Baccharis halimifolia is host to many species of insect herbivore, including myrmecophilous aphids. Previous studies with B. halimifolia have revealed strong effects of competition by an early-feeding beetle, Trirhabda bacharidis, and nitrogen enrichment. The effects of ant mutualists, however, have not been evaluated for their potential influence on interspecific interactions among insects on the host plant. I have employed a series of experiments aimed at answering the following general questions. (1) How does the density of aphid-tending ants affect common insects on the host plant? (2) What are the relative effects of (a) competition from T. bacharidis, (b) nutrient enrichment, and (c) ant presence on common insects of the host plant? (3) How do the effects of exotic ants differ from those of native ants? The density of aphid-tending ants had positive effects on myrmecophilous aphids and aphid predators. However, given a choice between tended and untended aphid populations, aphid predators preferred to forage in the absence of ants. The density of aphid-tending ants also increased predation on leaf miners although this did not necessarily translate into reduced densities of leaf miners. Competition by early-season feeding of T. bacharidis negatively affected later-feeding herbivores but the effects of competition were unaffected by nutrient enrichment. Nutrient enrichment had positive effects on some herbivores, often only in the absence of early season herbivory. Trirhabda bacharidis larvae showed evidence of nitrogen and phosphorus limitation and suffered no predation by aphid-tending ants. Ant presence increased host plant survivorship from stemborer damage in 2004. Ant species identity was an important factor determining the densities of myrmecophiles and non-myrmecophiles on the host plant in addition to affecting the responses of herbivores to increases in host plant quality. Aphids were more abundant in the presence of the exotic Linepithema humile (Hymenoptera: Dolichoderinae) versus the native Camponotus floridanus (Hymenoptera: Formicinae). Aphid predators also had higher densities in the presence of L. humile versus C. floridanus. Only L. humile acted as predator on leaf mines although predation did not always translate into reduced seasonal abundances for both species of leaf miner.

ABSTRACT EFFECTS OF RECYCLED WATER ON LANDSCAPE PLANTS Casey Ray Miranda Recycled water is water that has been previously used, has suffered a loss of quality, and has been properly treated for redistribution (Wu et al. 2001). The use of recycled water as an alternative to fresh water in the landscape can have positive and negative effects. Experimentation on 40 different plant species during a 32 week period (2 phases of 16 weeks), was conducted to analyze the effects of recycled water irrigation on the appearance of landscape plants. Each species of plant was planted into 10 individual number 2 pots and irrigated with recycled water daily. Media and water were tested for nutrients and other constituents. In phase I there were four different species of grasses and grass-like plants, five different perennials, five species of shrubs, and four annuals tested; while phase II tested four species of herbaceous perennials, eight different species of shrubs, six species of groundcovers, and four species of annuals. All tests were conducted at the Paso Robles Waste Water Treatment Plant. Of the grasses and grass like species Yucca spp. and Buchloe spp. performed best. Osteospermum fruticosum, Lavandula angustifolia, Rosmarinus officinalis, Phormium tenax, and Pennisetum setaceum had the best appearance of the herbaceous perennials tested. For the shrubs, Coprosma repens, Cistus purpureus, Dodonea viscosa, Eleagnus pungens, Baccharis pilularis, Ceanothus thysiflorus, Thuja orientalis, and Nerium oleander had the best appearance when irrigated with recycled water. The best annuals were Senecio cineraria, Antirrhinum majus, Primula spp., Viola spp., and Calendula officinalis. Of the groundcovers Heuchera spp., Lonicera japonica, Vinca major, Hedera helix, and Ceanothus griseus had the best results. From the experiment a list of tolerant and non-tolerant plants was compiled (Appendices 1 and 2). While many plants were capable of developing and growing normally, other plants were sensitive to recycled water irrigation. In order to prevent salt damage to plants and expand the use of recycled water, salt tolerance of landscape plant material must be identified (Niu et.al, 2006).

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Made available in DSpace on 2014-07-29T14:52:03Z (GMT). No. of bitstreams: 1 Tese LUCIANA DOMINGUES BITTENCOURT FERREIRA.pdf: 2409105 bytes, checksum: fbcc36a65bdb242d4cfc3db0dcffbe14 (MD5) Previous issue date: 2009-03-19 / The market of chrysanthemum has grown in recent years, mainly due to its versatility as a product, which gives color and shape varied, and affordable to many consumption patterns. But there is a need for adequacy of technical and scientific information on culture, especially depending on the opening of new producing areas in Brazil and the introduction on the market of new cultivars. The objective was evaluate the performance of three cultivars of chrysanthemum in pot grown in the Goianira - GO between the months of August and October 2007. Plant characteristics were evaluated, quality, and determined to the nutrient uptake rate of the cultivars. Worked with the cultivars White Diamond, Eugene Yellow and Durban in five phenological stages, 20, 34, 48, 62 and 76 days after the planting - DAP. Treatments were arranged in a 3x5 factorial in completely randomized design with five replications. The results found that the cultivar White Diamond presented the lowest dry matter accumulation in all plant organs analyzed. Eugene Yellow showed the highest dry matter accumulation of leaves and stems, and accumulated more in Durban and plant flowers. With respect to phenological stages, the dry matter accumulation in different organs has been growing throughout the production cycle, reaching accumulations of 6.02, 8.75 and 9.55 for g.plant-1 White Diamond, Eugene Yellow and Durban, respectively. The scale of marks for the classification standard of quality, the cultivars had values within the limits pre-established by standards. The accumulation of nutrients in various organs of the plants differed between cultivars. In cultivar White Diamond, the N, K and S are accumulated in larger quantities by inflorescences, P, Ca, Mg and Mn in leaves and Cu and Zn in the stems. The highest accumulation of nutrients in Eugene Yellow were N, K, Mg, Mn and Zn in leaves, P, Ca and Cu in stems and flowers in S. Cultivar in Durban, the largest accumulation of N, P, K, Mg and S were observed in the inflorescences, and Ca in the leaves. Demand for nutrients has been increasing throughout the production cycle with the maximum observed 76 DAP. The total accumulation of macronutrients for the cultivars showed the following order: K> N> Ca> P> Mg> S. And to cultivate White Diamond and Eugene Yellow was the sequence of micronutrientes Mn> Zn> Cu. / A comercialização de crisântemos tem crescido nos últimos anos, principalmente à sua versatilidade como produto, já que apresenta cor e formato diversificados, e ao preço acessível a vários padrões de consumo. Mas há necessidade de adequação de informações técnicas e científicas sobre a cultura, principalmente em função da abertura de novas regiões produtoras no Brasil e do lançamento constante de novas cultivares. O objetivo deste trabalho foi avaliar o comportamento de três cultivares de crisântemo em vaso cultivado no Centro-Oeste brasileiro, no município de Goianira GO, entre os meses de agosto e outubro de 2007, quanto às técnicas de cultivo e a fertilização empregada. Avaliaram-se características fitotécnicas, qualidade das plantas e acumulo de nutrientes das cultivares White Diamond, Eugene Yellow e Durban em cinco estádios fenológicos (20; 34; 48; 62 e 76 dias após o plantio). Os tratamentos foram arranjados em esquema fatorial 3x5, em delineamento inteiramente casualizado com cinco repetições. A cultivar White Diamond apresentou os menores acúmulos de matéria seca em todos os órgãos vegetais analisados. Eugene Yellow apresentou o maior acúmulo de matéria seca de folhas e hastes e, Durban acumulou mais nas inflorescências e na parte aérea total. Com relação aos estádios fenológicos, o acúmulo de matéria seca nos diferentes órgãos foi crescente durante todo o ciclo de produção, atingindo acúmulos de 6,02; 8,75 e 9,55 g.planta-1 para White Diamond, Eugene Yellow e Durban, respectivamente. Segundo a escala de notas para classificação do padrão de qualidade, as cultivares obtiveram valores dentro dos limites pré-estabelecidos pelas normas vigentes, White Diamond e Eugene Yellow obtiveram nota 4 e Durban nota 5, demonstrando que o manejo empregado na propriedade foi eficiente. A acumulação de nutrientes nos diferentes órgãos das plantas diferiram entre as cultivares. Na cultivar White Diamond, o N, K e S foram acumulados em maiores quantidades pelas inflorescências, P, Ca, Mg e Mn nas folhas e Cu e Zn nas hastes. Na Eugene Yellow foram de N, K, Mg, Mn e Zn nas folhas; P, Ca e Cu nas hastes e de S nas inflorescências. Na cultivar Durban, os maiores acúmulos de N, P, K, Mg e S foram observados na inflorescências, e Ca nas folhas. A demanda por nutrientes foi crescente durante todo o ciclo de produção com máximos observados aos 76 dias após o plantio. Os acúmulos totais dos macronutrientes na parte aérea para as cultivares apresentaram a seguinte sequência: K > N > Ca > P > Mg > S. As cultivare White Diamond e Eugene Yellow, apresentaram, ainda, a seguinte sequência para micronutrientes Mn > Zn > Cu

Reindeer appear to have strong positive effects on plant productivity and nutrient cycling in strongly nutrient-limited ecosystems. While the direct effects of grazing on vegetation composition have been intensively studied, much less is known about the indirect effect of grazing on plant-soil interactions. This thesis investigated the indirect effects of ungulate grazing on arctic plant communities via soil nutrient availability and plant nutrient uptake. At high density, the deposition of dung alone increased plant productivity both in nutrient rich and nutrient poor tundra habitats without causing major changes in soil possesses. Plant community responses to dung addition was slow, with a delay of at least some years. By contrast, a 15N-urea tracer study revealed that nutrients from reindeer urine could be rapidly incorporated into arctic plant tissues. Soil and microbial N pools only sequestered small proportions of the tracer. This thesis therefore suggests a strong effect of dung and urine on plant productivity by directly providing nutrient-rich resources, rather than by stimulating soil microbial activities, N mineralization and ultimately increasing soil nutrient availability. Further, defoliation alone did not induce compensatory growth, but resulted in plants with higher nutrient contents. This grazing-induced increase in plant quality could drive the high N cycling in arctic secondary grasslands by providing litter of a better quality to the belowground system and thus increase organic matter decomposition and enhance soil nutrient availability. Finally, a 15N natural abundance study revealed that intense reindeer grazing influences how plants are taking up their nutrients and thus decreased plant N partitioning among coexisting plant species. Taken together these results demonstrate the central role of dung and urine and grazing-induced changes in plant quality for plant productivity. Soil nutrient concentrations alone do not reveal nutrient availability for plants since reindeer have a strong influence on how plants are taking up their nutrients. This thesis highlights that both direct and indirect effects of reindeer grazing are strong determinants of tundra ecosystem functioning. Therefore, their complex influence on the aboveground and belowground linkages should be integrated in future work on tundra ecosystem N dynamic.

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[ES] ¿Cuántas veces hemos realizado o participado en una repoblación forestal y pasados los años no hemos encontrado rastro de los árboles plantados? Y en muchas ocasiones nos habremos preguntado por qué e incluso sentido frustración de creer que no lo hemos cuidado adecuadamente. La respuesta no es sencilla como veremos en este trabajo. En las últimas décadas, las repoblaciones forestales o reforestaciones, enmarcadas dentro de planes de restauración, han experimentado altas tasas de mortalidad, sobre todo en nuestro ámbito mediterráneo donde predominan las tierras secas. Esta tasa alta de mortalidad en numerosas ocasiones se relaciona con las condiciones meteorológicas, pero existen multitud de aspectos que pueden influir en alcanzar o no el objetivo final de la repoblación. Para poder conocer cuáles son los aspectos que influyen en mayor o menor medida en la supervivencia y crecimiento adecuado de las plántulas puedas en campo, se plantea la puesta en marcha de un protocolo de control holístico o integral de repoblaciones y el estudio y seguimiento de la puesta en práctica en una repoblación real durante 10 años. El control de calidad en sí mismo se ha contemplado sobre las distintas fases de la repoblación: desde la revisión de las decisiones tomadas en proyecto, pasando por la ejecución en obra, la evaluación de los lotes de planta empleados, la caracterización de sitio o estación, hasta la realización del seguimiento climatológico, ambiental y de la propia repoblación (en términos de supervivencia y crecimiento). En base a distintos planteamientos experimentales y de toma de muestras dentro de una repoblación real, en condiciones cambiantes y con sequias extremas, se ha podido estudiar pormenorizadamente la calidad de planta o stock y la idoneidad de las especies utilizadas (Pinus sp., Quercus sp., Arbutus Unedo, Juniperus phoenicea y Fraxinus ornus) para posteriormente evaluar la repoblación tras 10 años en conjunto y por tanto, los demás aspectos y sus interacciones que influyen en el establecimiento, como: la calidad de ejecución, la calidad de sitio o estación, la idoneidad del tubo protector, etc. A grandes rasgos, los resultados tanto en las parcela experimental como en la repoblación, siendo en ellas las condiciones meteorológicas las mismas, no ha sido muy satisfactoria tras los 10 años. Al margen de conocer que las sequias extremas acontecidas han tenido gran influencia e interaccionan demás factores (acrecentando los efectos negativos), se ha podido evaluar que existen especies de dudosa idoneidad para determinados sitios; que la correcta ejecución juega un papel importante; que se requiere de una mejor zonificación; y que cuidados culturales post plantación como el tubo protector, pueden influir notablemente en la consecución de la repoblación. Así, además de identificar cuáles son los aspectos más influyentes en esta repoblación en particular, se han adquirido cuestiones prácticas tanto a la hora de aplicar el control de calidad como a la hora de como plantearnos, desde la redacción del proyecto, las nuevas repoblaciones, teniendo muy en cuenta el nuevo contexto de cambio climático. / [CAT] Quantes vegades hem realitzat o participat en una repoblació forestal i passats els anys no hem trobat cap rastre dels arbres plantats? I moltes vegades ens haurem preguntat per què i fins i tot, sentit frustració de creure que els hem cuidat adequadament. La resposta no és senzilla com veurem en aquest treball. En les darreres dècades, les repoblacions forestals o reforestacions, emmarcades dins de plans de restauració, han experimentat altes taxes de mortalitat, sobretot al nostre àmbit mediterrani on predominen les zones àrides. Aquesta taxa alta de mortalitat normalment es relaciona amb les condicions meteorològiques, però hi ha multitud d'aspectes que poden influir en assolir o no l'objectiu final de la repoblació. Per poder conèixer quins són els aspectes que influeixen en major o menor mesura en la supervivència i el creixement adequat de les plàntules posades camp, es fica en marxa un protocol de control holístic o integral de repoblacions, i l'estudi i el seguiment de la posada en pràctica en una repoblació real durant 10 anys. El control de qualitat en si mateix s'ha contemplat sobre les diferents fases de la repoblació: des de la revisió de les decisions preses en projecte, passant per l'execució en l'obra, l'avaluació dels lots de planta emprats, la caracterització de lloc o estació, fins a la realització del seguiment climatològic, ambiental i de la pròpia repoblació (en termes de supervivència i creixement). En base a diferents plantejaments experimentals i de presa de mostres dins una repoblació real, en condicions canviants i amb sequeres extremes, s'ha pogut estudiar detalladament la qualitat de planta i la idoneïtat de les espècies utilitzades (Pinus sp., Quercus sp., Arbutus Unedo, Juniperus phoenicea i Fraxinus ornus) per posteriorment avaluar la repoblació després de 10 anys en conjunt i per tant, els altres aspectes i les seves interaccions que influeixen en l'establiment, com ara: la qualitat d'execució, la qualitat de lloc o estació, la idoneïtat del tub protector, etc. A grans trets, els resultats tant a les parcel·les experimentals com a la repoblació, sent en elles les condicions meteorològiques les mateixes, no ha estat gaire satisfactòria després dels 10 anys. Al marge de saber que les sequeres extremes esdevingudes han tingut gran influència i interaccionen altres factors (augmentant els efectes negatius), s'ha pogut avaluar que hi ha espècies de dubtosa idoneïtat per a determinats llocs; que la correcta execució juga un paper important; que es requereix una millor zonificació; i que els tractaments culturals postplantació com el tub protector, poden influir notablement en la consecució de la repoblació. Així, a mes a més de conèixer quins són els aspectes més influents en aquesta repoblació en particular, s'han adquirit qüestions pràctiques tant a l'hora d'aplicar el control de qualitat com a l'hora de plantejar-nos, des de la redacció del projecte, les noves repoblacions, tenint molt en compte el nou context de canvi climàtic. / [EN] How many times have we carried out or participated in a reforestation and over the years we have not found a trace of the planted trees? On many occasions, we will have wondered why and even felt frustrated to believe that we have not taken care of it properly. The answer is not simple as we will see in this work. In recent decades reforestations, framed within restoration plans, have experienced high mortality rates, especially in our Mediterranean area where drylands predominate. This high mortality rate is often related to weather conditions, but there are many aspects that can influence the final objective of the reforestation. In order to know which are the aspects that influence the survival and adequate growth of seedlings in the field, the implementation of a holistic control protocol for reforestation is proposed, as well as the study and monitoring of the put into practice in a real reforestation for 10 years. The quality control itself has been contemplated on the different phases of the reforestation: from the review of the decisions taken in the project, through the execution on site, the evaluation of the stock quality of plant used, the site characterization, until climatological, environmental and reforestation monitoring (in terms of survival and growth). Based on different experimental approaches and sampling within a real reforestation, with changing conditions and extreme droughts, it has been possible to study in detail the quality of the plant and the suitability of the species used (Pinus sp., Quercus sp., Arbutus Unedo, Juniperus phoenicea and Fraxinus ornus). Then has been evaluated the repopulation after 10 years as a whole, knowing the other aspects and their interactions that influence the establishment, such as: the quality of execution, the site quality, the suitability of shelter tube, etc. Broadly speaking, the results in the experimental plot and in the reforestation, being the same the weather conditions, have not been very satisfactory after 10 years. Apart from knowing that the extreme droughts that have occurred have had a great influence and their interactions with other factors (increasing the negative effects), it has been possible to evaluate that there are species of doubtful suitability for certain site conditions; that correct execution plays an important role; that better zoning is required; and post-planting cultural treatment, such as the protective tube, can significantly influence the establishment of reforestation. Thus, apart from identify which are the most influential aspects in this particular reforestation, practical questions have been acquired when applying quality control from the project drafting of the new reforestations taking into account the new context, the climate change. / Segura Orenga, G. (2023). Estudio del establecimiento de repoblaciones forestales en el ámbito mediterráneo mediante un análisis holístico de factores técnicos y ecológicos [Tesis doctoral]. Universitat Politècnica de València. https://doi.org/10.4995/Thesis/10251/192666