Toxicological evaluation of some food additives including anticaking agents, antimicrobials, antioxidants, emulsifiers and thickening agents WHO FOOD ADDITIVES SERIES NO. 5 The evaluations contained in this publication were prepared by the Joint FAO/WHO Expert Committee on Food Additives which met in Geneva, 25 June - 4 July 19731 World Health Organization Geneva 1974 1 Seventeenth Report of the Joint FAO/WHO Expert Committee on Food Additives, Wld Hlth Org. techn. Rep. Ser., 1974, No. 539; FAO Nutrition Meetings Report Series, 1974, No. 53. PHOSPHORIC ACID, POLYPHOSPHATES AND THEIR CALCIUM, MAGNESIUM, POTASSIUM AND SODIUM SALTS Explanation These compounds have been evaluated for acceptable daily intake by the Joint FAO/WHO Expert Committee on Food Additives (see Annex 1, Refs Nos. 6, 7, 9, 13, 20 and 23) in 1961, 1963, 1964, 1965, 1969 and 1970. Since the previous evaluation, additional data have become available and are summarized and discussed in the following monograph. The previously published monographs have been revised and are reproduced in their entirety below. BIOLOGICAL DATA BIOCHEMICAL ASPECTS (a) Phosphoric acid and its salts Phosphoric acid is an essential constituent of the human organism, not only in the bones and teeth, but also in many enzyme systems. Phosphorus plays an important role in carbohydrate, fat and protein metabolism. The level of inorganic phosphate in the blood is stabilized by exchange with the mineral depot in the skeleton through the action of parathyroid hormone. This hormone inhibits tubular reabsorption of phosphates by the kidney and brings about demineralization of bone tissue through the action of osteoclasts. The amount of parathyroid hormone that enters the circulation is probably regulated by the calcium level of the blood. Intestinal absorption depends on requirements and is therefore limited. Excretion takes place mainly in the faeces as calcium phosphate so that the continuous use of excessive amounts of sodium phosphate and phosphoric acid may cause a loss of calcium. As a result of physiological regulating mechanisms, man and animals can tolerate large variations in phosphate intake without the balance being upset. Some investigators have considered that the formation in the intestinal tract of insoluble salts of phosphate with calcium iron and other metal ions might result in decreased absorption of such minerals. From studies dealing with this aspect (Lang, 1959; van Esch et al., 1957; Lauersen, 1953; van Genderen, 1961) it is concluded that moderate dose levels of phosphates do not impair absorption as shown by results from carcass analyses or haemoglobin cathartics. Phosphate supplementation of the diet of rodents has been shown to lead to reduction in the incidence of dental caries and different phosphates have different powers in reducing the cariogenic potential of the carbohydrates in a diet. Phosphate supplements seem to exert their cariostatic effect on the tooth surface either directly during eating or by excretion in the saliva (Anon., 1968a; Anon., 1968b). Little specific toxicological information on potassium monophosphates is available. There is no reason to consider that the potassium salts, in the amounts that could be used as food additives, behave differently from the sodium salts and are therefore dealt with together. (b) Disodium and tetrasodium diphosphate In the animal body diphosphate is formed from adenosyl triphosphate (ATP) in many enzymatic reactions. It is either utilized by entering phosphorolytic reactions, or it is hydrolyzed by an inorganic diphosphatase to monophosphate (Long, 1961). Ingested diphosphate is readily converted to monophosphate (Fourman, 1959; Mattenheimer, 1958); no diphosphate was found in faeces or urine of rats treated with diets containing up to 5% tetrasodium diphosphate. In these experiments diphosphate was almost completely absorbed by the gut and excreted as monophosphate in the urine. (c) Pentasodium triphosphate, sodium polyphosphate (Graham's sodium polyphosphate) Several studies indicate that polyphosphates can be hydrolyzed in vivo by enzymes with the formation of monophosphates. The localization of different polyphosphates in the nuclei of animal cells has been demonstrated (Grossmann & Lang, 1962). Injected hexametaphosphate is more slowly degraded than tripolyphosphate (Gosselin et al., 1952), and the highly polymerized Tammann's salt (KNa polyphosphate) is even more slowly eliminated from the blood after i.v. injection than is Graham's salt (Götte, 1953). When administered parenterally a small part of those products may escape in the urine as oligophosphates (Gosselin et al., 1952; Götte, 1953). The higher polyphosphates are probably not adsorbed as such in the intestinal tract. After hydrolysis into smaller units absorption takes place. The larger the molecule, the less the speed of hydrolysis and absorption, as shown by studies using p32 labelled polyphosphate (Ebel, 1958). After giving hexametaphosphate to rats and rabbits by stomach tube, no more than trace amounts of labile phosphate were found in the urine (Gosselin et al., 1952). The oral administration of radioactively-labelled Tammann's salt did not give rise to radioactivity in the blood (Götte, 1953). With Graham's salt and Kurrol's salt, 10 to 30% was absorbed as monophosphate and small amounts of oligophosphates were found in the urine (Lang et al., 1955; Lang, 1958). In experiments in rats with labelled tripolyphosphates and Graham's salt these polymers were not absorbed as such, but were taken up after hydrolysis into monophosphate and diphosphate. In a period of 18 hours only 40% of the dose of Graham's salt was hydrolyzed and absorbed. The bacterial flora of the intestinal tract may contribute to the hydrolysis of the polyphosphates (Schreier & Noller, 1955). In other experiments, radioactively-labelled Kurrol's salt was given orally to rats. About half the radioactivity was recovered from the faeces, mainly as polymeric phosphate, and only a small percentage of the dose was found in the urine, in this case in the form of monophosphate. It is noted that, for practical reasons, in the studies cited high dosages were given to the animals. The efficiency of hydrolysis and absorption may be greater at lower dose levels, such as were used in the short-term and long-term feeding experiments quoted. In some of these (van Esch et al., 1957) the "monophosphate action", as demonstrated by the production of nephrocalcinosis, was not much smaller than when the same dose level was administered by the addition of monophosphate to the food. In another study, this applied only to tripolyphosphate, while Graham's salt had definitely less effect on the kidney (Hahn et al., 1958). The possibility of the intermediate formation of small amounts of trimetaphosphate in the hydrolysis of polyphosphates has been considered (Mattenheimer, 1958). At present, the only known method of production of sodium polyphosphate is by the fusion process. In this process metaphosphates are also formed in amounts up to 8% and their presence is technically unavoidable. It is of interest to note that these metaphosphates (sodium trimetaphosphate and sodium tetrametaphosphate) have been tested in short-term experiments in rats and dogs in conjunction with polyphosphates (Hodge, 1956). The metaphosphates are also hydrolyzed to monophosphates. No specific action of these metaphosphates different from that of the other phosphates has been observed, and it is concluded that the presence of these impurities does not present a hazard. It is also noted that the preparation of sodium polyphosphates used in the toxicological studies mentioned always contained metaphosphates in amounts up to 8%. It has been considered by many authors that the ingestion of polyphosphate in the food may result in a loss of minerals (Ca, Fe, Cu, Mg) which are bound to the polyphosphate and are lost in the faeces with unhydrolyzed polyphosphate. For this reason, in most of the toxicological studies cited, particular attention has been paid to the mineral composition of the carcass and to the possible development of anaemia. The experimental results available indicate that such an action, if it occurs at all, is not significant. Anaemia is not a characteristic feature of treatment with high dose levels of polyphosphate and hexametaphosphate had no effect on iron utilization by rats (Chapman & Campbell, 1957). The use of polyphosphates for the prevention of scale formation in lead pipe water systems may lead to excessive lead levels in drinking-water (Boydens, 1957). (d) Disodium and tetrasodium phosphate In the animal body diphosphate is formed from adenosyl triphosphate (ATP) in many enzymatic reactions. It is either utilized by entering phosphorolytic reactions, or it is hydrolyzed by an inorganic diphosphatase to monophosphate (Long, 1961). Ingested diphosphate is readily converted to monophosphate (Schreier & Nöller, 1955; Mattenheimer, 1958); no diphosphate was found in faeces or urine of rats treated with diets containing up to 5% tetrasodium diphosphate. In these experiments diphosphate was almost completely absorbed by the gut and excreted as monophosphate in the urine. (e) Calcium and magnesium phosphate tribasic Calcium phosphates are insoluble in water and constitute the following series: calcium phosphate (menobasic) which is used as acidulant and mineral supplement; calcium phosphate (dibasic) is used as dietary supplement in doses of 1 g orally; calcium phosphate (tribasic) is used as gastric antacid in doses of 1 g orally; and bone phosphate. Metabolically they behave as sources of calcium and phosphate ions. These compounds need not be considered separately from other monophosphates from the toxicological point of view. Magnesium phosphates are mostly insoluble in water and form the following series: magnesium phosphate (monobasic); magnesium phosphate (dibasic) which is used as laxative: magnesium phosphate (tribasic) is used as antacid in doses of 1 g orally. Metabolically they behave as sources of magnesium and phosphate ions. These compounds need not be considered separately from other monophosphates from the toxicological point of view. TOXICOLOGICAL STUDIES Acute toxicity (a) Phosphoric acid and its salts Minimum lethal Compound Animal Route dose (mg/kg bw) Reference NaH2PO4 guinea-pig oral > 2000 Eichler, 1950 Na2HPO4 rabbit i.v. infusion 985 - 1075 Eichler, 1950 (b) Disodium and tetrasodium diphosphate Minimum lethal dose Animal Route (mg/kg) References Rabbit i.v. approx. 50 Behrens & Seelkopf, 1932 Rat oral LD50 > 4000 Datta et al., 1962 (Na4P2O7) (c) Pentasodium triphosphate, sodium polyphosphate (Graham's sodium polyphosphate) Approx. LD50 LD100 Animal Substance Route (mg/kg bw) (mg/kg bw) References Mouse hexametaphosphate Behrens & (neutralized Na oral 100 Seelkopf, 1932 salt) approx. " Rabbit " i.v. 140 Rat 1/3 Kurrol's salt van Esch et and 2/3 oral 4000 al. 1957 tetra- and disodium diphosphates (water i.v. 18 " soluble, neutral) (d) Disodium and tetrasodium phosphate Minimum lethal dose Animal Route (mg/kg) References Rabbit i.v. About 50 Behrens & Seelkopf, 1932 Rat oral LD50 (Na4P2O7): > 4000 Datta et al., 1962 Short-term studies (a) Phosphoric acid and its salts Rat There are many reports of short-term studies to determine the effects of the addition of monophosphates to the diet of rats (House & Hogan, 1955; Maynard et al., 1957; Selye & Bois, 1956; MacKay & Oliver, 1935; Behrens & Seelkopf, 1932; McFarlane, 1941; van Esch et al., 1957; Sanderson, 1959). Pathological effects in the parathyroids, kidneys and bones have been observed in mature male rats fed a diet containing an excessively high level (8%) of sodium orthophosphate for seven months or until the animal succumbed (Saxton & Ellis, 1941). Histological and histochemical changes in the kidneys have been found in rats fed for 24 to 72 hours on a diet containing an excess of inorganic phosphate (10% disodium acid phosphate) (Craig, 1957). Three groups of 12 rats each were fed diets containing added dibasic potassium phosphate so that the calcium and phosphorus concentrations in the experimental diets were as follows: Diet Calcium % Phosphorus % Control 0.56 0.42 "normal orthophosphate" 0.47 0.43 "high orthophosphate" 0.50 1.30 The experiment was conducted in three stages, with experimental observations made when animals had consumed the test diets for 50, 60 and 150 days. No adverse physiological effects were observed clinically at autopsy or on histological examination. All the data obtained from this study indicated that there was probably adequate absorption and utilization of calcium, phosphorus and iron with both high and normal levels of monophosphate (Dymsza et al., 1959). Reports of short-term studies do not provide for a differentiation between the action of the mono-, di- and trisodium or potassium salts; several authors have used "neutral mixtures" e.g. of mono- and disodium monophosphates. There is no reason to expect a specific action on the part of one of these three monophosphates, the relevant factor being the phosphate content and the acidity of the food mixture as a whole. On high-dose levels, hypertrophy of the parathyroid glands has been observed. A more important and more sensitive criterion for the deleterious action of phosphate overdosage is the appearance of metastatic calcification in soft tissues, especially in the kidney, stomach and aorta. Kidney calcification may be observed in a few weeks or months, depending on the dose level. The pathology of calcification and necrosis of the tubular epithelium in the kidneys (nephrocalcinosis) has been studied in detail (MacKay & Oliver, 1935; McFarlane, 1941; Sanderson, 1959; Fourman, 1959). It is difficult to indicate a border line between those levels that do not produce nephrocalcinosis and those that produce early signs of such changes, because: (1) even on diets to which no phosphate has been added, rats, in apparently healthy condition, may have a few isolated areas of renal calcification; (2) the composition of the diet (amount of calcium, acid-base balance, vitamin D) has an important influence on the appearance of renal calcification. There are numerous reports of experimental phosphate-containing diets that do not produce kidney damage by excessive calcification, e.g. the Sherman diet (0.47 to 0.51%P) (Lang, 1959; Hahn & Seifen, 1959; van Esch et al., 1957), the diet used by MacKay & Oliver (1935) (0.62% P) and the commercial "Purina A" diet (0.90% P) (Lang, 1959). Early calcification has been observed in rats on a Sherman diet to which 1% of a 2:3 mixture of NaH2PO4 and Na2PHO4 was added, bringing the P-content to 0.71% (van Esch et al., 1957). Similar effects were observed with the addition of a phosphate mixture resulting in a P-content of 0.89% (Hahn & Seifen, 1959), and with levels of phosphate in the diet corresponding to a P-content varying from 1.25% to 2.85% (Lang, 1959; MacKay & Oliver, 1935; Eichler, 1950; McFarlane, 1941; van Esch et al., 1957; Haldi et al., 1939). In recent experiments (Dymsza et al., 1959), however, a diet to which K2HPO4 had been added and containing 1.3% P and 0.5% Ca did not produce nephrocalcinosis in a group of 12 mice within a period of 150 days, although the weight of the kidneys was increased. Also food and protein efficiency was diminished as compared with animals on the control diet. These effects may have resulted from the large amount of salts added to the diet in these experiments. Guinea-pig Diets containing 0.9% P and 0.8% Ca or higher levels of phosphate produced calcification in the soft tissues (House & Hogan, 1955; Hogan et al., 1950). (b) Disodium and tetrasodium diphosphate Rat In a series of successive experiments (Hahn & Seifen, 1959; Hahn et al., 1958), Na4P2O7 was added in concentrations of 1.8%, 3% and 5% to a modified Sherman diet and fed to groups of 34-36 young rats for six months. The studies also included control groups and groups receiving the same levels of sodium monophosphate. With 3% and 5% diphosphate diets growth was significantly decreased and at both these concentrations nephrocalcinosis appeared as the main toxic effect. The degree of damage to the kidneys was about the same as that observed in the corresponding monophosphate groups. With the 1.8% diphosphate and monophosphate diets, normal growth occurred but a slight yet statistically significant increase in kidney weight was noted. Microscopic examination revealed kidney calcification in some of the animals, both in the diphosphate and monophosphate groups. This was more extensive than the calcification occasionally found in the control animals. In an additional experiment, 1.1% of diphosphate and of monophosphate were used (Hahn, 1961). There was a slight growth retardation in the first part of the experiment. After 39 weeks a slight degree of kidney calcification was noted and this was the same for both phosphates (Hahn, 1961). In a recent series of experiments (Datta et al., 1962), Sherman diets containing 1%, 2.5% and 5% Na4P2O7 were fed for 16 weeks to groups of 20 male and female rats weighing between 90 and 115 g; a similar group received a diet containing 5% monophosphate. In the sodium phosphate groups, growth was normal up to the 2.5% level; kidney weight was increased at the 2.5% level (females) and above; kidney function was (concentration test) decreased at the 2.5% level (males) and above. Kidney damage (calcification, degeneration and necrosis) was observed in a greater percentage of rats in the 1% group than in the controls. At the higher concentration of sodium diphosphate more severe kidney damage occurred and, in addition, some of the animals had hypertrophy and haemorrhages of the stomach. The latter abnormality was not found in rats in the 5% monophosphate group. (c) Pentasodium triphosphate, sodium polyphosphate (Graham's sodium polyphosphate) Rat Groups of five male rats were fed for a period of one month on diets containing 0.2%, 2% and 10% sodium hexametaphosphate or 0.2%, 2% and 10% sodium tripolyphosphate. Control groups were given the standard diet, or diets with the addition of 10% sodium chloride or 5% disodium phosphate (Hodge, 1956). With 10% of either of the polyphosphate preparations and also with 10% sodium chloride in the diet, growth retardation occurred, but none of the rats died. Increased kidney weights and tubular necrosis were, however, observed. With 2% of polyphosphate in the diet, growth was normal, but in the kidneys inflammatory changes were found which were different from the tubular necrosis observed in the 10% groups. With 0.2% of polyphosphate in the diet, normal kidneys were seen. In another series of experiments (Hahn & Seifen, 1959; Hahn et al., 1958; Hahn et al., 1956), 3% and 5% of sodium tripolyphosphate (pH 9.5 in 1% solution) and 1.8%, 3% and 5% of Graham's salt (pH 5) were added to a modified Sherman diet, which was then fed during 24 weeks to groups of 36 male and 36 female rats. Growth retardation was exhibited by the rats in the 5% polyphosphate groups. With 3% of either preparation, a temporary growth inhibition was observed, and with 1.8% of Graham's salt (male animals) growth was normal. Nephrocalcinosis was observed in the 3% and 5% groups. It was noted that the degree of damage with Graham's salt was less than that in control groups treated with the same concentrations of orthophosphate; with tripolyphosphate, however, kidney damage was practically identical with that exhibited by the animals in the orthophosphate group. In the animals on a diet containing 1.8% Graham's salt, calcification in the kidneys was slight or absent and the kidney weights were normal (Hahn & Seifen, 1959). In a further group of experiments (van Esch et al., 1957; van Genderen, 1958), Kurrol's salt was used in a commercial preparation consisting of 1/3 Kurrol's salt and 2/3 of a mixture of disodium and tetrasodium diphosphate (Na2H2P2O7 and Na4P2O7). Kurrol's salt is practically insoluble in water, but the mixture with diphosphate can be dissolved and a 1% solution had a pH of 7.6. Groups of 10 male and 10 female rats were fed for a period of 12 weeks on a Sherman diet to which 0.5%, 1%, 2.5% and 5% of the preparation had been added. Normal growth was observed in the groups treated with the 0.5%, 1% and 2.5% concentrations of the polyphosphate mixture, but in those receiving the 5% concentrations growth retardation was exhibited. Kidney weights were normal in the 0.5% group, slightly increased (males significantly) in the 1% group and further increased in the 2.5% and 5% groups. The histopathological examination revealed that in the kidneys of the animals of the 5% group definite nephrocalcinosis had occurred, with extensive damage to the tubular tissue. Calcification was also observed in other tissues. In the 2.5% group a less extensive nephrocalcinosis was exhibited, and in the 5% group isolated areas of calcification with lymphocyte infiltrations were found. In the 0.5% group kidney structure was normal. The results obtained with this polyphosphate preparation were practically identical, qualitatively and quantitatively, with the results of a similar experiment made with a neutral mixture of NaH2PO4 and Na2HPO4 carried out at a later date in the same laboratory (Hahn et al., 1958; Götte, 1953). In other experiments, groups of 12 male rats were treated with diets to which 0.9% and 3.5% sodium hexametaphosphate had been added (corresponding to 0.46% and 1.20% P). Other groups received the control diet alone (0.4% P and 0.5% Ca), or with addition of potassium monophosphate. To the experimental diets different amounts of salts were added to replace cornstarch in order to equalize the levels of major minerals; this resulted in a rather high salt concentration. The duration of treatment was up to 150 days. With 3.5% added hexametaphosphate growth and food and protein efficiency were poorest. The kidneys of the animals fed the high level of hexametaphosphate were significantly heavier than those of the control rats. This was perhaps a manifestation of the high salt load on the kidneys. No histopathological abnormalities were observed in kidney sections from animals taken from any of the groups (Dymsza et al., 1959). Dog Sodium tripolyphosphate (Na5P3O10) and sodium hexametaphosphate were fed to one dog each in a dose of 0.1 g/kg per day for one month; two other dogs received daily doses which increased from 1.0 g/kg at the beginning to 4.0 g/kg at the end of a five-month period. The dog treated with the starting dose of 10 g/kg/day of hexametaphosphate began to lose weight when the daily dose reached 2.5 g/kg, while the one receiving gradually increasing doses of tripolyphosphate lost weight only when its diet contained 2.0 g/kg/ day. In other respects (urinalysis, haematology, organ weights) the animals were normal, with the exception of an enlarged heart, due to hypertrophy of the left ventricle, in the dog receiving gradually increasing doses of sodium tripolyphosphate. In addition, tubular damage to the kidneys was observed in both dogs on the higher dose regime. In the tissues of the dogs fed 0.1 g/kg/day no changes were found that could he attributed to the treatment (Hodge, 1956). (d) Disodium and tetrasodium phosphate Rat In a series of successive experiments (Hahn et al., 1958; Hahn & Seifen, 1959) tetrasodium diphosphate (Na4P2O7) was added in concentrations of 1.8%, 3% and 5% to a modified Sherman diet and fed to groups of 34 to 36 young rats for six months. The studies also included control groups and groups receiving the same levels of sodium monophosphate. With 3% and 5% diphosphate diets growth was significantly decreased and at both these concentrations nephrocalcinosis appeared as the main toxic effect. The degree of damage to the kidneys was about the same as that observed in the corresponding monophosphate groups. With the 1.8% diphosphate and monophosphate diets, normal growth occurred, but a slight yet statistically significant increase in kidney weight was noted. Microscopic examination revealed kidney calcification in some of the animals, both in the diphosphate and monophosphate groups. This was more extensive than the calcification occasionally found in the control animals. In an additional experiment, 1.1% of diphosphate and of monophosphate were used. There was a slight growth retardation in the first part of the experiment. After 39 weeks, a slight degree of kidney calcification was noted and this was the same for both phosphates (Hahn et al., 1958). In a series of experiments Sherman diets containing 1%, 2.5% and 5% tetrasodium diphosphate (Na4P2O7) were fed for 16 weeks to groups of 20 male and 20 female rats weighing between 90 and 115 g; a similar group received a diet containing 5% monophosphate. In the sodium diphosphate groups, growth was normal up to the 2.5% level; kidney weight was increased at the 2.5% level (females) and above; kidney function, as determined by a concentration test, decreased at the 2.5% level (males) and above. Kidney damage (calcification, degeneration and necrosis) was observed in a greater percentage of rats in the 1% group than in the controls. At the higher concentrations of sodium diphosphate more severe kidney damage occurred and, in addition, some of the animals had hypertrophy and haemorrhages of the stomach. The latter abnormality was not found in rats in the 5% monophosphate group (Datta et al., 1962). Long-term studies (a) Phosphoric acid and its salts Rat Three successive generations o£ rats were fed diets containing 0.4% and 0.75% of phosphoric acid for 90 weeks. No harmful effects on growth or reproduction could be observed. No significant differences were noted in the blood picture in comparison with control rats and there was no other pathological finding which was attributable to the diets. There was no acidosis, nor any change in the calcium metabolism. The dental attrition was somewhat more marked than that in the control rats (Lang, 1959). No other long-term studies on monophosphates have been found in the literature. (b) Disodium and tetrasodium diphosphate Rat No specific studies with diphosphates have been made, but in one series of experiments a mixed preparation was used which consisted of 2/3 Na2H2P2O7 and 1/3 Kurrol's salt (KPO3)n. H2O with n = 400 to 5000. Concentrations of 0.5%, 1% and 5% were added to a Sherman diet and given to groups of 10 male and 10 female rats. From these animals a second and third generation were produced, during which the treatment with phosphates was continued. Growth and fertility and average life span were normal and the life span was not significantly reduced up to the 2.5% level. Nephrocalcinosis occurred at the 1% level and above. At 0.5% no abnormalities were observed that were not also present in control animals. At none of the concentrations did tumours appear with higher frequency than in the controls (van Esch et al., 1957). (c) Pentasodium triphosphate, sodium polyphosphate (Graham's sodium polyphosphate) Rat To a Sherman diet containing 0.47% P a mixture of 1/3 Kurrol's salt and 2/3 diphosphate was added in concentrations of 0.5%, 1%, 2.5% and 5% and fed to groups of 30 male and 10 female rats from weaning to end of their life span (van Esch et al., 1957). Two successive generations of offspring were produced on these diets. Significant growth inhibition was observed in the 5% groups of both first and second generations. In other groups growth was normal. Fertility was normal in the 0.5%, 1% and 2.5% groups, but much decreased in the 5% group. Haematology of the 0.5%, 1% and 2.5% groups showed a decreased number of erythrocytes in the 2.5% group, second generation only. In the 0.5% group no kidney damage attributable to the polyphosphate treatment was observed, but in the groups having higher intakes renal calcification occurred in a degree increasing with the dose level. In another series of feeding tests (Hodge, 1960a), diets containing 0.05%, 0.5% and 5% sodium tripolyphosphate were given for two years to groups of 50 male and 50 female weanling rats. Only when 5% of polyphosphate was added to the diet was growth reduced; the reduction was significant in males but slight and delayed in females. A smaller number of rats survived in the 5% groups than in the other groups. A low grade of anaemia was sometimes observed in the 5% groups only. Increased kidney weights were noted in the 5% group; pathological changes which could be ascribed to treatment were not observed in the 0.5% and 0.05% groups. In the control group and the 0.5% tripolyphosphate group, reproduction studies were carried out over three generations involving the production of two litters in each generation. Reproduction was normal and no changes in the offspring were observed. A long-term study (Hodge, 1960b) of the same design was made with sodium hexametaphosphate also at concentrations of 0.05%, 0.5% and 5% in the diet. Growth retardation occurred only in the 5% groups. Mortality was high in all groups but had no relation to the amount of hexametaphosphate in the diet. Periodic blood examination gave normal haematological values. Kidney weights were increased in the 5% group and calcification was present. Rats given the 0.5% diet did not have significant changes in the kidneys. Reproduction studies for three generations in the 0.5% group revealed normal performance in every respect. (d) Disodium and tetrasodium phosphate No specific long-term studies with diphosphates have been made, but in one series of long-term experiments a mixed preparation was used which consisted of 2/3 disodium and tetrasodium diphosphate (Na2H2P2O7 and Na4P2O7) and 1/3 Kurrol's salt.* Concentrations of 0.5%, 1%, 2.5% and 5% were added to a Sherman diet and given to groups of 10 male and 10 female rats. From these animals a second and third generation were produced, during which the treatment with phosphates was continued. Growth and fertility and average life span were normal and the life span was not significantly reduced up to the 2.5% level. Nephrocalcinosis occurred at the 1% level and above. At 0.5% no abnormalities were observed that were not also present in control animals. At none of the concentrations did tumours appear with a higher frequency than in the controls (van Esch et al., 1957). OBSERVATIONS IN MAN Studies on 15 students, who drank 2000 to 4000 mg of phosphoric acid in fruit juices every day for 10 days, and on two males who received 3900 mg of phosphoric acid every day for 14 days, revealed no observable change in urine composition indicative of a disturbed metabolism (Lauersen, 1953). The long-continued daily intake of 5 to 7000 mg of NaH2PO4 (corresponding to 1000 to 1500 mg of P) did not produce adverse effects (Lang, 1959). Similarly a daily intake of 6000 mg of NaH2PO4 Ê 2H2O was tolerated without difficulty (Lauersen, 1953). Comments: Ingested phosphates from natural sources should be considered together with that from food additives sources. The usual calculation for provision of a margin of safety is probably not suitable for food additives that are also nutrients. The dose levels producing nephrocalcinosis were not consistent, among the various rat feeding studies. However, the rat is exquisitely susceptible to calcification and hydronephrosis upon exposure to acids forming calcium chelates or complexes. The lowest dose levels that produce nephrocalcinosis overlap the higher dose levels failing to do so. The lowest level that produced nephrocalcinosis in the rat (1% P in the diet) is used as the basis for the evaluation and, by extrapolation based on the daily food intake of 2800 calories, this gives a dose level of 6600 mg P per day as the best estimate of the lowest level that might conceivably cause nephrocalcinosis in man. Nutritional demands to balance Ca:P ratio do not apply to calcium phosphate itself. * Kurrol's salt is a polymer of high molecular weight obtained by fusion of monopotassium monophosphate. The formula is (KPO3)n.H2O, where n = 400 to 5000. EVALUATION Estimate of acceptable total dietary phosphorus load for man 0-70* mg/kg bw. REFERENCES Anon (1968a) Lancet, 1, 1187 Anon (1968b) Brit. med. J., 1, 268 Behrens, B. & Seelkopf, K. (1932) Arch. exp. Path., 169, 238 Bonting, S. L. & Jansen, B. C. (1956) Voeding, 17, 137 Boydens, M. R. (1957) Bull. Acad. Roy. Med. Bulg., 22, 293 Chapman, D. G. & Campbell, J. A. (1957) Brit. J. Nutr., 11, 127 Craig, J. M. (1957) Amer. J. Path., 33, 621 Datta, P. K., Frazer, A. C., Sharratt, M. & Sammons, H. G. (1962) J. Sci. Food Agric., 13, 556 Dymsza, H. A., Reussner, G. jr & Thiessen, R. jr (1959) J. Nutr., 69, 419 Ebel, J. P. (1958) Ann. Nutr. Alim., 12, 57 Eichler, O. (1950) Handbuch der experimentellen Pharmakologie, Bd 10, Berlin, 363 van Esch, G. J., Vink, H. H., Vit, S. J. & van Genderen, H. (1957) Arzneimittel Forsch., 7, 172 Fourman, J. (1959) Brit. J. exp. Path., 40, 464 van Genderen, H. (1958) In: Kondensierte Phosphate in Lebensmitteln, Berlin, Springer * This figure applies to the sum of added phosphate and food phosphate. Acceptable daily intake levels of phosphate depend on the amount of calcium in the diet. The levels stated above apply to diets that are nutritionally adequate with respect to calcium. However, if the calcium intake were high, proportionally higher amounts of phosphate would be acceptable, and the reverse relation would also apply. van Genderen, H. (1961) Z. Ernahrungsw., Suppl. 1, 32 Gosselin, R. E., Rothstein, A., Miller, G. J. & Berke, H. L. (1952) J. Pharmacol. Exp. Ther., 106, 180 Götte, H. (1953) Z. Naturforsch., 86, 173 Grossman, D. & Lang, K. (1962) Biochem. Z., 336, 351 Hahn, F. (1961) Z. Ernahrungsw., Suppl. 1, 55 Hahn, F., Jacobi, H. & Rummel, W. (1956) Naturwissenschaften, 43, 539 Hahn, F., Jacobi, H. & Seifen, E. (1958) Arzneimittel-Forsch., 8, 286 Hahn, F. & Seifen, E. (1959) Arzneimittel-Forsch., 9, 501 Haldi, J., Backmann, G., Wynn, W. & Ensor, C. (1939) J. Nutr., 18, 399 Hodge, H. C. (1956) Short-term oral toxicity tests of condensed phosphates in rats and dogs, Unpublished report Hedge, H. C. (1960a) Chronic oral toxicity studies in rats of sodium tripolyphosphate, Unpublished report Hodge, H. C. (1960b) Chronic oral toxicity studies in rats of sodium hexametaphosphate, Unpublished report Hogan, A. G., Regan, W. O. & House, W. B. (1950) J. Nutr., 41, 203 House, W. B. & Hogan, A. G. (1955) J. Nutr., 55, 507 Lang, K. et al. (1955) Biochem. Z., 327, 118 Lang, K. (1958) In: Kondensierte Phosphate in Lebensmitteln, Berlin, Springer Lang, K. (1959) Z. Lebensmitt-Untersuch., 110, 450 Lauersen, F. (1953) Z. Lebensmitt-Untersuch., 96, 418 Long, C., ed. (1961) Biochemist's Handbook, London, E & F. N. Spon Ltd., 251 MacKay, E. M. & Oliver, J. (1935) J. exp. Med., 61, 319 Mattenheimer, H. (1958) In: Kondensierte Phosphate in Lebensmitteln, Berlin, Springer Maynard, L. A., Boggs, D., Fisk, G. & Seguin, D. (1958) J. Nutr., 64, 85 McFarlane, D. (1941) J. Path. Bact., 52, 17 Sanderson, P. H. (1959) Clin. Sci., 18, 67 Saxton, J. A. jr & Ellis, G. M. (1941) Amer. J. Path., 17, 590 Schreier, K. & Nöller, H. G. (1955) Naunyn-Schmiedeberg's Arch. exp. Path. Pharmak., 227, 199 Selye, H. & Bois, P. (1956) Amer. J. Physiol., 187, 41
See Also: Toxicological Abbreviations