Analysis of a large nontranscribed spacer in the ribosomal DNA of the house cricket,Acheta domesticus (Orthoptera:Gryllidae)

An analysis of a 29-kilobase nontranscribed spacer fragment in the ribosomal DNA (rDNA) of the house cricket, Acheta domesticus, revealed a highly repetitious structure. A total of eight EcoRI repeats of three different size classes measuring 259, 420, and 508 base pairs (bp) was mapped to a region 2 kilobases (kb) from the 18 S coding region. The repeats were oriented in a nonrandom manner and had sequences homologous to DNA located immediately adjacent to the repetitive array. DNA sequence analysis showed that the repetitive region was composed of smaller direct repeats 66, 67, and 383 bp in length. There was minor length heterogeneity of the chromosomal restriction fragments containing the entire array, indicating that a variable number of EcoRI repeats is a minor contributor to the total repeat-unit length heterogeneity. Immediately upstream from the EcoRI array there is a 17-kb region composed of 50 to 60 subrepeat elements recognized by a variety of restriction endonucleases. A subcloned SmaI repeat from the array was not homologous to any other part of the rDNA repeat unit or other chromosomal DNA. There was little length heterogeneity in restriction fragments containing the chromosomal 17-kb repetitions region. Immediately upstream from the 17-Kb region there is a 4.1-kb segment with sequences homologous to the EcoRI repeats.     

Seasonal histochemical changes in the cambium ofTectona grandis L. f. andgmelina arborea roxb

Starch, lipids and proteins are localized histochemically in fusiform and ray initials ofTectona grandis andGmelina arborea during the periodicity of cambium in the year 1978. The histochemical variations are correlated with the seasonal activity and dormancy of the cambium and phenology. Starch grains appear in the cambial cells with the development of young leaves after defoliation. Lipid and protein bodies are significantly high in dormant cambial cells and scarce in active ones.     

Ammonia formation in isolated rat liver mitochondria

Studies of isolated rat liver mitochondria were undertaken in order to evaluate the importance of glutamate transport, oxidation reduction state, and product inhibition on the rates of formation of ammonia from glutamate. Uptake and efflux of glutamate across the mitochondrial membrane were measured isotopically in the presence of rotenone. Efflux was stimulated by H+ in the mitochondrial matrix and was found to be first order with respect to matrix glutamate except when the matrix pH was unphysiologically low. The data suggest that the Km of matrix glutamate for efflux is decreased by H+. Matrix H+ also appeared to stimulate glutamate uptake, but the effect was to increase both the Km of medium glutamates and Vmax. Mitochondria were incubated at 15 and 28 degrees C with glutamate and malonate. Under these conditions, glutamate was metabolized only by the deamination pathway. Flux was evaluated by assay of ammonia formation. Oxidation reduction state was varied with ADP and uncoupling agents. Matrix alpha-ketoglutarate was varied either by the omission of malonate from the incubation media or by adding alpha-ketoglutarate to the external media. Influx and efflux of glutamate could be calculated from previously determined transport parameters. The difference between calculated influx and efflux was found to be equal to ammonia formation under all conditions. It was, therefore, possible to evaluate the relative contributions of oxidation reduction state, transport, and product inhibition as effectors of ammonia formation. The contribution of transport was relatively small while oxidation reduction state exerted a large influence. alpha-Ketoglutarate was found to be a potent competitive inhibitor of ammonia production and glutamate dehydrogenase. Inhibition of glutamate dehydrogenase by alpha-ketoglutarate was judged to be a potentially important modulator of metabolic fluxes.     

The use of monoclonal antibodies to localize the low density lipoprotein receptor-binding domain of apolipoprotein B

Human apolipoprotein (apo) B-100 is composed of 4536 amino acids. It is thought that the binding of apoB to the low density lipoprotein (LDL) receptor involves an interaction between basic amino acids of the ligand and acidic residues of the receptor. Three alternative models have been proposed to describe this interaction: 1) a single region of apoB is involved in receptor binding; 2) groups of basic amino acids from throughout the apoB primary structure act in concert in apoB receptor binding; and 3) apoB contains multiple independent binding regions. We have found that monoclonal antibodies (Mabs) specific for a region that spans a thrombin cleavage site at apoB residue 3249 (T2/T3 junction) totally blocked LDL binding to the LDL receptor. Mabs specific for epitopes outside this region had either no or partial ability to block LDL binding. In order to define the region of apoB directly involved in the interaction with the LDL receptor we have tested 22 different Mabs for their ability to bind to LDL already fixed to the receptor. A Mab specific for an epitope situated between residues 2835 and 2922 could bind to its epitope on LDL fixed to its receptor whereas a second epitope between residues 2980 and 3084 is inaccessible on receptor-bound LDL. A series of epitopes near residue 3500 of apoB is totally inaccessible, and another situated between residues 4027 and 4081 is poorly accessible on receptor-bound LDL. In contrast, an epitope that is situated between residues 4154 and 4189 is fully exposed. Mabs specific for epitopes upstream and downstream of the region 3000-4000 can bind to receptor-bound LDL with a stoichiometry close to unity. Our results strongly suggest that the unique region of apoB directly involved in the LDL-receptor interaction is that of the T2/T3 junction.     

Micropropagation of Sterculia urens Roxb. — an endangered tree species

An in vitro procedure for large scale multiplication of Sterculia urens Roxb. (Gum Kadaya Tree) has been developed using cotyledonary node segments. An average of 4.0 shoots per node were obtained on Murashige and Skoog's (MS) medium containing 2.0 mgl^–1 6-benzyl amino-purine (BAP) within 21 days of initial culture. Upon subsequent subculture 16 shoots/node could be harvested every three weeks and upto three times. Sixty per cent of the shoots were successfully rooted. Rooted plantlets were transferred to plastic pots containing soil under mist house conditions before they were finally exposed to an external environment. Fifty seven per cent of the plantlets survived in nursery sheds.     

Degradation of acrylic acid by fungi from petrochemical activated sludge

Summary Geotrichum sp. and Trichoderma sp. isolated from petrochemical effluent treatment plant activated sludge completely degraded 2 g acrylic acid/l as sole carbon source in 4 d. However, after neutralization with Ca(OH)₂, concentration as high as 10 g/l was degraded in 6 d. During the degradation acetic acid and -hydroxy propionic acid transiently accumulated.     

Transfer of heavy metals from sediment to fish,and their biliary excretion

Uptake and biliary excretion of metals were studied in rainbow trout, Oncorhynchus mykiss, exposed through spiked sediment to a mixture of seven heavy metals. Metal concentrations and toxicity of bile and blood plasma were used as indicators of exposure. Among the seven metals (Cd, Cr, Cu, Hg, Ni, Pb, and Zn) only three (Cu, Hg, and Pb) were concentrated in the bile (bile-plasma ratio >1). Bile-plasma ratios in the rainbow trout were similar to those found in rats for Cu and Hg. Daphnia magna bioassays were used to determine toxicity of bile and blood plasma in the same trout. Toxicity of bile and blood plasma increased after treatment with acid. An analysis of variance (ANOVA) showed that toxicity of bile and blood plasma to D. magna in metal-exposed trout was significantly correlated with (1) bile and blood plasma test concentration, (2) acid treatment of bile and blood plasma (hydrolysis of metal-plasma and metal-bile complexes) and (3) sediment concentration of metals during exposure of trout. In order to significantly detect the magnitude of the exposure to a xenobiotic the biomarker must respond in a dose- or time-dependent manner. Therefore, the potential use of bile toxicity as a biomarker of heavy metal exposure in fish is probably limited by the low bioconcentration of many of these toxicants in bile.     

Sediment toxicity in the Kattegat and Skagerrak

Sediments were sampled from 62 sites in the Kattegat and Skagerrak, which are located between the Baltic and the North Sea in the Western Atlantic, during autumn 1989 and spring 1990. From each site 5 to 6 samples were taken wit ha box-corer. After mixing to composite samples on board, transport and storage (at 4 °C for 2 to 4 weeks), the samples were tested for toxicity to Daphnia magna and Nitocra spinipes. Immobility in Daphnia after exposure to 16 percent sediment (wet wt) in reconstituted standardized water (ISO, 1982) ranged from 0 to 88 percent after 24 h and from 3 to 95 percent after 48 h. For Nitocra the toxicity, determined as the 96-h LC50 (% wet wt) at 7 salinity, ranged from > > 32 percent (nontoxic) to 1.8 percent (most toxic). All exposures were made in duplicates and the effects obtained in the duplicates with the same sediment were correlated to each other. However, sediment toxicity to Daphnia and Nitocra was not. The test with Nitocra, which was made at several concentrations of sediment, was considered to give the most reliable picture of sediment toxicity in the Kattegat and Skagerrak. This ambient toxicity assessment identified three areas with toxic sediment, (1) the Göta älv estuary (outside the city of Göteborg) and its surroundings, (2) the Bay of Laholm in southern Kattegat, which is an area with periodic oxygen depletion and where repeated mussel kills have occurred during the last decade, and (3) an area in the open Skagerrak northwest of Skagen (the tip of the Jutland peninsula). Sediments, which had been stored at 4 °C, were tested again after 6 to 13 mos with the Nitocra test. Stored sediment toxicity was poorly correlated with fresh sediment toxicity. The average detoxification during storage was 5 times, but the range was 3 orders of magnitude, from 17 times more toxic to 73 times less toxic. The reasons for the observed areal and storage differences in sediment toxicity are so far not understood.