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1.
Arch Environ Contam Toxicol ; 32(1): 11-21, 1997 Jan.
Article in English | MEDLINE | ID: mdl-9002430

ABSTRACT

Insecticides are increasingly being used in hot arid ecosystems. The evaluation of the ecological risk these insecticides may pose, however, is based largely on data derived from temperate organisms and ecosystems. The major differences in the composition, structure, and functioning of desert animal communities when compared to temperate terrestrial ecosystems are discussed. Desert communities are characterized by a high fraction of ectotherms (both vertebrates and invertebrates);rodents and insectivores appear to dominate the mammalian fauna; and detritivores make up a very large part of the arthropod fauna. Presently available toxicity data cover these groups only to a very limited extent. It is not known if the ranges of insecticide susceptibility observed in temperate species are representative of those in arid organisms. Thus, it is not certain that ecotoxicological assessments based on such data sets adequately protect desert animal communities. It is shown that food web connectance is higher in desert ecosystems than in temperate grasslands or forests. This may to a large extent be due to the high degree of omnivory among desert organisms. Population regulation between predators and prey appears to be weaker in deserts. The same is often, though not always, the case for competition among desert organisms. It is argued that such characteristics will reduce the chance that strong indirect effects of insecticide perturbations will occur. In spite of the fact that many desert organisms are well adapted to cope with high temporal and spatial environmental variability, there is no reason to believe that they will always recover more rapidly from population perturbations caused by insecticides. The relatively large physiological and life-history plasticity encountered in many desert animals may increase tolerance to insecticide stress. Food chains are longer in deserts than in temperate grasslands and forests. The implications of this observation for the risk of biomagnification of contaminants are discussed.


Subject(s)
Ecosystem , Insecticides/toxicity , Agriculture/trends , Animals , Climate , Environmental Monitoring/standards , Food Contamination , Poisoning , Risk Assessment , Species Specificity
2.
Plant Physiol ; 87(2): 536-41, 1988 Jun.
Article in English | MEDLINE | ID: mdl-16666179

ABSTRACT

The distribution and subcellular localization of the two major proteases present in oat (Avena sativa L. cv Victory) leaves was investigated. Both the acidic protease, active at pH 4.5, and the neutral protease, active at pH 7.5, are soluble enzymes; a few percent of the enzyme activity was ionically bound or loosely associated with organellar structures sedimenting at 1000g. On the average, 16% of the acidic protease could be washed out of the intercellular space of the leaf. Since isolated protoplasts contained correspondingly lower activities as compared to crude leaf extracts, part of the acidic activity is associated with cell walls. No neutral protease activity was recovered in intercellular washing fluid. Of the activities present in protoplasts, the acidic protease was localized in the vacuole, whereas the neutral protease was not. The localization of the acidic protease in vacuoles did not change during leaf development up to an advanced stage of senescence, when more than 50% of the leaf protein had been degraded. These observations indicate that protein degradation during leaf senescence is not due to a redistribution of acidic protease activity from the vacuole to the cytoplasm.

3.
Plant Cell Rep ; 7(7): 489-92, 1988 Dec.
Article in English | MEDLINE | ID: mdl-24240398

ABSTRACT

The DNA of agarose-embedded protoplasts of Nicotiana plumbaginifolia was stained with Hoechst 33342 by immersing microscope slides, coated with immobilized protoplasts, into Erlenmeyer flasks containing consecutively dye solution, pH-correcting washing solutions and culture medium. After staining, protoplasts regenerated cell walls, started to divide and proliferated to calli. The culture system with immobilized protoplasts permits rapid change of culture media and accurate control of experimental conditions. The staining technique offers the opportunity for continuous observation of chromosomal behaviour and cell dynamics in individual plant cells.The same staining procedure was successfully applied to DNA of plant cells in suspension. Flow cytometric analysis revealed a retarding effect of the dye on the cell cycle, but within hours the cells recovered and showed their normal growth characteristics as compared to the controls.

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