Comparison between responses to gametophytic and sporophytic recurrent selection in maize (Zea mays L.)

Summary Experiments were conducted to determine the chromosomal location of the gene conditioning overproduction of a methionine-rich, 10-K zein in maize kernels of line BSSS53. In addition, the chromosomal location of the structural gene encoding the overproduced protein was determined. Whereas the structural gene, designated Zps10/(22), was found to be located on the long arm of chromosome 9 near the centromere, the locus regulating overproduction of the zein protein was mapped to the short arm of chromosome 4. This regulatory gene has been designated Zpr10/(22). Regulation of 10-K zein production by Zpr10/(22) is, therefore, via a trans-acting mechanism.     

Sedimentation and distribution of gamma-emitting radionuclides in bottom sediments of southern Lake Päijänne,Finland, after the Chernobyl accident

The rates of sedimentation of fallout nuclides were determined by means of sediment traps during 28 months after the Chernobyl accident in southern Lake Päijänne, Finland. The spatial distribution of the radionuclide content of the lake bottom was studied on 35 sediment cores in winters 1987/88 and 1988/89. The results were compared with simultaneous observations of the radionuclide content of the water and seston. The role of different transfer mechanisms in the elimination of radionuclides from the water column is discussed.The values recorded for the flux to the lake sediments were on average of the same order of magnitude as the initial deposition on the lake surface (Cs-137 65 kBqm^–2). The radionuclide flux to the sediments was rapid during the first months after the accident. After that the elimination of dissolved nuclides from the water mass became significantly slower. The highest flux rate was that of Ce-144 and the lowest that of Rh-106 (Ru-106). Of the radiocesium, about half of the initial inventory was transferred to the sediments after the first observation year.The content of radionuclides showed considerable spatial variation on the lake bottom (Cs-137 7–280 kBqm^–2). Direct adsorption of radiocesium explains unexpectedly high concentrations on shallow erosion bottoms. There was a clear tendency for the concentrations to increase with depth, as a result of the focusing effect. Sediment resuspension had a significant impact on the total flux of radionuclides to deepwater sediments. Estimates were made of the resuspended flux of radionuclides.     

Biochemical identification of B-F and B-G allelic variants of the chicken major histocompatibility complex

Biochemical methods were used to analyse B-F and B-G antigens of the chicken major histocompatibility complex (MHC). In a panel of 12 inbred or partially inbred chicken lines the MHC haplotypes, originally defined by serological and histogenetical methods, were compared. Using monoclonal 18-6G2, allele-specific B-G patterns were obtained by immunoblotting. Comparison of B-G12 and B-G2 revealed a shared banding pattern, but additional products were detected for B-G12. The B-F products of B2 and B12 had identical IEF patterns. The identical B-F products and partially shared B-G products might explain the serological cross-reaction between these haplotypes. In addition, the IEF pattern of B-F21 appeared similar to B-F2 and B-F12, but the partial proteolysis map showed a clear difference. Although two B-F bands could be detected per haplotype, no evidence for the expression of more than one B-F locus was found. The biochemical methods enabled a precise definition of expressed MHC products and can be a useful tool for the identification of B-alleles in other chicken lines or outbred chickens for their MHC antigens.