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Population and behavioural studies on Calycomyza eupatorivora spencer (Diptera : Agromyzidae), a biological control agent of Chromolaena odarata (L.) King and Robinson (Asteraceae) in South Africa.Nzama, Sindisiwe N. 27 November 2013 (has links)
Chromolaena odorata (L.) King and Robinson (chromolaena, triffid weed) (Asteraceae: Eupatorieae) is one of the most problematic weeds in the subtropical northeastern parts of South Africa. Calycomyza eupatorivora Spencer (Diptera: Agromyzidae) was introduced as a biological control agent for the control of this weed. No study has yet been done to quantify field populations of C. eupatorivora since its establishment in 2003. The aim of this study was therefore to measure aspects of the field population and laboratory behaviour of C. eupatorivora on C. odorata.
The first objective was to determine the percentage leaf area mined by larvae of C. eupatorivora on C. odorata plants exposed to three densities of mated flies, and also to determine the number of mines produced by these different densities, and their distribution on the plant. It also attempts to determine the relationship between chromolaena leaf quality and usage by C. eupatorivora. The maximum percentage of leaf area damaged was 37.5% for one of the trials involving five pairs of flies. Mean percentage leaf area damaged was slightly higher with five (28.5%) than ten pairs (22.0%) of adults and was lowest with one pair (6.5%), but these differences were not significant. In relation to the mean number of mines per plant, five and ten pairs of flies caused slightly more mines than one pair. The other significantly different parameter was number of leaves mined per plant, which was higher for five pairs. Within a plant, C. eupatorivora probably selects a subset of leaves with certain chemical and physical characteristics for oviposition since certain leaves were left unmined while others received multiple eggs. Percentage water content did not differ between mined and unmined leaves, but clear patterns were shown by acid detergent lignin which was higher in unmined leaves and nonstructural carbohydrates which were much higher in mined leaves. It is likely that leaf age plays a role in its suitability.
The second objective was to quantify C. eupatorivora infestation levels, by counting and examining larval leaf mines, on C. odorata in the field at four times ('seasons' - September, December, March and July) over a 12-month period, and at three study sites that each included two habitats, viz. open and shady. At each of these six sampling sites, line transects were laid out and plants/branches sampled along them. Both plant/branch height and the number of leaves increased between September and March, and plants in the open habitats were taller and had more leaves than those in the shaded habitats. At the third site, the shady habitat supported taller plants with more leaves compared to the same habitat at the other sites. There was a steep increase in the number of C. eupatorivora mines from December to March. The mean number of mines, both total and in relation to leaves available, was highest in March, and was higher in the shaded habitats compared to the open habitats. The mean number of mines per damaged leaf was slightly higher in December compared to the other seasons, and was also higher in the open than the shaded habitats. Mean larval mortality was high (70%) in September but decreased to 32% in December, and increased again in late summer. The overall levels of mining by C. eupatorivora were low, with less than 5% of leaves sampled having mines. Taken together, the laboratory and field trials suggest that C. eupatorivora is restricted to a subset of the leaves of C. odorata for its development; that the field population is unable to make full use of the resource of young, palatable leaves that develop in early- to mid-summer because it only becomes large in late summer; and that the high mortality rate of young larvae negatively affects both the population of the fly and the level of damage to the plant. Given that these results were obtained in an area where the population of C. eupatorivora is relatively high, it is unlikely that the fly is having anything more than a negligible effect on C. odorata in South Africa at present. / Thesis (M.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2011.
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Monitoring serial changes in coastal grasslands invaded by Chromolaena odorata (L.) R.M. King and Robinson.Goodall, Jeremy Marshall. 17 December 2013 (has links)
The objective of this study was to describe the impacts of the density of Chromolaena odorata
(chromolaena) on species composition in coastal grasslands and to investigate serial changes in
the vegetation following the implementation of a burning programme. The thesis deals with key
ecological concepts and issues, so a comprehensive literature review is included.
Chromolaena invades coastal grasslands that are not burnt regularly (i.e. biennially). Grasslands
that were not burnt for 30 years were seral to secondary forest. The successional pathway from
open grassland to closed canopy forest varied according to soil type. Coastal grasslands on
Glenrosa soils were characterised by savanna at an intermediate stage between the grassland and
forest states. Shading ended the persistence of savanna species (e.g. Combretum molle,
Dichrostachys cinerea and Heteropyxis natalensis) in forest, whereas forest precursors (e.g.
Canthium inerme, Maytenus undata and Protorhus longifolia) only established where fire was
absent. Chromolaena infestations were characterised by multi-stemmed adult plants of variable
height (i.e. 1-3 m), depending on soil type. Regic sands did not support stratified woody
vegetation and chromolaena infestations were self-supporting, reaching a maximum height of
1.5 m. Glenrosa soils supported tree communities and chromolaena reached more than 3 m in
places. The density of chromolaena affected species composition in grasslands with moderate to
dense stands (> 5 adult plants m ¯² or >50000 shrubs ha ¯¹). Chromolaena stands became monospecific when the number of adult plants exceeded 7 m ¯². Succession to forest also ceased
once chromolaena became thicket-forming.
Fire-induced mortality of the chromolaena depended on grass fuel loads. Grass cover of 30% (c.
1 000 kg ha ¯¹) was required to achieve 80% mortality of the parent infestation after the initial
burn. Dense infestations could only be killed by running head-fires from adjacent grasslands
into thickets. Under conditions where head-fires could not be used, infestations were slashed
and burnt at the height of the dry season (July to August) to achieve an 80% kill rate. Seedlings
were killed (99%) by annual burning in sparse (≤ 10000 shrubs ha ¯¹) to moderate
< 50 000 shrubs ha ¯¹) infestations. The suppression of chromolaena and other alien species,
establishing on bare ground after clearing dense infestations, required chemical control until
grass cover was sufficient (i.e. 1 000 kg ha ¯¹) to effect uniform burning. Certain secondary alien
invaders (e.g. Lantana camara, Psidium guajava and Solanum mauritianum) persisted by
coppicing profusely after fire and herbicides need to be integrated into burning programmes
when these species occur. Grasslands on regic sands (e.g. Ischaemum fasciculatum, Panicum
dregeanum and Themeda triandra) were more resilient to the modifying effects of woody
vegetation, than grasslands on Glenrosa soils. Grasslands on Glenrosa soils did not revert to an
open state but persisted as ruderal savanna grassland (e.g. Eragrostis curvula, Hyparrhenia
tamba and Cymbopogon validus) once fire-resistant tree species (e.g. Combretum molle and
Heteropyxis natalensis) had established.
Depending the objectives for land management and the vegetation's condition, coastal
grasslands can be rehabilitated and managed in multiple states, i.e. grassland, savanna or forest
communities. A state-and-transition model based on the empirical data recorded in the study is
presented and shows chromolaena altering vegetation states from open grassland to chromolaena
dominated thicket. The model illustrates chromolaena thickets as the dominant phase of a moist
coastal forest/savanna succession, irrespective of soil type, in absence of appropriate land
management practices (e.g. control burning and integrated control of alien vegetation). This
model should aid in planning strategies for the control of chromolaena in subtropical grasslands in South Africa. / Thesis (M.Sc.)-University of Natal, Pietermaritzburg, 2000.
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Caractérisation structurale et biologique de nouveaux agents antibactériens naturels actifs dans les infections intestinales : des peptides de la chromogranine A et des principes actifs de Chromolaena odorataAtindehou, Ménonvè 15 June 2012 (has links) (PDF)
Les premières souches bactériennes résistantes aux antibiotiques sont connues depuis 70 ans et se sont multipliées ces dernières années posant un grave problème de santé publique. Parmi les nombreux types d'infections induites par ces bactéries, nous nous sommes intéressés aux infections intestinales qui peuvent dégénérer en maladies inflammatoires de l'intestin et cancers. Notre travail de thèse a consisté à proposer des outils thérapeutiques dans le traitement des pathologies intestinales infectieuses : des peptides antimicrobiens dérivés de la chromogranine A et des extraits de plantes de la médecine traditionnelle béninoise. La chromogranine A est une protéine libérée par les cellules nerveuses, neuroendocrines et immunitaires au cours d'un stress et maturée en peptides. Des peptides actifs contre quatre souches bactériennes pathogènes (Klebsiella oxytoca, Salmonella enterica, Shigella sonnei et Vibrio cholera non O1) ont été identifiés et l'interaction bactérie-peptide analysée. L'étude de la combinaison peptide-antibiotique montre que la cateslytine permet de réduire les doses d'antibiotiques nécessaires. Ensuite, nous avons étudié l'implication de deux peptides sur un modèle de cellules neuroendocrines, les cellules BON. La chromofungine provoque la stimulation des cellules BON en induisant un influx de calcium extracellulaire, tandis que la catestatine est capable de bloquer l'activité de la chromofungine.Après un screening des extraits de 14 plantes du Bénin, nous avons isolé deux molécules, la sinensétine et l'O-tétraméthyléther scutellaréine, responsables de l'activité antibactérienne de Chromolaena odorata contre les pathogènes étudiés.
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