (x 4,20-50 mesh, H+ form) to remove final traces of cations and to convert the dye into the free acid form. The solution was evaporated to dryness in vacuo, the dye dried overnight in vacuo at 50 °C over P2O5 and subsequently a 1 % solution in distilled water prepared. The purity of each dye was estimated by titration with 0-05 N titanous sulphate solution and was found to be 90% for Niagara blue 2B, 91 % for Niagara blue 4B, 91 % for Afridol blue and 100 % for Evans blue. Table 1. Structural formulae of dyes used NH OH OH •N=N—( v ,)—(K Name Colour index no. (Colour Index, 1956) Trypan blue Niagara blue 2 B Niagara blue 4 B Afridol blue Evans blue 23850 22610 24400 — 23860 NH, /V-N=N Substituents A f X Q R CH 3 H OCH 3 Cl CH 3 SO 3 H SO3H SO3H SO3H H H H H H SO3H Teratogenesis experiments Wistar rats from an inbred laboratory strain propagated by brother-sister mating were used, and pregnancy diagnosed by vaginal smearing. Taking midnight of the night of mating as the time of conception, animals were injected subcutaneously at 8-5 days with a 1 % solution of dye and killed with chloroform at 20-5 days. The uteri were removed, foetal resorption sites counted and live embryos examined for evidence of external malformation. In the case of Niagara blue 4B two further groups were killed at 11-5 and 14-5 days following dye treatment at 8-5 days, and in the case of Evans blue additional animals were killed at 20-5 days following 7-5-day injection. Serum level determinations Male rats of the same strain as those in the teratogenesis experiments were used for dye serum level determinations after a preliminary experiment had shown that there was no sex-dependent difference in response. Animals were injected subcutaneously with a 1 % solution of dye and individuals killed at varying intervals after injection by withdrawal of blood from the aorta under light ether anaesthesia. The blood was allowed to clot and the serum (isolated after centrifugation) was suitably diluted with pH 8-6 sodium barbitone-hydro- Chemical structure and teratogenic activity 33 chloric acid buffer. The dye concentration was estimated by measuring light extinction at 600 m/i with a Unicam SP600 spectrophotometer. RESULTS The results of the teratogenesis experiments are presented in Table 2 and Fig. 1, the data for trypan blue having been presented in a previous publication (Beck & Lloyd, 1964). It may be seen that in addition to trypan blue, Niagara blue 2B and Afridol blue are potent teratogens, the three dyes producing a very similar Table 2. Teratogenic response to four bisazo dyes injected subcutaneously at 8-5 days of pregnancy No. of mothers Dye Niagara blue 2B Niagara blue 4B Afridol blue Surviving Total Resorbed Abnormal Normal , to \ /— > t— Dose Inimplanta- r— A (mg/kg) jected term tions No. %* No • 0//o * No. 0//o * A - * 150 200 300 11 13 14 7 13 12 13 11 10 14 8 11 10 9 11 12 12 5 13 11 11 5 10 14 8 11 9 8 86 7 33 46 53 31 39 64 50 22 32 16 57 45 71 50 7 7 70 13 100 150 200 8 8 10 8 7 7 72 70 74 31 66 58 50 100 150 200 50 75 100 150 25 50 100 Evans blue 97 114 128 53 122 109 114 50 123 134 77 113 80 1 0-9 89 90 28-7 4 3-5 77 40-7 32 22-2 50 100 0 0 0 33-5 2-4 88 3 36-4 0 0 70 56-6 0 0 50 100 0 0 0 17-2 9 7-6 92 260 11 7-7 91 21-8 13 16-3 48 50-3 21 17-2 35 58-7 10 13-2 25 81-7 7 10-6 8 1 16-3 1 1 56 2-5 39 48-4 2 95-2 4 4-8 0 79-8 2 2-4 14 N 901 67-8 37-1 0 641 63-6 43-4 0 75-2 66-3 61-9 32-5 28-1 7-7 82-6 491 0 17-9 * Percentages represent the arithmetic means of the percentage within each individual litter; this enables the standard error of the mean resorptions and malformations for each dose to be calculated and shown in Fig. 1. pattern of response, the chief difference being that whereas trypan blue has an optimum teratogenic dose in the region of 50 mg/kg Niagara blue 2B and Afridol blue are maximally active as teratogens at several times this dose. The teratogenic potencies (the percentage of external malformation observed at term at the optimum teratogenic dose) of the three dyes are strikingly similar. In contrast Niagara blue 4B and Evans blue, although producing much intrauterine mortality, do not at any dose lead to the appearance of more than a very few malformed foetuses at term. Fig. 2 presents graphically the marked variation observed in toxicity of the 3 JEEM l6 34 J. B. LLOYD & F. BECK various dyes to the mother; Niagara blue 4B is seen to be the most potent of the dyes in this respect, killing over 50 % of mothers before term when administered at 150 mg/kg. Direct measurement of the toxicity of Niagara blue 4B and of the less toxic dye Afridol blue were also performed on male rats. The results confirmed those seen in Fig. 2 in that the Ld50 (Karber, 1931) over a 12-day period was 179 mg/kg for Niagara blue 4B and over 400 mg/kg for Afridol blue. 100 - i 50 100 Niagara blue 2B 80604020 - 100- 250 300 250 300 250 300 250 300 80 - Niagara blue 4B 6040 20 - 10080- 50 100 60- A 4020- 100-i 150 200 Afridol blue .Ai 50 Evans blue 100 150 X 40- 200 -I 8060- *- -?'''' 2050 100 150 200 Dose (mg/kg) Fig. 1. Dosage-response curves for the teratogenic activity of five bisazo dyes. , Resorptions; , abnormalities. 35 Chemical structure and teratogenic activity 60 -i Niagara blue 4B 50- 40- Evans blue £ 30 \ Niagara blue 2B £ 20 I v*- 1 " 1 " 1 10- / 50 —| 100 1 150 Afridol blue Trypan blue 1 200 Dose (mg/kg) 1— 250 —r~ 300 Fig. 2. Maternal mortality within 12 days of administration of various bisazo dyes. Trypan blue (174) Hours Fig. 3. Serum levels following injection of 50 mg/kg of various dyes (figures in parenthesis are the average levels over the first 24 h). 3-2 36 J. B. LLOYD & F. BECK Fig. 3 shows the serum levels of the five dyes at intervals after subcutaneous injection of 50 mg/kg. By calculation of the areas under the curves it is possible to obtain the average concentration over the first 24 h, and these values are given in parenthesis. The results suggest an explanation of the different optimum teratogenic doses of the three active dyes; they imply that, in order to reach serum levels comparable with those reached by trypan blue when administered at 50 mg/kg, Niagara blue 2B and Afridol blue would have to be given at significantly higher doses. It may therefore be supposed that differences between these dyes as teratogens are in part reflexions of differences in their handling by the mother, particularly in rate of release from the subcutaneous injection site. Table 3. Teratogenic response to Evans blue injected subcutaneously at 7-5 days of pregnancy No. of mothers Dose (mg/kg) Injected 100 150 10 6 Surviving Total to implanterm tations 10 6 76 71 Resorbed A , > 0/ * No. /o 27 65 301 90-9 Abnormal A , , 0/ * No. /o 9 0 12-7 0 Normal , * 0/ No. /o * 40 6 57-2 9- 1 *See footnote to Table 2. Evans blue differs markedly from the other dyes in its very slow release into the bloodstream, the maximum concentration being reached only after 36 h (Fig. 3). Since the average serum level during the first 24 h is only 27 /*g/ml, it might be estimated that doses of 300 mg/kg or higher would be needed to give teratogenic effects. At this dose the dye would be highly toxic to the mother (Fig. 2) leading almost invariably to maternal death before term. An alternative method of achieving adequate serum levels utilizes the fact that average serum levels in the period 24-48 h after injection is 60 /tg/ml. Consequently two series of rats were injected with Evans blue at 7-5 days of pregnancy at doses of 100 and 150 mg/kg. The results (Table 3) show that considerable teratogenic potency is observed at the lower of the two doses. With Evans blue, therefore, a teratogenic effect similar to that shown by the other dyes can be demonstrated if adequate serum levels can be maintained over the susceptible period. Wilson's (1955) demonstration of the teratogenic potency of Evans blue is therefore explicable, for he administered the dye in divided doses, beginning at day 7 (7-5 days of pregnancy according to the present authors' convention), and his results, when allowance is made for a different method of presentation, are not unlike those in Table 3. From Fig. 3 one would predict that Niagara blue 4B might have a high teratogenic potency at doses of about 150 mg/kg because at this level of dosage the Chemical structure and teratogenic activity 37 average serum levels attained in the first 24 h might be expected to be comparable with those following the optimum teratogenic doses of the other dyes. However, in this case the complicating factor of a high toxicity alters the picture. At 150 mg/kg Niagara blue 4B causes a 55 % maternal mortality and the total resorption of litters in the survivors, suggesting that the foetal mortality observed at term following the administration of Niagara blue 4B may well represent not malformed embryos dying before 20-5 days but a direct toxic effect comparable with that observed among treated mothers. In order to test this hypothesis two further series of animals were injected at 8-5 days of pregnancy with Niagara blue 4B at 100 mg/kg and killed at 11-5 or 14-5 days. The results (Table 4) show that the vast majority of resorption sites seen at term are due to death of conceptuses within 3 days of injection. This suggests that a direct toxic effect rather than the secondary consequences of induced malformation is responsible for the embryonic loss. Table 4. The effect of 100 mg/kg Niagara blue 4B injected subcutaneously at 8-5 days of pregnancy No. of mothers A , > Total Resorbed A Day In- Sur- implan- , > killed jected viving tations No. %* 11-5 14-5 20-5 8 9 13 8 9 11 73 86 114 34 49 73 47-8 61-7 566 Abnormal A , * No. %* 4| 1 0 7-3 10 0 Normal , * * No. %* 35 36 41 44-9 37-3 43-4 * See footnote to Table 2. t Including two embryos showing doubtful abnormalities of the body axis. DISCUSSION The evidence presented is consistent with a hypothesis that the dyes investigated will demonstrate high teratogenic potency if present in the blood at an average concentration of 150-300 /*g/ml for a period of 24 h between 8-5 and 9-5 days of gestation. In the case of four dyes, trypan blue, Niagara blue 2B, Afridol blue and Evans blue, this has been shown to be the case. The remaining dye Niagara blue 4B is highly toxic to the maternal organism when present in these concentrations, and the ensuing maternal and embryonic death masks any teratogenic effects. The four examples investigated are probably not the only teratogenic bisazo dyes. Beaudoin (1% 4 ) has found that Congo Red (C.I. 22120), previously thought to be inactive (Wilson, 1955), is capable of producing malformations if given at higher dose. The malformations observed, however, were all of the viscera, so that a direct comparison with the present results is not possible. 38 J. B. LLOYD & F. BECK Although alterations in chemical structure are certain to modify embryopathic activity to some extent, the increasing probability that most, if not all, bisazo dyes are potential teratogens should direct attention from the differences between 'teratogenic' and 'non-teratogenic' dyes towards a study of the means whereby they elicit their response. SUMMARY 1. Samples of five bisazo dyes, trypan blue, Niagara blue 2B, Niagara blue 4B, Afridol blue and Evans blue, of confirmed identity and known purity, have been tested as teratogens by sucbutaneous injection into the Wistar rat. Each dye except Niagara blue 4B, if administered at an appropriate dose and stage of pregnancy, shows high activity. Niagara blue 4B at low dose produces a few malformed survivors at term, but in higher doses leads to considerable maternal and embryonic mortality. 2. Serum dye concentrations at intervals after subcutaneous injection were calculated and it was found that when injected at doses which gave maximum teratogenic response serum levels of the same order over the susceptible period were maintained for each dye. The hypothesis is advanced that the observed differences in teratogenic behaviour of the dyes to some extent reflect differences in the handling of the dyes by the mother rather than absolute differences in activity. RESUME Relation entre la structure chimique et Vactivite teratogene de colorants azoiques: une re-evaluation 1. Des echantillons de cinq colorants azoiques, le bleu trypan, le bleu Niagara 2B, le bleu Niagara 4B, le bleu Afridol et le bleu Evans, de nature certaine et de purete connue, ont ete testes en tant que substances teratogenes par des injections sous-cutanees chez le rat Wistar. Chaque colorant, a l'exception du bleu Niagara 4B, administre a une dose et a un stade de la gestation adequats, montre une haute activite. Le bleu Niagara 4B, a faible dose, produit quelques survivants malformes qui vont jusqu'a terme, tandis qu'a hautes doses il cause une mortalite maternelle et foetale considerable. 2. Les concentrations des colorants dans le serum ont ete calculees a differents intervalles de temps apres les injections sous-cutanees et les resultats montrent que, lorsque les injections sont faites a des doses qui ont l'effet teratogene maximum, les teneurs du serum, pour chaque colorant, sont maintenues du meme ordere au cours de la periode sensible. Une hypothese est avancee: les differences observees dans les effets teratogenes des colorants refleteraient, dans une certaine mesure, plutot des differences dans le sort de ces colorants dans l'organisme maternel que des differences absolues d'activite. Chemical structure and teratogenic activity 39 We thank Mr A. Griffiths for carrying out some of the spectrophotometric analyses, Ciba Clayton Ltd. for preparing and supplying a sample of Afridol blue, the Medical Research Council and the Spastics Society for financial support, and Professors K. S. Dodgson and J. D. Lever for their encouragement and criticism. We should also like to acknowledge the excellent technical assistance of Miss G. M. Perry and Miss B. Humphreys. REFERENCES BEAUDOIN, A. R. (1961). Teratogenic activity of several closely related disazo dyes on the developing chick embryo. /. Embryol. exp. Morph. 9, 14-21. BEAUDOIN, A. R. (1962). Interference of Niagara blue 2B with the teratogenic action of trypan blue. Proc. Soc. exp. Biol. Med. 109, 709-11. BEAUDOIN, A. R. (1964). The teratogenicity of Congo red in rats. Proc. Soc. exp. Biol. Med. 117, 176-9. BEAUDOIN, A. R. & PICKERING, M. J. (1960). Teratogenic activity of several synthetic compounds structurally related to trypan blue. Anat. Rec. 137, 297-305. BECK, F. & LLOYD, J. B. (1963 a). The preparation and teratogenic properties of pure trypan blue and its common contaminants. /. Embryol. exp. Morph. 11, 175-84. BECK, F. & LLOYD, J. B. (19636). An investigation of the relationship between foetal death and foetal malformation. /. Anat. 97, 555-64. BECK, F. & LLOYD, J. B. (1964). Dosage-response curves for the teratogenic activity of trypan blue. Nature, Lond. 201, 1136-7. BECK, F. & LLOYD, J. B. (1966). The teratogenic effects of azo dyes. Adv. Teratol. 1, 131-93. Colour Index (1956). Second Edition, The Society of Dyers and Colourists, Bradford, England, and The American Society of Textile Chemists and Colorists, Lowell, Mass. GILLMAN, J., GILBERT, C , SPENCE, I. & GILLMAN, T. (1951). A further report on congenital anomalies in the rat produced by trypan blue. S. Afr. J. med. Sci. 16, 125-35. KARBER, G. (1931). Beitrag zur kollektiven Behandlung pharmakologischer Reihenversuche. Arch. exp. Path. Pharmak. 162, 480-3. LLOYD, J. B. & BECK, F . (1963). An evaluation of acid disazo dyes by chloride determination and paper chromatography. Stain Technol. 38, 165-71. LLOYD, J. B. & BECK, F. (1964). The identification of some acid disazo dyes by paper electrophoresis of their reduction products. Stain Technol. 39, 7-12. TUCHMANN-DUPLESSIS, H. & MERCIER-PAROT, L. (1955). Influence du bleu trypan et de l'azobleu sur le developpement de l'embryon du rat. C. r. Ass. Anat. 42, 1326-30. WILSON, J. G. (1955). Teratogenic activity of several azo dyes chemically related to trypan blue. Anat. Rec. 123, 313-33. (Manuscript received 29 November 1965)
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