Contribution à l’étude de la thérophytisation des matorrals des versants sud des monts de Tlemcen (Algérie occidentale)

La zone sur laquelle porte notre contribution est localisée dans le Nord-Ouest Algérien. Cette étude est consacrée à l’analyse de la diversité biologique et la dynamique des formations végétales des matorrals des versants sud des monts de Tlemcen. L’utilisation de la méthode aire-espèce de Braun Blanquet nous a permis de dégager une liste de 149 espèces à partir de 150 relevés fl oristiques effectués sur l’ensemble des stations d’étude. 4,69 % des espèces appartiennent aux for mations forestières et pré-forestières, avec une hauteur n’excédant pas 2 mètres; 13,42 % aux matorrals et 81,87 % aux pelouses. La conjugaison des facteurs de dégradation a entrainé une perturbation des écosystèmes locaux accompagnée d’une régression des aires de répartition de nombreux taxons. Deux facteurs majeurs peuvent être évoqués : – amplifi cation de l’impact humain lié à l’utilisation anarchique des écosystèmes (défrichement; coupe; surpâturages; bois de chauffe), – péjorations climatiques. L’analyse statistique des spectres biologiques nous a permis de mettre en évidence les modifications de la flore le long d’un gradient dynamique: forêt – pré forêt – matorral – pelouse. Plus des 3/4 des espèces recensées dans la zone d’étude appartiennent aux thérophytes et aux hemicryptophytes.

Optimizing the number of stations in arrays measurements: experimental outcomes for different array geometries and the f-k method

Array measurements have become a valuable tool for site response characterization in a non-invasive way. The array design, i.e. size, geometry and number of stations, has a great influence in the quality of the obtained results. From the previous parameters, the number of available stations uses to be the main limitation for the field experiments, because of the economical and logistical constraints that it involves. Sometimes, from the initially planned array layout, carefully designed before the fieldwork campaign, one or more stations do not work properly, modifying the prearranged geometry. Whereas other times, there is not possible to set up the desired array layout, because of the lack of stations. Therefore, for a planned array layout, the number of operative stations and their arrangement in the array become a crucial point in the acquisition stage and subsequently in the dispersion curve estimation. In this paper we carry out an experimental work to analyze which is the minimum number of stations that would provide reliable dispersion curves for three prearranged array configurations (triangular, circular with central station and polygonal geometries). For the optimization study, we analyze together the theoretical array responses and the experimental dispersion curves obtained through the f-k method. In the case of the f-k method, we compare the dispersion curves obtained for the original or prearranged arrays with the ones obtained for the modified arrays, i.e. the dispersion curves obtained when a certain number of stations n is removed, each time, from the original layout of X geophones. The comparison is evaluated by means of a misfit function, which helps us to determine how constrained are the studied geometries by stations removing and which station or combination of stations affect more to the array capability when they are not available. All this information might be crucial to improve future array designs, determining when it is possible to optimize the number of arranged stations without losing the reliability of the obtained results.

Impacts on particles and ozone by transport processes recorded at urban and high-altitude monitoring stations

In order to evaluate the influence of particle transport episodes on particle number concentration temporal trends at both urban and high-altitude (Aitana peak-1558 m a.s.l.) stations, a simultaneous sampling campaign from October 2011 to September 2012 was performed. The monitoring stations are located in southeastern Spain, close to the Mediterranean coast. The annual average value of particle concentration obtained in the larger accumulation mode (size range 0.25–1 μm) at the mountain site, 55.0 ± 3.0 cm− 3, was practically half that of the value obtained at the urban station (112.0 ± 4.0 cm− 3). The largest difference between both stations was recorded during December 2011 and January 2012, when particles at the mountain station registered the lowest values. It was observed that during urban stagnant episodes, particle transport from urban sites to the mountain station could take place under specific atmospheric conditions. During these transports, the major particle transfer is produced in the 0.5–2 μm size range. The minimum difference between stations was recorded in summer, particularly in July 2012, which is most likely due to several particle transport events that affected only the mountain station. The particle concentration in the coarse mode was very similar at both monitoring sites, with the biggest difference being recorded during the summer months, 0.4 ± 0.1 cm− 3 at the urban site and 0.9 ± 0.1 cm− 3 at the Aitana peak in August 2012. Saharan dust outbreaks were the main factor responsible for these values during summer time. The regional station was affected more by these outbreaks, recording values of > 4.0 cm− 3, than the urban site. This long-range particle transport from the Sahara desert also had an effect upon O3 levels measured at the mountain station. During periods affected by Saharan dust outbreaks, ozone levels underwent a significant decrease (3–17%) with respect to its mean value.