Compromisos en la adaptación a distintos huéspedes en virus de plantas

Los patógenos han desarrollado estrategias para sobrevivir en su entorno, infectar a sus huéspedes, multiplicarse dentro de estos y posteriormente transmitirse a otros huéspedes. Todos estos componentes hacen parte de la eficacia biológica de los patógenos, y les permiten ser los causantes de enfermedades infecciosas tanto en hombres y animales, como en plantas. El proceso de infección produce efectos negativos en la eficacia biológica del huésped y la gravedad de los efectos, dependerá de la virulencia del patógeno. Por su parte, el huésped ha desarrollado mecanismos de respuesta en contra del patógeno, tales como la resistencia, por la que reduce la multiplicación del patógeno, o la tolerancia, por la que disminuye el efecto negativo de la infección. Estas respuestas del huésped a la infección producen efectos negativos en la eficacia biológica del patógeno, actuando como una presión selectiva sobre su población. Si la presión selectiva sobre el patógeno varía según el huésped, se predice que un mismo patógeno no podrá aumentar su eficacia biológica en distintos huéspedes y estará más adaptado a un huésped y menos a otro, disminuyendo su gama de huéspedes. Esto supone que la adaptación de un patógeno a distintos huéspedes estará a menudo dificultada por compromisos (trade-off) en diferentes componentes de la eficacia biológica del patógeno. Hasta el momento, la evidencia de compromisos de la adaptación del patógeno a distintos huéspedes no es muy abundante, en lo que se respecta a los virus de plantas. En las últimas décadas, se ha descrito un aumento en la incidencia de virus nuevos o previamente descritos que producen enfermedades infecciosas con mayor gravedad y/o diferente patogenicidad, como la infección de huéspedes previamente resistentes. Esto se conoce como la emergencia de enfermedades infecciosas y está causada por patógenos emergentes, que proceden de un huésped reservorio donde se encuentran adaptados. Los huéspedes que actúan como reservorios pueden ser plantas silvestres, que a menudo presentan pocos síntomas o muy leves a pesar de estar infectados con diferentes virus, y asimismo se encuentran en ecosistemas con ninguna o poca intervención humana. El estudio de los factores ecológicos y biológicos que actúan en el proceso de la emergencia de enfermedades infecciosas, ayudará a entender sus causas para crear estrategias de prevención y control. Los virus son los principales patógenos causales de la emergencia de enfermedades infecciosas en humanos, animales y plantas y un buen modelo para entender los procesos de la emergencia. Asimismo, las plantas a diferencia de los animales, son huéspedes fáciles de manipular y los virus que las afectan, más seguros para el trabajo en laboratorio que los virus de humanos y animales, otros modelos también usados en la investigación. Por lo tanto, la interacción virus – planta es un buen modelo experimental para el estudio de la emergencia de enfermedades infecciosas. El estudio de la emergencia de virus en plantas tiene también un interés particular, debido a que los virus pueden ocasionar pérdidas económicas en los cultivos agrícolas y poner en riesgo la durabilidad de la resistencia de plantas mejoradas, lo que supone un riesgo en la seguridad alimentaria con impactos importantes en la sociedad, comparables con las enfermedades infecciosas de humanos y animales domésticos. Para que un virus se convierta en un patógeno emergente debe primero saltar desde su huésped reservorio a un nuevo huésped, segundo adaptarse al nuevo huésped hasta que la infección dentro de la población de éste se vuelva independiente del reservorio y finalmente debe cambiar su epidemiología. En este estudio, se escogió la emergencia del virus del mosaico del pepino dulce (PepMV) en el tomate, como modelo experimental para estudiar la emergencia de un virus en una nueva especie de huésped, así como las infecciones de distintos genotipos del virus del moteado atenuado del pimiento (PMMoV) en pimiento, para estudiar la emergencia de un virus que aumenta su patogenicidad en un huésped previamente resistente. El estudio de ambos patosistemas nos permitió ampliar el conocimiento sobre los factores ecológicos y evolutivos en las dos primeras fases de la emergencia de enfermedades virales en plantas. El PepMV es un patógeno emergente en cultivos de tomate (Solanum lycopersicum) a nivel mundial, que se describió primero en 1980 infectando pepino dulce (Solanum muricatum L.) en Perú, y casi una década después causando una epidemia en cultivos de tomate en Holanda. La introducción a Europa posiblemente fue a través de semillas infectadas de tomate procedentes de Perú, y desde entonces se han descrito nuevos aislados que se agrupan en cuatro cepas (EU, LP, CH2, US1) que infectan a tomate. Sin embargo, el proceso de su emergencia desde pepino dulce hasta tomate es un interrogante de gran interés, porque es uno de los virus emergentes más recientes y de gran importancia económica. Para la emergencia de PepMV en tomate, se recolectaron muestras de tomate silvestre procedentes del sur de Perú, se analizó la presencia y diversidad de aislados de PepMV y se caracterizaron tanto biológicamente (gama de huéspedes), como genéticamente (secuencias genomicas). Se han descrito en diferentes regiones del mundo aislados de PMMoV que han adquirido la capacidad de infectar variedades previamente resistentes de pimiento (Capsicum spp), es decir, un típico caso de emergencia de virus que implica la ampliación de su gama de huéspedes y un aumento de patogenicidad. Esto tiene gran interés, ya que compromete el uso de variedades resistentes obtenidas por mejora genética, que es la forma de control de virus más eficaz que existe. Para estudiar la emergencia de genotipos altamente patogénicos de PMMoV, se analizaron clones biológicos de PMMoV procedentes de aislados de campo cuya patogenicidad era conocida (P1,2) y por mutagénesis se les aumentó la patogenicidad (P1,2,3 y P1,2,3,4), introduciendo las mutaciones descritas como responsables de estos fenotipos. Se analizó si el aumento de la patogenicidad conlleva un compromiso en la eficacia biológica de los genotipos de PMMoV. Para ello se evaluaron diferentes componentes de la eficacia biológica del virus en diferentes huéspedes con distintos alelos de resistencia. Los resultados de esta tesis demuestran: i). El potencial de las plantas silvestres como reservorios de virus emergentes, en este caso tomates silvestres del sur de Perú, así como la existencia en estas plantas de aislados de PepMV de una nueva cepa no descrita que llamamos PES. ii) El aumento de la gama de huéspedes no es una condición estricta para la emergencia de los virus de plantas. iii) La adaptación es el mecanismo más probable en la emergencia de PepMV en tomate cultivado. iv) El aumento de la patogenicidad tiene un efecto pleiotrópico en distintos componentes de la eficacia biológica, así mismo el signo y magnitud de este efecto dependerá del genotipo del virus, del huésped y de la interacción de estos factores. ABSTRACT host Pathogens have evolved strategies to survive in their environment, infecting their hosts, multiplying inside them and being transmitted to other hosts. All of these components form part of the pathogen fitness, and allow them to be the cause of infectious diseases in humans, animals, and plants. The infection process produces negative effects on the host fitness and the effects severity will depend on the pathogen virulence. On the other hand, hosts have developed response mechanisms against pathogens such as resistance, which reduces the growth of pathogens, or tolerance, which decreases the negative effects of infection. T he se responses of s to infection cause negative effects on the pathogen fitness, acting as a selective pressure on its population. If the selective pressures on pathogens va ry according to the host s , probably one pathogen cannot increase its fitness in different hosts and will be more adapted to one host and less to another, decreasing its host range. This means that the adaptation of one pathogen to different hosts , will be often limited by different trade - off components of biological effectiveness of pathogen. Nowadays , trade - off evidence of pathogen adaptation to different hosts is not extensive, in relation with plant viruses. In last decades, an increase in the incidence of new or previously detected viruses has been described, causing infectious diseases with increased severity and/or different pathogenicity, such as the hosts infection previously resistants. This is known as the emergence of infectious diseases and is caused by emerging pathogens that come from a reservoir host where they are adapted. The hosts which act as reservoirs can be wild plants, that often have few symptoms or very mild , despite of being infected with different viruses, and being found in ecosystems with little or any human intervention. The study of ecological and biological factors , acting in the process of the infectious diseases emergence will help to understand its causes to create strategies for its prevention and control. Viruses are the main causative pathogens of the infectious diseases emergence in humans, animals and plants, and a good model to understand the emergency processes. Likewise, plants in contrast to animals are easy host to handle and viruses that affect them, safer for laboratory work than viruses of humans and animals, another models used in research. Therefore, the interaction plant-virus is a good experimental model for the study of the infectious diseases emergence. The study of virus emergence in plants also has a particular interest, because the viruses can cause economic losses in agricultural crops and threaten the resistance durability of improved plants, it suppose a risk for food security with significant impacts on society, comparable with infectious diseases of humans and domestic animals. To become an emerging pathogen, a virus must jump first from its reservoir host to a new host, then adapt to a new host until the infection within the population becomes independent from the reservoir, and finally must change its epidemiology. In this study, the emergence of pepino mosaic virus (PepMV) in tomato, was selected as experimental model to study the emergence of a virus in a new host specie, as well as the infections of different genotypes of pepper mild mottle virus (PMMoV) in pepper, to study the emergence of a virus that increases its pathogenicity in a previously resistant host. The study of both Pathosystems increased our knowledge about the ecological and evolutionary factors in the two first phases of the emergence of viral diseases in plants. The PepMV is an emerging pathogen in tomato (Solanum lycopersicum L.) in the world, which was first described in 1980 by infecting pepino (Solanum muricatum L.) in Peru, and almost after a decade caused an epidemic in tomato crops in Netherlands. The introduction to Europe was possibly through infected tomato seeds from Peru, and from then have been described new isolates that are grouped in four strains (EU, LP, CH2, US1) that infect tomato. However, the process of its emergence from pepino up tomato is a very interesting question, because it is one of the newest emerging viruses and economically important. For the PepMV emergence in tomato, wild tomato samples from southern Peru were collected, and the presence and diversity of PepMV isolates were analyzed and characterized at biological (host range) and genetics (genomic sequences) levels. Isolates from PMMoV have been described in different world regions which have acquired the ability to infect pepper varieties that were previously resistants (Capsicum spp), it means, a typical case of virus emergence which involves the host range extension and an increased pathogenicity. This is of great interest due to involve the use of resistant varieties obtained by breeding, which is the most effective way to control virus. To study the emergence of highly pathogenic genotypes of PMMoV, biological clones from field isolates whose pathogenicity was known were analyzed (P1,2) and by mutagenesis we increased its pathogenicity (P1,2,3 and P1,2, 3,4), introducing the mutations described as responsible for these phenotypes. We analyzed whether the increased pathogenicity involves a trade-off in fitness of PMMoV genotypes. For this aim, different components of virus fitness in different hosts with several resistance alleles were evaluated. The results of this thesis show: i). The potential of wild plants as reservoirs of emerging viruses, in this case wild tomatoes in southern Peru, and the existence in these plants of PepMV isolates of a new undescribed strain that we call PES. ii) The host range expansion is not a strict condition for the plant virus emergence. iii) The adaptation is the most likely mechanism in the PepMV emergence in cultivated tomato. iv) The increased pathogenicity has a pleiotropic effect on several fitness components, besides the sign and magnitude of this effect depends on the virus genotype, the host and the interaction of both.

Ozone depletion and UVB radiation: Impact on plant DNA damage in southern South America

The primary motivation behind the considerable effort in studying stratospheric ozone depletion is the potential for biological consequences of increased solar UVB (280–315 nm) radiation. Yet, direct links between ozone depletion and biological impacts have been established only for organisms of Antarctic waters under the influence of the ozone “hole;” no direct evidence exists that ozone-related variations in UVB affect ecosystems of temperate latitudes. Indeed, calculations based on laboratory studies with plants suggest that the biological impact of ozone depletion (measured by the formation of cyclobutane pyrimidine dimers in DNA) is likely to be less marked than previously thought, because UVA quanta (315–400 nm) may also cause significant damage, and UVA is unaffected by ozone depletion. Herein, we show that the temperate ecosystems of southern South America have been subjected to increasingly high levels of ozone depletion during the last decade. We found that in the spring of 1997, despite frequent cloud cover, the passages of the ozone hole over Tierra del Fuego (55° S) caused concomitant increases in solar UV and that the enhanced ground-level UV led to significant increases in DNA damage in the native plant Gunnera magellanica. The fluctuations in solar UV explained a large proportion of the variation in DNA damage (up to 68%), particularly when the solar UV was weighted for biological effectiveness according to action spectra that assume a sharp decline in quantum efficiency with increasing wavelength from the UVB into the UVA regions of the spectrum.

When Can Oral Health Education Begin? Relative effectiveness of three oral health education strategies starting pre-partum

Objective: To test the impact of oral health education provided to pregnant mothers on subsequent practices within the infant’s family. Research design: A quasi-experimental intervention trial comparing the effectiveness of ‘usual care’ to one, or both, of two oral health education resources: a ‘sample bag’ of information and oral health care products; and/or a nine-minute “Healthy Teeth for Life” video on postnatal oral health issues. Participants: Women attending the midwife clinic at approximately 30 weeks gestation were recruited (n=611) in a public hospital providing free maternity services. Results and Conclusions: Four months after the birth of their infant, relative to the usual care condition, each of the oral health education interventions had independent or combined positive impacts on mother’s knowledge of oral health practices. However young, single, health care card-holder or unemployed mothers were less likely to apply healthy behaviours or to improve knowledge of healthy choices, as a result of these interventions. The video intervention provided the strongest and most consistent positive impact on mothers’ general and infant oral health knowledge. While mothers indicated that the later stage of pregnancy was a good time to receive oral health education, many suggested that this should also be provided after birth at a time when teeth were a priority issue, such as when “baby teeth” start to erupt.

Stop and revive? The effectiveness of nap and active rest breaks for reducing driver sleepiness

Objectives The purpose for this study was to determine the relative benefit of nap and active rest breaks for reducing driver sleepiness. Methods Participants were 20 healthy young adults (20-25 years), including 8 males and 12 females. A counterbalanced within-subjects design was used such that each participant completed both conditions on separate occasions, a week apart. The effects of the countermeasures were evaluated by established physiological (EEG theta and alpha absolute power), subjective (Karolinska Sleepiness Scale), and driving performance measures (Hazard Perception Task). Participants woke at 5am, and undertook a simulated driving task for two hours; each participant then had either a 15-minute nap opportunity or a 15-minute active rest break that included 10 minutes of brisk walking, followed by another hour of simulated driving. Results The nap break reduced EEG theta and alpha absolute power and eventually reduced subjective sleepiness levels. In contrast, the active rest break did not reduce EEG theta and alpha absolute power levels with the power levels eventually increasing. An immediate reduction of subjective sleepiness was observed, with subjective sleepiness increasing during the final hour of simulated driving. No difference was found between the two breaks for hazard perception performance. Conclusions Only the nap break produced a significant reduction in physiological sleepiness. The immediate reductions of subjective sleepiness following the active rest break could leave drivers with erroneous perceptions of their sleepiness, particularly as physiological sleepiness continued to increase after the break.

Temporal variation in arthropod sampling effectiveness: The case for using the beat sheet method in cotton

Predatory insects and spiders are key elements of integrated pest management (IPM) programmes in agricultural crops such as cotton. Management decisions in IPM programmes should to be based on a reliable and efficient method for counting both predators and pests. Knowledge of the temporal constraints that influence sampling is required because arthropod abundance estimates are likely to vary over a growing season and within a day. Few studies have adequately quantified this effect using the beat sheet, a potentially important sampling method. We compared the commonly used methods of suction and visual sampling to the beat sheet, with reference to an absolute cage clamp method for determining the abundance of various arthropod taxa over 5 weeks. There were significantly more entomophagous arthropods recorded using the beat sheet and cage clamp methods than by using suction or visual sampling, and these differences were more pronounced as the plants grew. In a second trial, relative estimates of entomophagous and phytophagous arthropod abundance were made using beat sheet samples collected over a day. Beat sheet estimates of the abundance of only eight of the 43 taxa examined were found to vary significantly over a day. Beat sheet sampling is recommended in further studies of arthropod abundance in cotton, but researchers and pest management advisors should bear in mind the time of season and time of day effects.

Review of approaches to evaluate the effectiveness of weed biological control agents

We review key issues, available approaches and analyses to encourage and assist practitioners to develop sound plans to evaluate the effectiveness of weed biological control agents at various phases throughout a program. Assessing the effectiveness of prospective agents before release assists the selection process, while post-release evaluation aims to determine the extent that agents are alleviating the ecological, social and economic impacts of the weeds. Information gathered on weed impacts prior to the initiation of a biological control program is necessary to provide baseline data and devise performance targets against which the program can subsequently be evaluated. Detailed data on weed populations, associated plant communities and, in some instances ecosystem processes collected at representative sites in the introduced range several years before the release of agents can be compared with similar data collected later to assess agent effectiveness. Laboratory, glasshouse and field studies are typically used to assess agent effectiveness. While some approaches used for field studies may be influenced by confounding factors, manipulative experiments where agents are excluded (or included) using chemicals or cages are more robust but time-consuming and expensive to implement. Demographic modeling and benefit–cost analyses are increasingly being used to complement other studies. There is an obvious need for more investment in long-term post-release evaluation of agent effectiveness to rigorously document outcomes of biological control programs.

Relative host plant species use by the lantana biological control agent Aconophora compressa (Membracidae) across its native and introduced ranges

Aconophora compressa Walker (Hemiptera: Membracidae) was released in 1995 against the weed lantana in Australia, and is now found on multiple host plant species. The intensity and regularity at which A. compressa uses different host species was quantified in its introduced Australian range and also its native Mexican range. In Australia, host plants fell into three statistically defined categories, as indicated by the relative rates and intensities at which they were used in the field. Fiddlewood (Citharexylum spinosum L.: Verbenaceae) was used much more regularly and at higher densities than any other host sampled, and alone made up the first group. The second group, lantana (Lantana camara L.: Verbenaceae; pink variety) and geisha girl (Duranta erecta L.: Verbenaceae), were used less regularly and at much lower densities than fiddlewood. The third group, Sheena’s gold (another variety of D. erecta), jacaranda (Jacaranda mimosifolia D. Don: Bignoniaceae) and myoporum (Myoporum acuminatum R. Br.: Myoporaceae), were used infrequently and at even lower densities. In Mexico, the insect was found at relatively low densities on all hosts relative to those in Australia. Densities were highest on L. urticifolia, D. erecta and Tecoma stans (L.) Juss. ex Kunth (Bignoniaceae), which were used at similar rates to one another. It was found also on a few other verbenaceous and non-verbenaceous host species but at even lower densities. The relative rate at which Citharexylum spp. and L. urticifolia were used could not be assessed in Mexico because A. compressa was found on only one plant of each species in areas where these host species co-occurred. The low rate at which A. compressa occurred on fiddlewood in Mexico is likely to be an artefact of the short-term nature of the surveys or differences in the suites of Citharexylum and Lantana species available there. These results provide further incentive to insist on structured and quantified surveys of non-target host use in the native range of potential biological control agents prior to host testing studies in quarantine.

Study of the relative effectiveness of extension methods in educating fisherwomen

Three experimental groups from three different fishing villages were selected and administered with three extension treatments on two messages, namely, production of fish wafers and fish pickles. There was a significant knowledge gain in the subjects taught through different extension methods. It was observed that lecture aided with slides induced maximum knowledge followed by lecture aided with charts and lecture alone. Among all, the young and highly educated women gained maximum knowledge.

A global assessment of the effectiveness of different protection levels in marine protected areas of tropical waters, following a new categorization

Dissertação de mestrado, Biologia Marinha, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

Variations in the Work and Lives of Teachers: Relative and Relational Effectiveness

The VITAE project is a four‐year (2001–2005) research study, commissioned by the Department for Education and Skills, conducted with 300 teachers in 100 schools in seven local education authorities in England. The project aimed to identify factors that may affect their work and lives over time and how these factors may, in turn, impact on their teaching and subsequent pupil progress and outcomes. It combined quantitative and qualitative methods of data collection and analysis in order to define and examine notions of teachers' relational and relative effectiveness. The first part of the paper addresses the nature of effectiveness and three key themes relating to the changing contexts of teachers' work, lives and effectiveness: the challenge of reform to notions of professionalism; professional identities; changes in teachers' work and lives. The research design and early findings and their effects upon the development of the research form the second part. The final part of the paper discusses three sets of understandings which are fundamental to any consideration of teachers' work, lives and effectiveness: relative and relational effectiveness; teacher identities; teachers' life and work contexts. The research suggests that policy‐makers, school leaders and teachers themselves need to attend to these if teacher recruitment, retention and standards are to improve.