The Control of Food Mobilization in Seeds of Cucumis sativus L. VI. The Production of Starch

During germination and early seedling growth of cucumber, cotyledonarylipid and protein reserve material mobilization is controlledthrough a cotyledon/axis, source/sink relationship. Earlierwork has shown that some cotyledonary lipid breakdown is ableto occur even in the absence of the embryonic axis. This studyshows that such breakdown is probably a consequence of the formationof a transitory starch store. Excised cucumber cotyledons accumulatelarge amounts of starch following the accumulation of reservebreakdown products which can no longer be utilized in the absenceof the axis and represents a mechanism in the issue to regulatethe concentration of osmotically active substances such as sucroseand glucose. The starch content of both attached and excisedcotyledons increased during the experimental period. In theformer case, however, the increase was very small and starchlevels fell subsequently, while in the later instance the increasecontinued, reaching a maximum at day 8 after which it stabilizedat this elevated level. The increase in starch content is mostclosely correlated with an increase in the activity of boundADPG-starch synthase although soluble ADPG-starch synthase activityalso increases during the experimental period. Cucumber, Cucumis sativus, starch, food mobilization, germination, ADPG-starch synthase     

EVALUATION OF BEADRETRIEVERTM, AN AUTOMATED SYSTEM FOR CONCENTRATION OF ESCHERICHIA COLI O157 FROM ENRICHMENT CULTURES BY IMMUNOMAGNETIC SEPARATION

The aim of this study was to compare automated immunomagnetic separation (AIMS) with manual IMS (MIMS) for detection of E. coli O157 in natural and artificially inoculated samples. E. coli O157 was isolated from 27 (14.7%) of 184 natural bovine fecal samples by MIMS and from 26 (14.1%) by AIMS. Of 94 natural carcass samples, E. coli O157 was isolated from 6 by both MIMS and AIMS and from a further 6 by AIMS only. Three of the six positive only by AIMS were from tubes processed adjacently to one containing an inoculated sample and strains isolated from these adjacent tubes were indistinguishable by various typing techniques. Of the 36 carcass samples inoculated with E. coli O157, the organism was isolated from 25 by both MIMS and AIMS and from a further 9 by AIMS only. To process 100 samples by MIMS took 5h whereas by AIMS this took only 3h 20 min which represented a considerable saving of staff time.     

Exposure of seawalls to waves within an urban estuary: effects on intertidal assemblages

Abstract Despite being largely protected from sea swell by headlands, shores within Sydney Harbour, New South Wales, Australia are subjected to considerable wave action from wind waves and the numerous recreational and commercial boats and ships using the waterways. The aim of this study was to test whether assemblages on artificial shores, that is, seawalls, either exposed to or sheltered from waves would show similar patterns to those published for natural shores exposed to or sheltered from sea swell. Specifically, the hypotheses were tested that sheltered seawalls would have greater cover of algae, whereas exposed seawalls would have greater cover of sessile invertebrates and greater abundance of mobile invertebrates. It was found that encrusting algae had greater cover on sheltered seawalls, whereas cover of turfing algae was greater on exposed walls. Sessile filter‐feeders generally had greater cover on exposed seawalls, although a dominant space occupier, the oyster Saccostrea glomerata, showed either no difference, or greater cover on sheltered seawalls among different locations. The pattern for the dominant grazer on seawalls, the pulmonate limpet Siphonaria denticulata showed the predicted pattern low on the shore, but the opposite pattern at mid‐tidal levels. Despite some inconsistencies the results were similar to those predicted from studies on natural shores, showing that assemblages on urban structures respond to wave action in a way that is predictable from studies on natural shores. Experiments were carried out where assemblages were transplanted to sites with differing exposure to waves to determine whether differences in recruitment or post‐recruitment mortality were responsible for patterns of difference. We found that some sessile invertebrates did not survive when transplanted to sheltered seawalls, suggesting that difference in survival of organisms was responsible for observed patterns. This was not, however, found when the experiment was repeated at other locations. It is likely that processes affecting the assemblages are temporally and spatially very variable, or that more than one process interacts to cause observed patterns. Identifying such complexity requires rigorously structured sampling designs and appropriate manipulative experiments.     

Land use and the ecology of benthic macroinvertebrate assemblages of high-altitude rainforest streams in Uganda

1. In sub‐Saharan Africa, tropical forests are increasingly threatened by accelerating rates of forest conversion and degradation. In East Africa, the larger tracts of intact rainforest lie largely in protected areas surrounded by converted landscape. Thus, there is critical need to understand the functional links between large‐scale land use and changes in river conditions, and the implications of park boundaries on catchment integrity. 2. The objective of this study was to use the mosaic of heavily converted land and pristine forest created by the protection of the high‐altitude rainforest in Bwindi Impenetrable National Park, Uganda to explore effects of deforestation on aquatic systems and the value of forest in buffering effects of adjacent land conversion. A set of 16 sites was selected over four drainages to include four categories of deforestation: agricultural land, deforested upstream (of the park boundary), forest edge (park boundary) and forest. We predicted that forest buffer (downstream or on the edge) would moderate effects of deforestation. To address this prediction, we quantified relationships between disturbance level and both physicochemical characters and traits of the macroinvertebrate assemblages during six sampling periods (February 2003 and June 2004). 3. Results of both principal components analysis and cluster analyses indicated differences in limnological variables among deforestation categories. PC1 described a gradient from deforested sites with poor water quality to pristine forested sites with relatively good water quality. Agricultural sites and deforested upstream sites generally had the highest turbidity, total dissolved solids (TDS), and conductivity values and low transparency values. Forest sites and boundary site groups generally exhibited low turbidity, TDS, and conductivity values and high water transparency values. Sites also clustered according to deforestation categories; forest and forested edge sites formed a cluster independent of both agricultural land and deforested‐upstream. 4. Water transparency, water temperature, and pH were the most important factors predicting benthic macroinvertebrate assemblages. Sensitive invertebrate families of Trichoptera, Ephemeroptera, Plecoptera, and Odonata dominated forested sites with high water transparency, low water temperature, and low pH while the tolerant families of Ephemeroptera, Diptera, Hemiptera, and Coleoptera were abundant in agriculturally impacted sites with low water transparency, high water temperature, and high pH. 5. This study provides support for the importance of riparian buffers in moderating effects of deforestation. Forest and forested edge sites were more similar in both limnological and macroinvertebrate assemblage structure than sites within or downstream from agricultural lands. If the protected area cannot encompass the catchment, the use of rivers as park boundaries may help to maintain the biological integrity of the rivers by buffering one side of the watercourse.