Water and formula fluoride concentrations: significance for infants fed formula

The independent contributions of formula and water to the total fluoride (F) intake from the diet of formula-fed infants is not fully documented. Although the precise timing and mechanism by which dental fluorosis occurs has not been fully defined, water F levels can be an important consideration in the risk of dental fluorosis for formula-fed infants. An assessment of 1,308 participants younger than 2 years old revealed that: 81% of homes received public water; 19% received well water; 26% of participants used bottled water; and 11% used some kind of filtration system. In this study, virtually all formulas consumed by the birth cohort and water sources used in the reconstitution of these formulas were assayed for F using a F ion specific electrode and direct read method, except for soy-based formulas, which were analyzed by microdiffusion (modified Taves). Among 78 commercially available bottled waters in Iowa, F levels ranged from 0.02 to 1.36 ppm (mean 0.18 ppm), 83% from 0.02 to 0.16 ppm, 7% from 0.34 to 0.56 ppm, 1% had a F level of 0.88, and 9% had F levels > 1.0 ppm. Among 47 casein (milk)-based formulas, 16 ready-to-feed (RTF) formulas had levels of 0.04-0.55 ppm F (mean 0.17 ppm), 14 liquid concentrates (LC) reconstituted with distilled water had levels of 0.04-0.19 ppm F (mean 0.12 ppm), and 17 powdered concentrates (PC) reconstituted with distilled water had levels of 0.05-0.28 ppm F (mean 0.14 ppm). The 17 soy-based formulas had a range of 0.04-0.47 ppm F (mean 0.26 ppm).(ABSTRACT TRUNCATED AT 250 WORDS)

Reversibility of the effects of dietary fish oil on the fatty acid composition of the brain and retina of growing chicks

Dietary fish oil increases levels of (n-3) fatty acids in the brain and retina of younger animals but has less effect in adults. The duration of the effects of fish oil in young animals, as well as the extent of reversibility of the effects, are unknown. Laying hens were fed either a fish oil diet or a soybean oil-based control diet. Resulting chicks were assigned to three diet groups: chicks from fish oil and soybean oil hens were continued on fish oil and soybean oil diets, respectively, for 0, 3, 6, or 9 weeks, and additional chicks from the fish oil hens were fed the fish oil diet for 0, 3, or 6 weeks and then reversed to the soybean oil diet for a period of 3 weeks. The fatty acid composition of the brain, retina, liver, and serum of the reversal chicks was compared with chicks fed the fish oil diet only or the soybean oil diet only. Brain levels of docosahexaenoic acid (22:6(n-3)) decreased substantially when reversal from the fish oil diet to the control diet was begun at hatching, but did not decrease when reversal was begun at later times. Other (n-3) fatty acids in the brain, docosapentaenoic acid (22:5(n-3)) and eicosapentaenoic acid (20:5(n-3)), decreased substantially at all ages, and to a greater extent than 22:6(n-3). Brain arachidonic acid (20:4(n-6)), which was low in fish oil chicks, rose to control after reversal at hatching, but recovered only partially when reversal was begun at later times. A similar patterns was observed in the retina. Serum and liver (n-3) fatty acids fell to control in all reversal chicks, and (n-6) fatty acids increased to control, except in chicks reversed at 6 weeks. This study demonstrates that by 3 weeks of age the chick brain strongly resists diet-induced lowering of high levels of 22:6(n-3).

Modulation of diethylnitrosamine-induced hepatocarcinogenesis and O6-ethylguanine formation in rainbow trout by indole-3-carbinol, beta-naphthoflavone, and Aroclor 1254

Rainbow trout were fed a diet containing indole-3-carbinol (2000 ppm), beta-naphthoflavone (500 ppm), or Aroclor 1254 (100 ppm) for 6 weeks before a single 24-hr exposure to an aqueous solution of 250 ppm diethylnitrosamine (DEN). The fish were killed 42 weeks later to determine the carcinogenic response. DEN exposure produced an 80.2% incidence of liver tumors and an average of 3.47 tumors per tumor-bearing fish, whereas no tumors were detected in the sham-treated control fish. Tumor induction was inhibited by indole-3-carbinol (27.5% incidence, 1.89 tumors per tumor-bearing fish) but enhanced by beta-naphthoflavone (91.8% incidence, 3.60 tumors per tumor-bearing fish). Aroclor 1254 had no effect on DEN-induced hepatocarcinogenesis (80.0% incidence, 3.03 tumors per tumor-bearing fish). The effects of these modulators on O6-ethylguanine and 7-ethylguanine formation (measured by HPLC and fluorescence spectrophotometry) were examined. Liver DNA ethylguanine levels were reduced in indole-3-carbinol-pretreated fish and increased in beta-naphthoflavone-pretreated fish compared to untreated controls after DEN exposure. Aroclor 1254 pretreatment had no significant effect on DNA ethylguanine formation. Similar O6-ethylguanine to 7-ethylguanine ratios were found among the control and treated groups. The results of this study indicate that modulation of DEN hepatocarcinogenesis by indole-3-carbinol and beta-naphthoflavone may be mediated by their effects on O6-ethylguanine formation and, therefore, on the initiation phase of carcinogenesis.

Formation and persistence of ethylguanines in liver DNA of rainbow trout (Salmo gairdneri) treated with diethylnitrosamine by water exposure

Diethylnitrosamine exposure via the water resulted in the formation of 7-ethylguanine and O6-ethylguanine in rainbow trout liver DNA. The modified bases were quantitated by high-pressure liquid chromatography and fluorescence spectrophotometry. In vivo 7-ethylguanine and O6-ethylguanine levels were directly proportional to DEN concentrations between 62.5 and 250 ppm. 7-Ethylguanine and O6-ethylguanine levels were approximately directly proportional to duration of exposure to DEN between 0 and 6 hr under the conditions used, with less than proportionate increases thereafter. Removal of ethylguanines from liver DNA following a 24-hr exposure to 250 ppm DEN (a known carcinogenic regimen) was biphasic; 24% of the O6-ethylguanine and 32% of the 7-ethylguanine found immediately after exposure were removed in 12 hr but no significant decline was found over the period from 12 to 96 hr after exposure. Alkyl acceptor protein activity in trout liver was examined to assess the role of enzymatic repair in the observed loss of O6-ethylguanine in vivo. Although an O6-alkylguanine repair system similar to the alkyltransferase system reported in rodents was found in trout liver, only 4% of the O6-ethylguanine lost from DNA after exposure to 250 ppm DEN can be accounted for by activity of the alkyl acceptor protein. The high incidence of liver tumours observed in DEN-treated rainbow trout may be related to the rapid formation and substantial persistence of the promutagenic O6-ethylguanine in liver DNA.