POLYVINYLPYRROLIDONE (PVP) Explanation This substance was evaluated for acceptable daily intake for man (ADI) by the Joint FAO/WHO Expert Committee on Food Additives in 1966 and 1973 (see Annex I, Refs. 12 and 32). Toxicological monographs were issued in 1966 and 1973 (see Annex I, Refs. 13 and 33). Since the previous evaluation, additional data have become available and are summarized and discussed in the following monograph. BIOLOGICAL DATA Povidone is the generic name for polyvinylpyrrolidone (PVP). It is the soluble homopolymer of N-vinyl-2-pyrrolidone. As a food additive it appears as the form identified as K-30. To clarify the discussion, the relationship of K-30 to other marketed forms is as follows: Form K-range* Average molecular weight K-15 or 17 12-18 10 000 K-30 26-35 40 000 K-90 80-100 360 000 * Note: based on viscosity. It should be noted that the data described in this evaluation include some studies of povidone having molecular weights other than that of K-30. Another related product is crospovidone - chemically identified as polyvinylpolypyrrolidone or cross-linked, insoluble polyvinylpyrrolidone. It is the insoluble, cross-linked homopolymer of N-vinyl-2-pyrrolidone. Crospovidone is not the subject of the present evaluation. BIOCHEMICAL ASPECTS Absorption Loehry et al. (1970) measured the permeability of the rabbit small intestine to water soluble molecules over a range of molecular weights from 60 to a molecular weight of 80 000. They reported a well correlated inverse log/log linear relationship between absorption and molecular weight. The amount of povidone (average molecular weight 33 000) that was cleared from the lumen by blood was 0.39% of the urea cleared from the lumen by blood. If urea is completely absorbed from the intestine, then povidone of this average molecular weight is 0.39% absorbed. Hanka (1971) detected povidone in the portal venous blood of rabbits following intestinal perfusion with a solution containing povidone (av. mw 40 000). Other studies of the gastrointestinal absorption of povidone have usually been associated with conventional toxicity studies that have been conducted. Scheffner (1955) reported that povidone (av. mw 16 000) was not absorbed from the gastrointestinal tract of guinea- pigs. It was reported that, following the oral administration of isotopically labelled povidone (av. mw 40 000 and 70 000) to rats, less than 0.5% of the activity was absorbed from the gastrointestinal tract (Shelanski, 1953; Burnette, 1962). In a group of rats fed diets containing 1% and 10% povidone (av. mw 38 000) for two years, no evidence of absorption of povidone from the gastrointestinal tract was observed (Shelanski, 1957; Burnette, 1962). Angervall & Berntsson (1961) reported that povidone (av. mw 11 500) was not absorbed from the gastrointestinal tract of man and rat. Burnette (1962) reported that in a group of beagles fed 2.5% and 10% povidone (av. mw 38 000) in the diet for one year, povidone was found in the mesenteric lymph nodes indicating gastrointestinal absorption. Distribution Information on the distribution of povidone within the body comes primarily from studies following its intravenous or intraperitoneal administration. Ravin et al. (1952) administered intravenous infusions of varying average molecular weights to rabbit, rat, dog and man. Cells of the reticuloendothelial (RES) retained povidone; the higher molecular weight molecules were retained the longest. Povidone with an average molecular weight of less than 40 000 left the body within a few days. Fresen & Weese (1952) reported on the presence of povidone (av. mw 38 000) in the RES as did Jeckeln (1952) for povidone (av. mw 40 000). Others have also made similar reports (for example, Frommer, 1955; Heinrich et al., 1966). Povidone storage in the RES is as a result of its incorporation into macrophages by pinocytosis (Pratten & Lloyd, 1979). This incorporation gives rise to the vacuolated appearance which has led to the description of "foam cells". The earlier assumption that the molecules were stored in the mitochondria (Traenckner, 1954) is incorrect (Wessel et al., 1974). Povidone of varying molecular weights was reported not to pass the blood-brain as well as the placental barriers (Ravin et al., 1952). Elimination The elimination of povidone has been studied by a number of investigators, again mostly following intravenous and intraperitoneal administration. The elimination of varying molecular weights has been tabulated from the world literature by Wessel et al. (1974). The T 1/2 for the elimination of povidone in the average molecular weight range of 40 000 has been reported to be as low as 12 hours and as high as 72 hours. The glomerulus can clear povidone of a molecular weight of at least 25 000 and perhaps as high as 40 000 and the peritubular capillaries are permeable to even larger molecules of povidone (Gartner et al., 1968). TOXICOLOGICAL STUDIES Carcinogenicity studies Hueper (1957, 1959, 1961) reported on three studies involving povidone of various molecular weights. In the first study, Hueper (1957) utilized four forms of povidone having average molecular weights of 20 000, 22 000, 50 000 and 300 000. In one series four povidones were implanted in powder form subcutaneously into the nape of the neck in C57 black mice and Bethesda black rats. In a second series the same four povidones were implanted intraperitoneally in the same two species. In still another series, rats were given 2.5 ml of a 7% solution intravenously once a week for eight weeks. All animals from all studies were autopsied either after dying on study or being sacrificed after 24 months. Hueper used the descriptions lymphosarcoma, reticulum cell sarcoma and Kupffer cell sarcoma. For purposes of this discussion all will be considered as RES sarcomas. The results were as follows: Povidone RES Species Route (av. mw) sarcomas Carcinomas Mouse Subcut. 20 000 0/50 0/50 (powder) 22 000 3/50 0/50 50 000 0/50 0/50 300 000 1/50 0/50 i.p. 20 000 0/50 0/50 (powder) 22 000 1/50 0/50 50 000 3/50 0/50 300 000 0/50 0/50 Rat Subcut. 20 000 7/50 0/50 (powder) 22 000 0/50 1/50 50 000 9/50 0/50 300 000 7/50 1/50 i.p. 20 000 7/50 4/50 (powder) 22 000 2/50 0/50 50 000 5/50 0/50 300 000 12/50 0/50 i.v. 20 000 2/50 1/50 22 000 0/50 1/50 50 000 6/50 1/50 300 000 2/50 1/50 The reported incidence of sarcomas among control mice was 0.4%. Among the rats 1/23 of the studied, untreated controls had an RES sarcoma. Other "control" rats had been exposed to various metal dusts or to dextran and did not provide useful data. A similar study was done by Hueper (1959) in which the incidence of RES sarcomas was 11/200 in untreated rats. In this study, additional samples of povidone within the same molecular weight range used previously were studied. The data suggested the development of RES sarcomas related to the parenteral administration of povidone as well as other polymers including dextran. Again the studies were controlled only to a limited extent. There were no manipulation controls for any of the groups. In the third study Hueper (1961) emphasized molecular size as a study criterion. He used povidone "K-17" (molecular weight range 2000-38 000 with the major fraction being between 5000 and 15 000; average mw 10 000) and povidone "K-25" (major fraction of molecular weight between 15 000 and 30 000; average mw 18 000) (these averages for K-17 and K-25 are somewhat lower than what has been reported since then for these forms). He also used for comparison purposes in rats two povidones having an average mw of 50 000. One made by GAF and one made by BASF. The materials were administered intraperitoneally in divided doses over a period from approximately six to 10 weeks. Maximum survival was 24 months for rats and 28 months for rabbits (at which times the experiments were terminated by sacrificing the surviving animals). Results were as follows: Povidone Total RES Species type Administration sarcomas Carcinomas Rat K-17 2 g 3/35 2/35 K-25 2 g 1/35 2/35 50 000 (GAF) 9 g 2/20 0/20 50 000 (BASF) 9 g 0/30 0/30 Control 2/30 3/30 Rabbit K-17 62.2 g 0/6 0/6 K-25 62.2 g 0/6 0/2 Control 0/2 0/2 Hueper concluded that the rabbit may have had less tumours because of the ability to filter larger molecules at the glomerulus than the rat can. Teratogenicity studies Povidone K-25 (av. mw less than 40 000) was tested for prenatal toxicity in rats. The animals received 10% povidone K-25 added to their feed. Substance-containing feed was available ad lib. on days 0-20 post-coitum. All foetuses were examined for externally recognizable skeletal malformation, variations and retardations in the case of two-thirds of the foetuses of a litter; the examination covered organ malformations, variations and retardations. The pregnant animals tolerated administration of substance-containing feed with no clinically recognizable symptoms of poisoning. The only observed effect was slightly loose faeces. With all other parameters examined, no changes, and particularly no damage to the progeny, such as could be attributed to administration of K-25 were found (BASF 1977c). A similar study was conducted on povidone K-90. The animals received 10% K-90 added to their feed. The results were qualitatively and quantitatively similar to those observed with povidone K-25 (BASF 1977d). In a special teratogenicity study, injection of povidone (av. mw 11 500) into the yolk sac of nine-day rabbit embryos (500 mg/embryo) did not increase the number of resorptions or malfunctions compared to the number of resorptions and malformations induced in saline injected embryos (Claussen & Breuer, 1975). Mutagenicity and transformation tests in vitro Povidone K-30 was tested for mutagenic effects on the germ cells of male mice (dominant lethal test) after one intraperitoneal application. The animals received a single injection of 3 160 mg povidone K-30 (dissolved in aquadest.) per kg body weight in a volume of 10 ml/kg. No animals displayed any recognizable symptoms of toxicity over the entire test period. The administration of povidone K-30 had no effect on the conception rate, average number of implantations, percentage of living foetuses or the mutagenicity index (BASF 1977e). Mutagenicity and transformation tests in vitro employing mouse cells (lymphoma L5178Y, TK+/-BUDR and Balb/3T3, respectively) demonstrated that PVP at concentrations of 0.5%, 1.0%, 5.0% and 10.0% in the media did not cause significant mutagenic or transformation effects when compared to non-treated cells (Carchman, 1978). Quantification of RES storage Frommer (1956) quantified storage of povidone "foam cells" following the administration of povidone (av. mw 20 000, 40 000 and 125 000) in rats. He suggested a threshold existed for storage equivalent to the system content of 0.1 g/kg. Acute toxicity Average LD50 Animal Route molecular weight (mg/kg bw) References Rat Oral 10 000-30 000 40 000 Scheffner, 1955; BASF, 1958 Mouse Oral 40 000 Scheffner, 1955; BASF, 1958 i.p. 12 000-15 000 Angervall & Berntsson, 1961 Rat Oral 40 000 100 000 Burnette, 1962; Shelanski et al., 1954 Guinea-pig Oral 40 000 100 000 Burnette, 1962; Shelanski et al., 1954 Oral povidone (av. mw up to 40 000) in high doses caused diarrhoea, the minimal effective dose being 0.5 g/kg bw for cats, and 1-2 g/kg for dogs (Scheffner, 1955). Two dogs were given oral doses of 5 g/kg bw povidone (av mw 220 000 and 1 500 000) for one-and-a-half weeks and two weeks, respectively, without any abnormal findings (Scheffner, 1955). Four pure bred beagles of each sex were given 0, 25 000, 50 000 and 100 000 ppm povidone (K-90) in the feed for 28 days. Another group of eight animals receiving 100 000 ppm cellulose in the feed were also used as control. No toxic effects or pathological changes were noted which could be related to the administered substance, except slightly increased relative spleen weight was observed in the female animals of the 100 000 ppm group (BASF, 1977). Povidone K-90 was administered to Sprague-Dawley rats (10 rats/sex/group) in concentrations of 25 000 and 50 000 ppm in the feed over a 28-day test period. No toxic effects or pathological- histological changes were noted due to administration of K-90 (BASF, 1973). Povidone was also evaluated for acute toxic effect by rapid intravenous administration to beagle dogs (Hazleton Laboratories, 1970). One animal of each sex was given 0, 1, 3 or 10 g of povidone/kg bw. The animals were observed for the subsequent 28 days. No deaths occurred at any dose. Immediately following administration, the animals showed tremors and/or subconvulsive movements, defaecation, salivation, depression and ptosis. There were early sporadic changes in transaminases and haematologic values which generally returned to normal within 48 hours of the dose and remained essentially within normal limits during the remainder of the 28-day observation period. Gross and histopathological examinations of brain, spinal cord, thyroid, adrenal, heart, lung, thymus, spleen, parathyroid, trachea, oesophagus, salivary gland, liver, kidneys, stomach, pancreas, small and large intestine, mesenteric lymph nodes, urinary bladder, prostate and testes in males, uterus and ovaries in females, bone, peripheral nerve, and skeletal muscle were conducted. No histopathological or gross pathological changes were reported. Four groups of animals, each group consisting of two males and two females, were distributed as follows: control, 10% diet of Solka Floc;* 2% povidone K-30 plus 8% Solka Floc; 5% povidone K-30 plus 5% Solka Floc; 10% povidone K-30. The feeding period was two years. There were no reported adverse effects at the end of this treatment. Histopathological examination of thyroid, parathyroid, heart, lung, rib bone and bone marrow, skin, stomach, small bowel, large bowel, liver, gall bladder, spleen, kidneys, lymph nodes, urinary bladder, uterus or prostate, left adrenal, pancreas and testes or ovaries were conducted. Swollen RES cells in the lymph nodes of the high dose group were reported. There was evidence of this in the middle and low dose groups and the 10% Solka Floc control, but "less consistently and to a lesser degree". No other histopathological findings were reported (Burnette, 1962). In two similar feeding experiments using a total of 32 dogs and lasting for one year, no adverse effects could be detected. The intestines, spleens and livers of all animals were shown to be free of povidone, but povidone was demonstrated in the mesenteric lymph nodes of all animals, including the controls (Burnette, 1962). Several other short-term studies in rat, cat and dog showed no toxic effects (Scheffner, 1955; Wolven & Levensten, 1957; Shelanski, 1958). Chronic studies Groups of rats (Wistar strain) were fed diets containing 0, 1 and 10% povidone (mw 38 000) for two years. No toxic effects or gross histological changes were noted which could be attributed to the test compound (BASF, 1958; Burnette, 1962). * Solka Floc = cellulose. In another two-year rat feeding test povidone (K-25) was added to the feed in concentrations of 50 000 or 100 000 ppm. Groups each of 100 rats (Sprague-Dawley) equally divided by sex were used in this study. The feed intake, body weight, clinical parameters tested (urea, GPT, HB, Ery, HT, Leuco, differential blood count, urine status), macroscopic organ findings and the absolute and relative organ weights (heart, liver, kidneys) did not differ from those of the two control groups. No differences were found between average life span of the test and the control animals. In all control and test groups, the appearance of benign and malignant tumours was within the normal limits usually found in rats in long-term investigations in this strain of rats. Histological examination of the tissue of the organs revealed no changes that could be associated with the feeding test. There was no evidence that povidone K-25 or its degradation products were stored in either the mucous membrane of the duodenum or the intestines or the mesenterial lymph nodes (BASF, 1978b). OBSERVATIONS IN MAN Daily subcutaneous injections of polyvinylpyrrolidonevasopressin in a woman with diabetes insipidus for six years led to a papular dermatosis. Polyvinylpyrrolidone was detected in biopsy material (La Chapelle, 1966). To date, the only chronic toxic effect noted in man upon subcutaneous injection has been cutaneous thesaurismosis after parenteral doses of 200-1000 g over 3-12 years (La Chapelle, 1966). Injection of a povidone-containing medication (Depot-Impletol) in a woman resulted in large foreign body granulations in the breast and in the epigastric area (Gille & Brandau, 1975). Comments Only data on the soluble homopolymer of N-vinyl-2-pyrrolidone i.e., povidone were evaluated. No carcinogenicity has been reported for povidone as a consequence of oral administration. Studies involving parenteral administration, primarily intravenous or intraperitoneal indicate that there may be some storage of povidone in the reticuloendothelial system (RES) under certain conditions. The primary predictor of long-term storage relates to the molecular size of povidone in the circulation. That is, if the molecular size is such that filtration at the kidney occurs then the likelihood of storage is less. This leads to a question of povidone's absorption from the gastrointestinal tract. It is difficult to determine the exact level of povidone's absorption from the gastrointestinal tract. This difficulty is due to the fact that the absorption of a compound like povidone that is both hydrophilic and lipophobic is dependent on its molecular size and weight, and the fact that polymer products such as povidone consist of a range of molecular weights. It would appear that any povidone absorbed from the gastrointestinal tract would be of the size that would be cleared by the kidney thus reducing the likelihood of accumulation in the RES. Data from studies of povidone's oral absorption, distribution and elimination are needed to test this hypothesis. These data could be obtained from studies using radiolabelled povidone. Mathematical analyses of data available on molecular sizes absorbed from the intestine and filtered at the glomerulus may also provide the information sought. Since the phenomenon of RES storage may be common to all high molecular weight polymers, povidone should also be evaluated from the viewpoint of comparing it to other polymers used as food additives. The only reported biological effect attributed to oral administration of povidone is stool softening or diarrhoea. In long- term feeding studies in rats no evidence of carcinogenicity was noted as well as no indication of storage in the RES. EVALUATION Establishment of an ADI is deferred pending a review and evaluation of existing or new data relating to pharmacokinetics and RES storage. REFERENCES Altemeir, W. A., Schiff, L., Gall, E. A., Giuseffi, J., Freiman, D., Mindrum, G. & Braunstein, H. Physiological and pathological effects of long-term polyvinylpyrrolidone retention. AMA Arch. Surg., 69, 308-314, 1954 Ammon, R. & Muller, W. The influence of high doses of periston on the rabbit, with special consideration of the spleen (Ger.). Dtsch. med. Wschr., 74, 465-468, 1949 Angervall, L. & Berntsson, S. Oral toxicity of polyvinylpyrrolidone products at low average molecular weight. J. Inst. Brewing, 67, 335-336, 1961 Bennhold, H. & Schubert, R. Uber die plasmaahnlichkeit des periston, Klin. Wschr., 23, 30, 1944 Burnette, L. W. A review of the physiological properties of PVP. Proceedings of the Scientific Section of the Toilet Goods Association, 38, 1-4, 1960 Carchman, R. A. 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Submitted to the World Health Organization by BASF, 1958 Wessel, W., Schoog, M. & Winkler, E. Polyvinylpyrrolidone (PVP): its diagnostic, therapeutic and technical application and consequences thereof. Arzneim. Forsch. Drug Res., 21, 1468-1482, 1974 Traenckner, K. Experimental studies on periston storage in mitochondria of renal tubuli. Z. Ges. Exp. Med., 123, 101-103, 1954 Wolven, A. & Levenstein, I. One-year feeding study in dogs with PVP, final report. Unpublished report from Leberco Laboratories, United States of America. Submitted to the World Health Organization by GAF Corporation, Wayne, New Jersey, 1957 Zeller, H. & Engelhardt, G. Testing of Kollidon 30 for mutagenic effects in male mice after a single intraperitoneal application, dominant lethal test. Unpublished report from the Gewerbehygiene and Toxikologie, Ludwigshafen, Rhein, FRG. Submitted to the World Health Organization by BASF, 1977 Zeller, H. & Peh, J. Report on a study on the effects of Kollidon 25, batch 1229 on the prenatal toxicity with rats. Unpublished report from BASF Gewerbehygiene and Toxikologie, Ludwigshafen, Rhein, FRG. Submitted to the World Health Organization by BASF, 1976a Zeller, H. & Peh, J. Report on a study on the effects of Kollidon 90, batch 5, on the prenatal toxicity with rats. Unpublished report from BASF Gewerbehygiene and Toxikologie, Ludwigshafen, Rhein, FRG. Submitted to the World Health Organization by BASF, 1976b Zeller, H., Sachsse, K., Kirsch, P., Tobst, P., Birnstiel, H., Hempel, K. J. & Merkle, J. Two-year feeding test with Kollidon 25 in rats. Unpublished report from BASF Gewerbehygiene and Toxikologie, Ludwigshafen, Rhein, FRG. Submitted to the World Health Organization by BASF, 1969 Zendzion, R. P. & Teeter, W. R. Tests intravenous administration of PVP in beagle dogs. Unpublished report from Hazleton Laboratories
See Also: Toxicological Abbreviations