Sparing of bone marrow stem cells by long-term administration of Na-alginate to 226Ra contaminated mice.

226Ra toxicity studies form the experimental basis for the estimation of radiation risk from internal emitters in man. We investigated whether treatment with Na-alginate is able to protect haemopoietic bone marrow cells against alpha-irradiation from 226Ra contamination. Doses from 4 to 14 micronCi/kg were injected intraperitoneally in mice 12 days before the start of the treatment. Damage to marrow stem cells was assessed by the exogene clonal spleen technique. Collection of marrow cells by two methods was compared. In the lower dose groups no influence on stem cell survival is noticed. but from 9.0 micronCi/kg a decrease in the number of surviving stem cells is observable in non treated animals. while in animals treated with Na-alginate fewer stem cells are damaged. These preliminary data agree with the hypothesis that Na-alginate stimulates removal of 226Ra mainly from the endosteal bone surfaces, reducing the local 226 Ra dose which accounts for damage to marrow stem cells within the range of alpha-rays at the endosteal surfaces.     

17α-Ethyl-5β-estrane-3α,17β-diol, a biological marker for the abuse of norethandrolone and ethylestrenol in slaughter cattle

The metabolism of the illegal growth promoter ethylestrenol (EES) was evaluated in bovine liver cells and subcellular fractions of bovine liver preparations. Incubations with bovine microsomal preparations revealed that EES is extensively biotransformed into norethandrolone (NE), another illegal growth promoter. Furthermore, incubations of monolayer cultures of hepatocytes with NE indicated that NE itself is rapidly reduced to 17α-ethyl-5β-estrane-3α,17β-diol (EED). In vivo tests confirmed that, after administration of either EES or NE, EED is excreted as a major metabolite. Therefore, it was concluded that, both in urine and faeces samples, EED can be used as a biological marker for the illegal use of EES and/or NE. Moreover, by monitoring EED in urine or faeces samples, the detection period after NE administration is significantly prolonged. These findings were further confirmed by three cases of norethandrolone abuse in a routine screening program for forbidden growth promoters.     

Branchial and renal ion fluxes and transepithelial electrical potential differences in rainbow trout,Oncorhynchus mykiss: effects of aluminium at low pH

Synopsis Adult rainbow trout, Oncorhynchus mykiss, were acutely exposed for 4 hours to low pH (4.4) and elevated Al-concentrations (300 µgI^–1) in soft water (Ca²⁺ + Mg²⁺ = 25 µmolI^–1). Comparison of branchial and renal ion fluxes (Na⁺, Cl^–, Mg²⁺, Ca²⁺ and NH₄ ⁺) gave evidence that pH and Al effects were primarily localized at the gill site. The negative whole body ion balance seemed to be caused by stimulatory effects on Na and Cl efflux especially under Al stress and to a lesser extent by inhibition of influx. Measurements of gill potentials indicated positive shifts, which were similar in response to increasing levels of H⁺ ions and Al. It is suggested that Al-induced changes of branchial potentials causes high diffusable loss of ions through interference with membrane-bound Ca²⁺ at the gill site.     

The effect of humic substances on the toxicity of aluminium to adult rainbow trout, Oncorhynchus mykiss (Walbaum)

Some physiological parameters were measured in adult rainbow trout during a 10-day exposure to 180 μg Al_total l⁻¹ in acid water (pH 4.7) with or without humic substances (10 mg l⁻). The fish were acclimatized to pH 5.0 for 7 days prior to the experimental treatments.
Chemical analyses revealed that, in the presence of human substances, 74–80% of the A1 was organic bound, while in the absence of humic substances most of the Al(987percnt;) occurred in the inorganic form.
Al bound to humic substances (13–150 μg l⁻¹) did not alter the plasma NaCl-concentration, nor the haematocrit value, of rainbow trout during an exposure period of 10 days. This contrasts with the high death rate obtained within 2–3 days when most of the A1 (175 μg l⁻¹) was in the inorganic form. The lethality was accompanied by a 25% decrease in the plasmaconcentration of NaCl and a doubling of the haematocrit value. Bulk analysis revealed that when the metal was present in inorganic forms the total Al content of the gills (75 μg A1 g⁻¹ wet weight) was 15 times higher than when it was present as bound to the humic substances. These experiments showed that the accumulation of A1 at the gills was accompanied by physiological disturbances, both being a function of the chemical speciation of Al.