Le Grand-Tunis présente une vulnérabilité face à la pollution atmosphérique compte tenu des fortes densités de population et des nombreuses infrastructures caractérisant son territoire. L’ozone (O3) et les particules en suspension (PM10) dépassent fréquemment les normes tunisiennes relatives à ces polluants. Quant aux normes internationales fixées par l’OMS (Organisation Mondiale de la Santé), elles n’ont été respectées que rarement. L’appareil respiratoire constitue une voie d’exposition privilégiée aux agressions en rapport avec l’environnement. De nombreuses pathologies pulmonaires sont directement liées à l’inhalation des polluants dans l’atmosphère. Les influences des mécanismes climatiques sur la santé respiratoire sont très étendues également, notamment les épisodes météorologiques extrêmes appelés aussi paroxysmes météorologiques.L’objectif principal de cette thèse est de caractériser l’impact des facteurs environnementaux, climat et polluants atmosphériques sur la santé respiratoire dans le Grand-Tunis. Nous avons choisi de quantifier cette relation à partir des indicateurs biométéorologiques et des seuils absolus de stress météorologique, spécifiques au climat tunisois, et de la qualité de l’air pour prévoir des épisodes à risque pour la santé respiratoire. Cela est fait à partir des extrêmes météorologiques des paramètres les plus irritants pour la santé respiratoire : la température, l’humidité relative de l’air et la vitesse maximale du vent. Nous avons aussi établi des normes réalistes pour la qualité de l’air, relatives à l’O3 et aux PM10, identifiant les seuils critiques de surplus des hospitalisations dans le Grand-Tunis et qui peuvent être appliquées dans tout le pays. Compte tenu de l’effet de certains paramètres climatiques sur la dispersion des polluants dans l’atmosphère, nous avons aussi étudié la relation entre les paramètres météorologiques et les polluants d’O3 et de PM10. Les résultats de cette étude révèlent que, durant toute l’année, les tunisois sont confrontés au moins à un risque environnemental : la pollution photochimique et les vagues de chaleur, très répandues durant la saison chaude ; durant la saison froide, c’est le risque du froid et de la pollution particulaire ; et pendant les intersaisons, c’est la pollution biologique, avec les pollens, qui est le risque le plus important. Toutefois, l’exposition à court terme à ces risques, sur l’aggravation de la maladie respiratoire ou l’irritation du système respiratoire sont bien réelles. Cette recherche montre que le développement et l’aggravation des maladies respiratoires semblent découler d’une interaction complexe entre divers facteurs individuels et environnementaux. Ils sont essentiellement en relation avec le temps, la qualité de l’air et l’atopie. L’importance de ces facteurs varie selon la maladie considérée. Par ailleurs, le faible niveau socioéconomique de la famille augmente la probabilité d’être exposé à plusieurs de ces facteurs de risque. À cela s’ajoutent les facteurs comportementaux tels que l’alcool, le tabagisme actif et passif. / The Greater metropolitan area of Tunis, often referred to as Grand Tunis or Tunis, presents a vulnerability to air pollution due to the high concentrations of population and the infrastructures characterizing its territory. Ozone (O3) and particles (PM10) often exceed the Tunisian thresholds for these pollutants. As for the international standards set by the WHO (world health organization), they have not been met infrequently.The respiratory tract is a preferred route of exposure to aggressions related to the environment. Many lung diseases are directly linked to inhalation of pollutants in the atmosphere. The influences of climate mechanisms on respiratory health are also very extensive, including extreme weather events, also called weather paroxysms.The main objective of this thesis was to characterize the impact of environmental factors, climate and atmospheric pollutants on respiratory health in Grand Tunis. We have chosen to quantify this relationship from the biometeorological indicators and absolute thresholds of meteorological stress, specific Tunisian climate, and air quality to predict episodes at risk for respiratory health and thresholds of weather variables and air quality resulting in excess hospital admissions for respiratory causes. And this from the climate extremes of the parameters affecting the respiratory health : temperature, relative humidity and maximum wind speed. We, too, set realistic standards for air quality, relative to O3 and PM10, identifying critical thresholds excess hospitalizations in Grand Tunis and can be applied throughout the country. Given the effect of some climatic parameters on the dispersion of pollutants in the atmosphere, we also studied the relationship between climatic parameters and pollutants of O3 and PM10. The results of this study reveal that, throughout the year, Tunisians are confronted with at least an environmental risk : photochemical pollution and heat waves, which are very responsive during the hot season ; during the cold season, it is the risk of cold and particulate pollution; and during the off-season, biological pollution, together with pollen, is more at risk. However, short-term exposure to these risks, the worsening of the respiratory illness or irritation of the respiratory system is real. This study showed that the development and worsening of respiratory diseases appear to result from a complex interplay of individual and environmental factors. They are mainly in relation to time, air quality and atopy. The importance of these factors varies the respective disease. Moreover, the low socioeconomic status of the family increases the likelihood of being exposed to more of these risk factors. Added to this are behavioral factors such as alcohol, active and passive smoking.

Tendo em vista a importância de se conhecer as exigências climáticas da videira nas condições de cultivo, o objetivo deste trabalho foi determinar os índices biometeorológicos: graus-dia (GD), índice biometeorológico de Primault (IB), índice heliotérmico de Huglin (IH) e índice heliotérmico de Geslin (IHG) para a cultivar Niagara Rosada podada em diferentes épocas e fases do ciclo vegetativo. A poda seca foi realizada no final do inverno (fase de mobilização de reservas) e a poda verde foi realizada no verão (fase de acúmulo de reservas). O delineamento experimental utilizado foi o de blocos ao acaso, constituídos os tratamentos de 9 datas de poda: 20/07, 04/08, 19/08, 03/09, 18/09, 01/02, 15/02, 02/03 e 16/03 em dois anos agrícolas (2005/2006 e 2006/2007). A parcela experimental foi composta de 12 plantas sendo duas bordaduras (dez plantas úteis) com treze anos de idade, no espaçamento de 2,0 m x 1,0 m, conduzidas no sistema de espaldeira sob irrigação. As variáveis analisadas foram os períodos e subperíodos, em dias, poda-colheita, brotação-colheita, podabrotação, brotação-florescimento, florescimento-"veraison" e "veraison"-colheita. Para a análise de variância dos índices biometeorológicos foi utilizado o teste de Tukey para comparar as médias das datas de poda, duas a duas, e o teste F para contrastes ortogonais comparando a média da poda seca versus poda verde. Na análise do índice GD e IH verificou-se que plantas podadas em épocas distintas apresentaram valores diferentes para completar o período poda-colheita. Para IB e IHG verificou-se a mesma tendência em plantas podadas em épocas distintas, apresentando valores diferentes para completar o período brotação-colheita. Os subperíodos que não diferiram estatisticamente entre as épocas de poda foram respectivamente: florescimento- "veraison" para o IB e brotação-florescimento para o IH e IHG. Os demais subperíodos apresentaram diferenças pelo teste F para contraste ortogonal para as épocas de poda. / The goal of this work was to determine four biometeorological indexes: degreedays (DD), Primault's biometeorological index (BI), Huglin's heliothermal index (HI) and Geslin's heliothermal index (GHI) for grape 'Niagara Rosada' (Vitis labrusca L.) pruned at different seasons and physiological phases. The dry pruning was done at the end of winter (carbohydrate mobilization phase) and green pruning (carbohydrate stock phase) was done during summer. The experiment was carried out in a randomized block design consisting of 9 treatments, pruning dates 20th July, 04th August, 19th August, 03rd September, 18th September, 01st February, 15th February, 02nd March and 16th March during two years (2005/2006 and 2006/2007). Twelve plants were used as experimental plot, being two border plants. The grapevine was 13 years old grown under trellis system with a 2.0 x 1.0 meter spacing under irrigation. The grape phenology was evaluated considering numbers of days for each one of the following period and sub-periods: pruning - harvest, sprout - harvest, pruning - sprout, sprout - flowering, flowering - early ripening and early ripening - harvest. To analyze those indexes, the Tukey test was used comparing pruning dates and F test for orthogonal contrast comparing plants pruned at different seasons (dry pruning versus green pruning). It was observed that plants pruned at different seasons do not require the same amount of energy to complete pruning - harvest period when using DD and HI. The same tendency was observed when using BI and GHI for those plants to complete its period sprout - harvest. Some sub-periods that did not differ statistically between dry pruning and green pruning: flowering - early ripening for BI and sprout - flowering for HI and GHI. Other sub-periods differ statistically when using F test for orthogonal contrast.

Tendo em vista a importância de se conhecer as exigências climáticas da videira nas condições de cultivo, o objetivo deste trabalho foi determinar os índices biometeorológicos: graus-dia (GD), índice biometeorológico de Primault (IB), índice heliotérmico de Huglin (IH) e índice heliotérmico de Geslin (IHG) para a cultivar Niagara Rosada podada em diferentes épocas e fases do ciclo vegetativo. A poda seca foi realizada no final do inverno (fase de mobilização de reservas) e a poda verde foi realizada no verão (fase de acúmulo de reservas). O delineamento experimental utilizado foi o de blocos ao acaso, constituídos os tratamentos de 9 datas de poda: 20/07, 04/08, 19/08, 03/09, 18/09, 01/02, 15/02, 02/03 e 16/03 em dois anos agrícolas (2005/2006 e 2006/2007). A parcela experimental foi composta de 12 plantas sendo duas bordaduras (dez plantas úteis) com treze anos de idade, no espaçamento de 2,0 m x 1,0 m, conduzidas no sistema de espaldeira sob irrigação. As variáveis analisadas foram os períodos e subperíodos, em dias, poda-colheita, brotação-colheita, podabrotação, brotação-florescimento, florescimento-"veraison" e "veraison"-colheita. Para a análise de variância dos índices biometeorológicos foi utilizado o teste de Tukey para comparar as médias das datas de poda, duas a duas, e o teste F para contrastes ortogonais comparando a média da poda seca versus poda verde. Na análise do índice GD e IH verificou-se que plantas podadas em épocas distintas apresentaram valores diferentes para completar o período poda-colheita. Para IB e IHG verificou-se a mesma tendência em plantas podadas em épocas distintas, apresentando valores diferentes para completar o período brotação-colheita. Os subperíodos que não diferiram estatisticamente entre as épocas de poda foram respectivamente: florescimento- "veraison" para o IB e brotação-florescimento para o IH e IHG. Os demais subperíodos apresentaram diferenças pelo teste F para contraste ortogonal para as épocas de poda. / The goal of this work was to determine four biometeorological indexes: degreedays (DD), Primault's biometeorological index (BI), Huglin's heliothermal index (HI) and Geslin's heliothermal index (GHI) for grape 'Niagara Rosada' (Vitis labrusca L.) pruned at different seasons and physiological phases. The dry pruning was done at the end of winter (carbohydrate mobilization phase) and green pruning (carbohydrate stock phase) was done during summer. The experiment was carried out in a randomized block design consisting of 9 treatments, pruning dates 20th July, 04th August, 19th August, 03rd September, 18th September, 01st February, 15th February, 02nd March and 16th March during two years (2005/2006 and 2006/2007). Twelve plants were used as experimental plot, being two border plants. The grapevine was 13 years old grown under trellis system with a 2.0 x 1.0 meter spacing under irrigation. The grape phenology was evaluated considering numbers of days for each one of the following period and sub-periods: pruning - harvest, sprout - harvest, pruning - sprout, sprout - flowering, flowering - early ripening and early ripening - harvest. To analyze those indexes, the Tukey test was used comparing pruning dates and F test for orthogonal contrast comparing plants pruned at different seasons (dry pruning versus green pruning). It was observed that plants pruned at different seasons do not require the same amount of energy to complete pruning - harvest period when using DD and HI. The same tendency was observed when using BI and GHI for those plants to complete its period sprout - harvest. Some sub-periods that did not differ statistically between dry pruning and green pruning: flowering - early ripening for BI and sprout - flowering for HI and GHI. Other sub-periods differ statistically when using F test for orthogonal contrast.