Species that become naturalized in a new geographical range, subsequently multiply and spread, and persist to the detriment of resident communities, are known as alien invasive species. Two aspects of species invasion – spread and ecological impact – were examined using Lantana camara L. (henceforth lantana) as the study system, specifically in the context of a seasonally dry tropical forest ecosystem of the Mudumalai Wildlife Sanctuary and National Park. Lantana is a thicket-forming woody shrub of South and central American origin, which is now widespread across the tropics. The thesis is divided broadly into two parts -the first part examines the influences of environmental factors on the distribution and spread of lantana while the second part focuses on the effects of lantana on the distribution, survival and growth of native woody species. Much of the work presented in this thesis was conducted within a 50 ha permanent plot (the Mudumalai Forest Dynamics Plot, MFDP hereon) in Mudumalai, chiefly because the history of invasion by lantana has been recorded here since 1989. The influence of changing resources on lantana invasion was explored at two scales -small spatial but fine temporal scale in the MFDP and at the level of the landscape. Available data on an 18 year chronosequence of changes in the qualitative density of lantana from the MFDP and field studies between the years 2009 and 2010 were used to determine the environmental correlates of lantana spread in time and space. It was found that biotic factors such as the presence of the shrub Helicteres isora and abiotic factors such as proximity to drainages and the combination of fire and drought promoted the intensification of lantana invasion in time while proximity to streams, higher total annual rainfall and low fire frequency contributed to lantana invasion at the landscape level. The impacts of lantana on the seedlings of native woody species were assessed in 10m x 10m plots within the MFDP. An initial enumeration of 60 such plots revealed that animaldispersed, dry forest habitat preferring species were most affected by the presence of dense lantana. A follow-up study comprising of growth and survival measurements made on 1105 seedlings over two years (2008-2010) further confirmed that dry forest preferring species were most affected by the presence of dense lantana and that this response at the community level was most likely influenced by the most abundantly sampled species in this habitat preference guild – Catunaregam spinosa. In conclusion, while the environmental correlates of lantana most likely promoted its invasion, only certain guilds of native species seemed to be negatively affected by the presence of lantana.

Urbanization has destroyed and fragmented previously large areas of natural habitat. Small remnants that still exist in numerous cities will be unable to sustain many viable wild plant populations if they do not expand into the surrounding urban matrix. Residential gardens surrounding such remnants, and which form a significant component of urban green space in many cities, could play a role in redressing this problem. Riccarton Bush, a 7.8 hectare forest remnant, and its surrounding suburban residential area, in Christchurch, New Zealand, is a good example. Over 125 years the reported number of native vascular plants in the bush has declined by a third. My study was an attempt to understand: 1) the ecological, social and cultural factors influencing the dispersal and regeneration of 12 native bird-dispersed woody species from Riccarton Bush, into surrounding residential properties; and 2) the potential role residential properties could play in the future of the bush. To examine these diverse factors I adopted an interdisciplinary research approach combining methodologies, concepts and theories from ecology and the social sciences. In a broader context my work was an attempt to demonstrate how urban ecology can further develop and strengthen by adopting and integrating new methodologies, theories and concepts. The ecological component involved recording individuals of the study species found on 90 randomly selected properties within a 1.4 km radius of the bush. Soil samples were also collected from 31 of those properties and placed in a glasshouse and the study species that germinated were recorded. Results showed some species, particularly kahikatea (Dacrycarpus dacrydioides), the most abundant species in the bush, are being dispersed and establishing on properties predominantly within 250 m of the forest margin. These juveniles are not reaching maturity as most gardeners tend to remove all non-planted woody species. Qualitative interviews with 16 residents and a quantitative survey of the residents of 85 of the properties provided insights into the social context which these natural processes were operating. Using notions of place and performance I argue that gardens are continuously created and recreated by humans and non-humans. Residents attempt to create and maintain a garden that fulfils their individual and familial needs and desires (e.g., aesthetics, leisure and privacy), and public responsibilities such as ensuring they have a ‘neat’ and ‘tidy’ garden. This involves selecting plants for colour, shape and the care they require, and encouraging certain performances (e.g., flowering) while controlling other undesirable plants and performances (e.g. growth, spread and shading). While people make connections between native plants, belonging and identity; the ‘scientific’ demarcation between native and exotic species often becomes obscured as the garden is co-created by people and plants. Some plants become more significant than others but usually this is attributable to their performances rather than whether they are native or exotic. Residential gardens have the potential to play a major role in the conservation of species restricted to urban remnants. My research suggests that although the potential exists for woody species restricted to Riccarton Bush to naturally regenerate in nearby gardens, this will not happen without human intervention. Plants will need to be eco-sourced and propagated to avoid detrimental impacts on the genetic health of remnant populations, and then actively planted in gardens. The success of such planting initiatives will be increased by providing residents with information about the plants that are suitable for their performative needs and desires (e.g., the size, colour, and maintenance requirements of plants) and, most importantly, control over the location of plantings. In concluding, I argue that by adopting new concepts, theories and methodologies, the productivity, creativity and relevance of urban ecology can be significantly enhanced.