Diorhabda elongata elongata leaf beetles were released at two field locations in the upper Colorado River watershed of Texas in 2003 and 2004 for the biological control of invasive Tamarix, exotic trees deteriorating riparian ecosystems of western North America. Establishment and biological success were monitored using trees on transects from the release points. D. elongata elongata released at the Lake Thomas site in August 2003 successfully overwintered and were recovered in the spring 2004; however, beetles were not present after June 2004. The April 2004 release at Beals Creek led to establishment and survival during 2005 and 2006. Mean abundance increased from less than five insects per tree per 2 minute count in August 2004 to more than 40 insects per tree per 2 minute count in August 2006. By then the population was dispersed throughout an area of approximately 12 hectares and beetles were present on 100% of the 47 trees surveyed, 57% of which were at least 90% defoliated. To measure the impact of beetle defoliation on Tamarix, nonstructural carbohydrates (NCHOs) were measured in manipulative field cage experiments in Texas and natural experiments in Nevada. There was no significant difference in NCHOs between trees with versus trees without beetle herbivory in the cage experiment, although spring foliage regrowth was reduced by 35% in trees defoliated the previous fall. In Nevada, root crown tissue was sampled in 2005 and 2006 from trees that had experienced 0-4 years of defoliation. In 2005, NCHO concentrations differed between tree stands and ranged from 9.0 ± 0.8% (Mean ± SE) in non-defoliated trees to 3.2 ± 0.4%, 2.1 ± 0.4% and 2.3 ± 0.4% in trees defoliated for 1, 2 and 3 successive years, respectively. NCHO concentrations in 2006 were similar, ranging from 13.6 ± 0.9% in non-defoliated trees to 7.6 ± 0.8%, 2.3 ± 0.4%, 1.5 ± 0.3% and 1.7 ± 0.4% in trees defoliated for 1, 2, 3 and 4 years, respectively. The establishment, biological success and host impact of D. elongata leaf beetles suggest there is potential for biological control of Tamarix in the United States.

Diorhabda elongata elongata leaf beetles were released at two field locations in the upper Colorado River watershed of Texas in 2003 and 2004 for the biological control of invasive Tamarix, exotic trees deteriorating riparian ecosystems of western North America. Establishment and biological success were monitored using trees on transects from the release points. D. elongata elongata released at the Lake Thomas site in August 2003 successfully overwintered and were recovered in the spring 2004; however, beetles were not present after June 2004. The April 2004 release at Beals Creek led to establishment and survival during 2005 and 2006. Mean abundance increased from less than five insects per tree per 2 minute count in August 2004 to more than 40 insects per tree per 2 minute count in August 2006. By then the population was dispersed throughout an area of approximately 12 hectares and beetles were present on 100% of the 47 trees surveyed, 57% of which were at least 90% defoliated. To measure the impact of beetle defoliation on Tamarix, nonstructural carbohydrates (NCHOs) were measured in manipulative field cage experiments in Texas and natural experiments in Nevada. There was no significant difference in NCHOs between trees with versus trees without beetle herbivory in the cage experiment, although spring foliage regrowth was reduced by 35% in trees defoliated the previous fall. In Nevada, root crown tissue was sampled in 2005 and 2006 from trees that had experienced 0-4 years of defoliation. In 2005, NCHO concentrations differed between tree stands and ranged from 9.0 ± 0.8% (Mean ± SE) in non-defoliated trees to 3.2 ± 0.4%, 2.1 ± 0.4% and 2.3 ± 0.4% in trees defoliated for 1, 2 and 3 successive years, respectively. NCHO concentrations in 2006 were similar, ranging from 13.6 ± 0.9% in non-defoliated trees to 7.6 ± 0.8%, 2.3 ± 0.4%, 1.5 ± 0.3% and 1.7 ± 0.4% in trees defoliated for 1, 2, 3 and 4 years, respectively. The establishment, biological success and host impact of D. elongata leaf beetles suggest there is potential for biological control of Tamarix in the United States.

Covering 30% of the land surface and storing 45% of terrestrial carbon, forest ecosystems play a major role in global biogeochemical cycles and climate. Despite the importance of forests, responses and feedbacks of forests to global change agents remain among the least understood processes in predicting future global change scenarios. We use the temperate forests biome of the eastern US as a case study to ask several general questions about tree physiology and ecology to inform key knowledge gaps relevant to predicting how forests will respond to future global change. Trees invest significant amounts of carbon into support tissues, defense, and storage. To begin, we examine the process of tree carbon storage, as measured by nonstructural carbohydrates (NSCs) by evaluating the extent that NSCs vary as a function of tree life history strategy, physical traits, and phylogeny. We find that NSCs vary largely at broad taxonomic scales, and across study sites. This suggests that a broad-based approach to studying NSCs is needed if they are to effectively inform ecosystem models. Next, we use annual tree ring increments to determine the spatial scales controlling variation in tree growth. We find that individual variability is the largest control on growth, explaining 27% of variability – and primarily explained by tree size, canopy position, and species. Regional-scale variability is the next most dominant, explaining 13% of variability – half of which is explained by changes in species composition across the region. Growth and mortality are important demographic processes responsible for large, and potentially rapid, changes to the terrestrial carbon cycle. In the last chapter, we explore the extent that NSCs explain growth and mortality. We find that stressed trees have significantly lower NSC concentrations than living trees and dead trees have the lowest concentrations. We also find that the strength and direction of the NSC – growth relationship varies greatly by species This dissertation contributes to our understanding of the processes driving tree growth and NSC storage dynamics, as well as the extent to which NSCs drive tree demographic processes across eastern US forests.

Submitted by MARCELLO BONTEMPI PIZZI null (marcello.pizzi@gmail.com) on 2016-09-30T19:50:12Z No. of bitstreams: 1 Marcello_Bontempi_Pizzi_Dissertacao_UNESP_Desfolhas_Sucessivas.pdf: 7157176 bytes, checksum: 6cac889ca8ee38013ebd76f802772f05 (MD5) / Approved for entry into archive by Ana Paula Grisoto (grisotoana@reitoria.unesp.br) on 2016-10-04T17:29:25Z (GMT) No. of bitstreams: 1 pizzi_mb_me_bot.pdf: 7157176 bytes, checksum: 6cac889ca8ee38013ebd76f802772f05 (MD5) / Made available in DSpace on 2016-10-04T17:29:25Z (GMT). No. of bitstreams: 1 pizzi_mb_me_bot.pdf: 7157176 bytes, checksum: 6cac889ca8ee38013ebd76f802772f05 (MD5) Previous issue date: 2016-08-09 / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) / A produtividade de plantios de eucalipto no Brasil foi triplicada nas últimas quatro décadas graças, principalmente, à pesquisa intensiva, investimentos em tecnologia silvicultural, clonagem e melhoramento genético. Atualmente, existem diversas pesquisas relacionadas ao gênero Eucalyptus, mas são poucas as que abordam o tema estresse biótico por ser uma avaliação complexa e de difícil planejamento e execução. Em Piracicaba, em um sítio experimental com alta sanidade e sobrevivência, foram induzidas uma, duas e três desfolhas sucessivas, retirando-se manualmente todas as folhas da copa das árvores de 12 clones de eucalipto de extrema relevância à silvicultura brasileira. As desfolhas ocorreram aproximadamente aos 15, 19 e 23 meses de idade das árvores, e a avaliação final de perda de produtividade ocorreu aos 27 meses. O crescimento das árvores foi monitorado semanalmente, sendo possível ver o efeito das desfolhas ao longo do período. Os clones de eucalipto escolhidos para este estudo, apesar de pertencerem ao mesmo gênero, mostraram resultados bastante diferentes. O impacto das desfolhas no crescimento das árvores foi imediato e prolongado, com o crescimento próximo à zero por 50 a 120 dias após a desfolha. As desfolhas causaram redução de crescimento em DAP (Diâmetro à Altura do Peito), altura total, volume e biomassa de madeira. As árvores não desfolhadas acabaram dominando as desfolhadas. Isso causou o estiolamento das árvores desfolhadas e a redução da homogeneidade das parcelas. Aos 27 meses, as árvores que sofreram uma desfolha apresentaram biomassa de madeira 48% inferior ao das árvores que não sofreram desfolhas (variando entre 24 e 57% para clones). Duas desfolhas sucessivas causaram redução média de 59% de biomassa (variando entre 49 e 72%) e três desfolhas sucessivas causaram perdas médias de 68% (variando entre 57 e 80%). / The Brazilian Eucalyptus productivity has tripled in the last four decades, mainly because of intensive research, development of forestry and genetics. Nowadays, there are several studies related to the Eucalyptus genus, but only a few address biotic stress, as the subject is of complex evaluation, difficult planning and execution. In Piracicaba, in an experimental site with high health and survival rate, one, two and three successive defoliations were induced, manually removing all the canopy leaves of 12 extremely relevant clones to Brazilian forestry. The defoliations occurred in approximately 15, 19 and 23 months after planting and the final evaluation of productivity occurred at 27 months. Tree growth was weekly monitored, and the effect of defoliation over time was visible. The eucalypts clones chosen for this study, despite belonging to the same genus, showed quite different results. The impact of canopy defoliation on tree growth was immediate and prolonged, with growth close to zero for 50 to 120 days following defoliation. Defoliation caused growth reduction in DBH (Diameter at Breast Height), total height, volume and wood biomass. Defoliated trees were etiolated as the non-defoliated were the dominant trees in the plot. Defoliation reduced plot homogeneity. One year after the first defoliation, the 27-month-old trees that have undergone one defoliation showed 48% lower wood biomass, in comparison with non-defoliated trees (ranging from 24 to 57% by clones). Two successive defoliations caused an average reduction of 59% of biomass (ranging from 49 to 72%) and three successive defoliations caused 68% of losses (ranging from 57 to 80%).

Cranberry (Vaccinium macrocarpon Ait.) is a woody perennial crop that can remain productive for decades. Competition for resources between cranberries and weeds can depress cranberry farm yields, resulting in large annual crop losses. Renewed interest in reducing chemical inputs into cranberry systems has provided the motivation to evaluate methods, such as flame cultivation (FC), as potential nonchemical options for weed control. Also known as thermal weeding, FC exposes plants to brief periods of high temperature that causes the water in the plant tissue to expand rapidly, rupturing plant cells and leading to necrosis. Various FC methods have been used successfully in annual crops as both a preemergence and postemergence weed control, but few scientific reports have been published on the use of FC on perennial weeds in a woody perennial crop system. Dewberry (Rubus spp.), sawbrier (Smilax glauca), and common rush (Juncus effusus) are cranberry weeds that are difficult to control, spread quickly and can cause significant crop loss. Flame cultivation may be an effective non-chemical means for controlling these weeds in cranberry systems. FC would ideally be used as a spot treatment for weeds growing in the cranberry canopy, as well as on larger non-production areas where cranberry vines are not as abundant, such as bog edges, ditches, and dikes. Using FC to treat weeds within the cranberry canopy will likely cause localized damage to cranberry plants immediately surrounding the weeds, thus cranberry response to FC is also of interest. The following experiments were designed to examine the response of weeds and cranberry plants to FC. Perennial plants rely on reserves of nonstructural carbohydrates (NSC) for growth and survival, thus the efficacy of FC treatments to weeds will likely be impacted by the timing and frequency of treatments as they relate to the specific carbohydrate cycles of targeted weeds, such as dewberry. An additional experiment studied the seasonal fluctuations of NSC in dewberry roots. Cranberry growers were also surveyed on their past experiences with FC, as well as their willingness to adopt FC if proven an effective method for controlling weeds.