No description available.

Dissertação (mestrado) - Universidade Federal de Santa Catarina, Centro de Ciências Agrárias. Programa de Pós-Graduação em Aquicultura. / Made available in DSpace on 2013-07-16T03:08:57Z (GMT). No. of bitstreams: 1 235257.pdf: 966947 bytes, checksum: 82774c3c6a457b2783c7e2174d3f8fd9 (MD5)

Dissertação (mestrado) - Universidade Federal de Santa Catarina, Centro de Ciências Agrárias. Programa de Pós-Graduação em Aqüicultura. / Made available in DSpace on 2012-10-20T04:45:49Z (GMT). No. of bitstreams: 0

Thesis (Ph. D.)--Illinois State University, 1968. / Title from title page screen, viewed Aug. 18, 2004. Dissertation Committee: Jack A. Ward (chair), John Frehn, Howard R. Hetzel, Robert Weigel, Edwin Willis. Includes bibliographical references (leaves 126-129). Also available in print.

Neem, Azadirachta indica, products were tested for toxic, growth regulating, primary antifeedant, and secondary antifeedant effects on Dermestes maculatus, under conditions approximating those found in storage facilities. Toxic and growth regulating effects were investigated using topical application of mineral oil, neem oil, purified azadirachtin/methanol solution, and 10% neem seed kernel extract/methanol solution. All neem treatments exhibited higher mortality than the mineral oil treatment 5, 10, and 14 days after the application of the treatments; larvae treated with neem products often failed to pupate and never emerged as adults. Primary antifeedant effects of azadirachtin (1.5 g/L and 5 g/L) were investigated with an original no-choice feeding bioassay. Significant primary antifeedant effects were observed which were persistent for up to 13 weeks for adults and 17 weeks for larvae. Significant secondary antifeedant effects were also demonstrated after topical application of azadirachtin (.125 g/L, .25 g/L and .5 g/L) to the larvae.

Thesis (Ph. D.)--Illinois State University, 1973. / Title from title page screen, viewed Oct. 14, 2004. Dissertation Committee: J.A. Ward (chair), Lauren Brown, D. Birkenholz, B. Richards, J. Tone. Includes bibliographical references (leaves 277-284) and abstract. Also available in print.

No description available.

Vocal mimicry is well documented in songbirds, yet the function of this behaviour is poorly understood. I studied vocal mimicry in a wild population of male spotted bowerbirds Ptilonorhynchus maculatus to determine whether there was any support for the proposed functional hypotheses invoked to explain this behaviour. I collected observational data to determine what species male bowerbirds mimicked and how their mimetic repertoires related to the acoustic environment. Spotted bowerbirds preferentially mimicked the vocalisations of aggressive species, which is consistent with mimicry acting to deter predators or competitors (Batesian mimicry). However, these sounds were also relatively simple in terms of their structure, and may be mimicked purely due to their simplicity and similarity to the species-specific hiss. A survey of mimetic repertoires at three geographically isolated populations revealed a similar pattern in model choice: mimetic repertoires were predominantly composed of aggressive and predatory species but these sounds were also structurally simple. To test whether mimicry was used in a Batesian context I determined what contexts mimicry was produced in. Consistent with predictions, I found that males did not increase their mimetic rate in the presence of conspecifics but did increase their mimetic rate in response to human activity around the bower. To determine how mimetic sounds are acquired in this species, I compared the mimetic repertoires of individuals within a population and found that males with bowers closer together mimicked more of the same species than did males with bowers that were further apart. Closer inspection of two of these mimicked sounds revealed that neighbouring males did not produce structurally similar mimicry,which suggests that mimetic sounds are learned directly from the species being mimicked. Males did not increase their rate of species-specific vocalisation when mimetic rate increased, so these vocalisations are unlikely to serve the same function. Males increased their rate of species-specific hissing when in the presence of conspecifics and this vocalisation is likely to function in intraspecific communication. Males also produced ‘advertisement’ calls when alone at the bower that are likely to attract females to the bower or deter rival males. These vocalisations are a long distance signal that varied in structure in three populations of bowerbird. I discuss potential explanations for geographic variation in the structure of bowerbird vocalisations. Vocalisations may be part of the multi-component sexual signal produced by bowerbirds, but I found no relationship between any aspect of male vocalisation and predicted mating success, so these vocalisations are unlikely to indicate male quality to potential mates or rival males. In conclusion, it seems most likely that mimicry in this species is used to deter predators or competitors, but I cannot exclude the hypothesis that mimetic sounds are learned as a result of their relative simplicity and salience in the acoustic environment. Furthermore, I have shown that mimetic sounds in this species are most likely acquired directly from the species being mimicked. These findings are a useful step towards understanding the function and evolution of this fascinating behaviour.

Post-copulatory sexual selection is a strong evolutionary force, affecting morphological and behavioural traits in males and females in species with polyandrous mating systems. Many insects are subject to sperm competition; sperm from rival males compete to fertilise ova. Since sperm are finite, males should allocate them economically, tailoring ejaculate allocation to suit the reproductive potential of individual matings. Theory suggests when sperm competition risk is high, males should increase sperm numbers to achieve greater reproductive success than their rivals, but evidence of this expected fitness consequence of ejaculate allocation is largely lacking. In this thesis, I use Callosobruchus maculatus beetles to investigate the causes of ejaculate allocation patterns, and to examine whether ejaculate allocation does affect male reproductive success. In Chapter 3, I investigate the effect of rival male presence on ejaculate size and find that, while males grouped with rivals as adults produce bigger ejaculates, their increased effort unexpectedly does not lead to increased reproductive success. In Chapter 4, I examine whether larval conditions also affect ejaculate size, and find that, contrary to sperm competition theory, males reared under dense conditions produce smaller ejaculates than those reared solitarily, and that male reproductive success is consequently elevated in males reared at low larval densities compared to those reared at high densities. In Chapter 5, I then demonstrate that ejaculates produced by low density males contain more sperm than ejaculates produced by high density males, suggesting males do not respond to sperm competition level represented by larval density, but instead suffer resource limitation when reared at high density. In Chapter 6, I investigate the effects of water provision on ejaculate size, and find that males given water produce larger ejaculates, and females given water receive smaller ejaculates. Finally, I link my findings with those of other studies, and suggest my most important result is that plasticity of ejaculate allocation cannot be assumed to be an adaptive behaviour; studies directly measuring the fitness effects of male ejaculate allocation are needed, even when observed patterns conform to theory.

The spotted minnow, Galaxias maculatus has a widespread southern hemisphere and circum-polar distribution including south-western and south-eastern Australia. It was sampled at monthly intervals over 12-18 months, by seine and plankton netting at three localities including a freshwater lake, Moates Lake, and two intermittently flowing, naturally saline rivers, the Jerdacuttup and the Oldfield rivers on the south coast of Western Australia. The resulting data provided an opportunity to describe the biology of G. maculatus in some detail including; environmental variables, life cycle, larval development, diet and parasitism by platyhelminth and nematode worms. Comparisons were made with other studies in south-east Australia, including Tasmania, and New Zealand. The present study confirmed that, at least throughout most of its range in Western Australia, G. maculatus has established a self-sustaining land-locked reproductive strategy. It is hypothesised that the development of land-locked breeding is an adaptive response to changing coastal geomorphology in the Holocene period that restricted ocean access of rivers and their fauna and caused estuaries to become non-tidal. The principal conclusion arising is that the local biology differs largely in degree rather than kind from elsewhere it has been studied; differences in degree are interpreted as local adaptations to an environment that is both variable and unpredictable Field measurement of environmental variables revealed G. maculatus will withstand salinities to approximately 46 ppt and surface water temperatures to 280 c. Very low dissolved oxygen concentrations to <1.0 mg r1 are accommodated by practicing secondary aerial respiration at the water surface. Galaxias maculatus on the south coast of Western Australia were smaller than those reported from populations elsewhere. Overall tota11engths of Western Australian males and females ranged 23-132 mm compared to 38-187 mm length to caudal fork for south-west Victoria, 31-185 mm standard length for Tasmania and 40-152 mm length to caudal fork for New Zealand fish. In the present study, size varied between the lake and one river population that was smaller. It is hypothesised that reduction in size of Western Australian G. maculatus generally is an adaptive response to avoid predation by piscivorous birds in shallow, confined river pools and lakes. There was a well defined, albeit extended, breeding season between autumn and spring with peak spawning in winter. The season was longer in the relatively stable lake situation and shorter ~ the very variable river situation partly due to the influence of river flow, which is continuous into the lake and intermittent and variable in the rivers. A flow dependent upstream spawning migration was part of the reproductive strategy but there was also the capacity, in certain circumstances, of spawning on falling water levels in years of nil or little flow. There was an almost complete cessation of reproductive activity during summer. Fecundity ranged from 296-2 874 eggs with a mean of 912 and was positively correlated with total length. The overall total lengths at which 50% of females and males and attain sexual maturity were estimated at 52 and 49 mm total length, respectively. For 95% of females and males the total lengths were estimated at 74 and 62mm total length, respectively. Ageing by counting annual growth rings was successful for lake inhabiting fish only, the lack of consistency in growth rings in the river environments was attributed to the extreme variability of these environments. The von Bertalanffy growth equation predicted that, on average, at the end of their first, second and third years females were 61, 81 and 88 mm total length respectively. Male predictions were 56, 74 and 80 mm, respectively. Approximately 75% of males and 62% of females attained sexual maturity at the end of their first year. Excluding larval fish, 73.1, 22.7, 4.1 and 0.1 % were 0+, 1+, 2+ and 3+ fish, respectively. The overall sex ratio females:males was 1.09:1.0, the ratio favoured males for very small fish but favoured females as fish aged and grew. Larval development was described in detail for the first time for Australian G. maculatus. The sequence of fin development was the same as that reported for galaxiids elsewhere, i.e. caudal, dorsal, anal, pectoral and pelvic. Adult fin ray counts were; cauda1 16, dorsa1 9, anal 13, pectoral 12 and pelvic 6-7. Myomeres ranged from 45-50. Development of pigmentation and dentition were described; caniniform teeth began to develop during the late postflexion larval stage. Dietary analysis confirmed a previous description of G. maculatus as an euryphagic carnivore. A wide range of invertebrate food groups including copepods, amphipods and ostracods, aquatic insects as well as terrestrial invertebrates (spiders, winged ants and orthopterans) were consumed. Most variation in diet was explained by site, i.e whether fish were from river or lake environments or which river environment. A lack of replicate samples precluded a rigorous statistical analysis of the influence of either fish size or season on diet. However, a provisional analysis suggested these variables have minimal influence. Larval diets comprised copepods, cladocerans and unicellular algae; with the attainment of postflexion larval stage and development of caniniform dentition, a wider range of dietary items were ingested. One cestode, one trematode and two nematode larval worms infected river and lake inhabiting fish. The cestode, Ligula intestinalis, infected 13% of lake inhabiting fish causing gross disfiguration and probably reduced reproductive success, particularly of males. The degree and severity of cestode infection was much less in rivers, perhaps due to their saline waters. The worms' adult hosts in all cases were piscivorous waterfowl particularly the white-faced heron. At present G. maculatus is widespread and abundant throughout its range in Western Australia. As most of its range is in rivers and lakes which are, and will in the future be influenced by clearing for agriculture, it is likely that increased river recharge due to clearing will initially benefit G. maculatus. However long term change, particularly changes to riparian vegetation structure and species composition, are likely eventually to be inimical as the shading value of vegetation and its habitat value for terrestrial invertebrate food are diminished.