2,574 research outputs found
Crystallization of self-propelled hard-discs : a new scenario
We experimentally study the crystallization of a monolayer of vibrated discs
with a built-in polar asymmetry, a model system of active liquids, and contrast
it with that of vibrated isotropic discs. Increasing the packing fraction
, the quasi-continuous crystallization reported for isotropic discs is
replaced by a transition, or a crossover towards a "self-melting" crystal.
Increasing the packing fraction from the liquid phase, clusters of dense
hexagonally-ordered packed discs spontaneously form, melt, split and merge
leading to a highly intermittent and heterogeneous dynamics. The resulting
steady state cluster size distribution decreases monotonically. For packing
fraction larger than , a few large clusters span the system size and
the cluster size distribution becomes non monotonic, the transition being
signed by a power-law. The system is however never dynamically arrested. The
clusters permanently melt from place to place forming droplets of active liquid
which rapidly propagate across the system. This state of affair remains up to
the highest possible packing fraction questioning the stability of the crystal
for active discs, unless at ordered close packing.Comment: 4 pages, 4 figures, 1 Supp Mat
Influence de la pluviométrie sur la contamination de l'atmosphÚre et des eaux de pluie par les pesticides
Cette Ă©tude a pour objectif d'identifier les facteurs qui influencent la contamination des eaux de pluie par les produits phytosanitaires. Cinq sites contrastĂ©s ont Ă©tĂ© choisis de maniĂšre Ă ĂȘtre reprĂ©sentatifs des zones de productions lĂ©gumiĂšres ou de plein champs et Ă couvrir les diffĂ©rents modes de contamination des prĂ©cipitations. Il s'agit des sites de l'Ile de Ouessant, Landivisiau, Plouay, Ploufragan et Rennes. Les Ă©vĂšnements pluvieux collectĂ©s sont choisis en fonction des caractĂ©ristiques de formation de la perturbation et du calendrier des Ă©pandages de pesticides.Par ailleurs, les concentrations rencontrĂ©es pour le site de Rennes en 2000 (annĂ©e trĂšs humide) ont pu ĂȘtre comparĂ©es Ă celles obtenues lors d'une Ă©tude conduite en 1996 sur un site proche mais pour des conditions climatiques plus habituelles (annĂ©e humide Ă sĂšche).Les analyses sont rĂ©alisĂ©es par extraction en phase solide suivie d'une analyse en chromatographie en phase gazeuse couplĂ©e Ă la spectromĂ©trie de masse, ou par dĂ©tection azote-phosphore spĂ©cifique (NPD) ou dĂ©tection par capture d'Ă©lectrons pour les composĂ©s halogĂ©nĂ©s (ECD). Dans ces deux derniers cas, la confirmation de l'identitĂ© des produits est rĂ©alisĂ©e par un systĂšme de double colonnes.Sept Ă©vĂšnements pluvieux distincts ont Ă©tĂ© collectĂ©s et analysĂ©s entre les 15 mars et 15 juillet de l'annĂ©e 2000. Parmis les produits recherchĂ©s six molĂ©cules sont rĂ©guliĂšrement retrouvĂ©es : l'atrazine et son mĂ©tabolite la dĂ©ethylatrazine (DEA), l'alachlore, le lindane (gamma HCH) et son isomĂšre le bĂ©ta HCH ainsi que la desmĂ©thryne. Nous avions dĂ©jĂ des observations analogues Ă l'issu de nos premiĂšres investigations de 1996.Les analyses rĂ©alisĂ©es ont montrĂ© l'existence d'une contamination chronique du compartiment atmosphĂ©rique par l'atrazine et la DEA pour les zones sous influence agricole. Les niveaux de concentrations rencontrĂ©s sont faibles, de l'ordre de 10 ng/L. A ce bruit de fond s'ajoutent en pĂ©riode de traitement, des transferts depuis les parcelles traitĂ©es qui conduisent Ă des valeurs beaucoup plus Ă©levĂ©es (de 0,1 Ă 0,7 ”g.L-1). La dĂ©tection de l'alachlore et de la desmethryne est limitĂ©e aux pĂ©riodes d'application de ces produits.Du lindane, et dans un cas son isomĂšre le bĂ©ta-HCH, ont pu ĂȘtre mis en Ă©vidence sur quelques prĂ©lĂšvements, traduisant une contamination chronique du compartiment aĂ©rien due Ă la rĂ©manence de ce type de composĂ©s.Les concentrations dans les pluies, pour un site donnĂ©, sont trĂšs dĂ©pendantes de la pluviomĂ©trie. Alors qu'en annĂ©e de pluviositĂ© normale (1996), les concentrations en pĂ©riode d'application sont Ă©levĂ©es, elles restent faibles pour une annĂ©e humide (2000). Pour s'affranchir de l'effet de dilution, nous avons calculĂ© des retombĂ©es massiques (mg.ha-1) pour les deux pĂ©riodes de collecte de 1996 et 2000. Les rĂ©sultats de 2000 restent malgrĂ© cela trĂšs infĂ©rieurs Ă ceux de 1996 (d'un facteur quatre environ). Les surfaces emblavĂ©es et les diffĂ©rences d'usage entre les deux annĂ©es sont trop faibles pour expliquer les Ă©carts obtenus. Ceci nous permet de conclure que c'est l'intensitĂ© des transferts sol-air qui dĂ©termine les niveaux de contamination de l'atmosphĂšre. L'humiditĂ© Ă©levĂ©e des sols, pour une annĂ©e humide, favorise la migration verticale des produits phytosanitaires dans les couches infĂ©rieures, rĂ©duisant ainsi les concentrations de pesticides susceptibles d'ĂȘtre transfĂ©rĂ©s vers le compartiment aĂ©rien.Contamination of rainwater by pesticides was investigated by analyzing samples from 5 locations in Brittany (France). These sites were chosen on the basis of various characteristics including agricultural practices around the site, the direction of prevailing winds (west to east) and the proximity to heavily populated areas. The sites chosen were: Ile de Ouessant (a natural reserve without pesticide application), Landivisiau (a semi-natural zone), Plouay (a rural site with intensive agriculture, mainly cereals and vegetables), Ploufragan (a suburban site) and Rennes (an urban area surrounded by intensive agriculture and orchards). The pesticides to be monitored included the compounds most commonly used in Brittany. New molecules were added to this list to take into account new homologues or uses. Some organochlorines and pesticides with specific application modes were thus included in the list. Analytical techniques involved solid-liquid extraction procedures followed by GC-NPD, GC-ECD or GC-MS after prior derivatisation. Derivatisation was performed with heptafluorobutyric acid to detect urea and sulfonylurea herbicides. Quantification limits were about 5 ng/L for GC-ECD or GC-NPD, and 50 ng/L for molecules detected by GC-MS after derivatisation.Rain episodes were selected according to the prevailing meteorological conditions and the air mass trajectory. Only precipitation events greater than 6 mm were considered, in order to collect sufficient volume for analyses. Thirty-five samples (7 per location) were collected between 15 March and 15 July 2000, corresponding to various weather fronts.Six pesticides were detected: atrazine and its metabolite de-ethylatrazine (DEA), alachlor, desmethryne, lindane and its isomer (beta HCH). Among those detected most concentrations were below 100 ng/L but higher concentrations were occasionally detected during and after spraying in agricultural areas. Lindane was detected at low concentration (<10 ng/L) in several samples collected during different periods and locations. These results demonstrate chronic atmospheric contamination due to the presence of this substance even though its use has been banned in the Economic European Community (EEC) (e.g. in 1999 in France).The most frequently detected compound was atrazine, detected in 60 % of the samples. The presence of atrazine and its metabolite DEA in rainfall indicate chronic contamination of the atmosphere outside of spraying time (mid-March to mid-April). Detection of these compounds was generally limited to agricultural sites, and could also indicate transfer from agricultural areas during soil preparation for maize sowing. These hypotheses will be tested by monitoring atrazine in rainwater during a complete agricultural cycle. Important contamination by atrazine was detected during spraying time at agricultural locations, where concentrations ranged from 10 to 60 ng/L. Detection of alachlor was limited to application periods and rural sites, at levels ranging from 20 to 240 ng/L. However, amounts of alachlor were also detected in Ouessant, even though its use is banned on this isle. This presence was presumably due to the specific conditions of formation of the weather fronts that resulted in rainfall.Concentrations of pesticides in rainwater obtained in 2000 were generally lower than those described in literature or in a previous study done in Brittany. Alachlor and atrazine concentrations were compared to those of a previous study conducted in Brittany in 1996. The two sites chosen were Rennes in 2000 and Le Rheu in 1996. These two locations, separated by 5 km, were not significantly different since Rennes is directly downwind of Le Rheu. Pluviometry was very important in the year 2000, showing a 30 % increase in rainfall compared to the average from 1961-1990. The concentrations of pesticides in both years were also very different. During a year of normal rainfall (e.g., 1996) concentrations of pesticides in application periods were high, but they remained low during wet years (e.g., 2000). These differences could not be explained by a dilution effect - when fall-out was calculated (mg/ha) to correct for the dilution effect, the differences remained important. Maize surfaces (132 000 ha in 1996 compared to 128 000 ha in 2000) and the quantities of pesticides applied (580 tonnes in 1994 in Brittany compared to 350 tonnes for atrazine, and 263 tonnes in 1998 compared to 119 tonnes in 1994 for alachlor) were too similar to explain the differences observed in 1998. Photodegradation processes, which are more important during normal or dry years, should also favour higher concentrations in 2000 than in 1996. Rain concentrations and fallout observed in 2000 remained lower than those obtained in 1996. Thus, it can be concluded that atmospheric contamination is lower for wet years (e.g., 2000) than for normal or dry years (e.g., 1996). Soil humidity, high for wet years, favours the vertical migration of these substances to lower soil layers, reducing pesticide concentrations available to be transferred to the atmosphere
Functional Microbial Features Driving Community Assembly During Seed Germination and Emergence
Microbial interactions occurring on and around seeds are especially important for plant fitness since seed-borne microorganisms are the initial source of inoculum for the plant microbiota. In this study, we analyze structural and functional changes occurring within the plant microbiota at these early stages of the plant cycle, namely germination and emergence. To this purpose, we performed shotgun DNA sequencing of microbial assemblages associated to seeds, germinating seeds and seedlings of two plant species: bean and radish. We observed an enrichment of and during emergence and a set of functional traits linked to copiotrophy that could be responsible for this selection as a result of an increase of nutrient availability after germination. Representative bacterial isolates of taxa that are selected in seedlings showed indeed faster bacterial growth rate in comparison to seed-associated bacteria isolates. Finally, binning of metagenomics contigs results in the reconstruction of population genomes of the major bacterial taxa associated to the samples. Together, our results demonstrate that, although seed microbiota varied across plant species, nutrient availability during germination elicits changes of the composition of microbial communities by potentially selecting microbial groups with functional traits linked to copiotrophy. The data presented here represents the first attempts to empirically assess changes in the microbial community during plant emergence and moves us toward a more holistic understanding of the plant microbiome
Thin film transistors fabricated by in-situ doped unhydrogenated polysilicon films obtained by solid phase crystallization
International audienceHigh mobility low temperature (†600°C) unhydrogenated in-situ doped polysilicon thin film transistors are made. Polysilicon layers are grown by a LPCVD technique and crystallized in vacuum by a thermal annealing. Source and drain regions are in-situ doped. Gate insulator is made of an APCVD silicon dioxide. Hydrogen passivation is not performed on the transistors. One type of transistors is made of two polysilicon layers, the other one is constituted of a single polysilicon layer. The electrical properties are better for transistors made of single polysilicon layer: a low threshold voltage (1.2 V), a subthreshold slope S = 0.7 V/dec, a high field effect mobility (â 100 cm2/Vs) and a On/Off state current ratio higher than 107 for a drain voltage Vds = 1 V. At low drain voltage, for both transistors, the Off state current results from a pure thermal emission of trapped carriers. However, at high drain voltage, the electrical behavior is different: in the case of single polysilicon TFTs, the current obeys the field-assisted (Poole-Frenkel) thermal emission model of trapped carriers while for TFTs made of two polysilicon layers, the higher Off state current results from a field-enhanced thermal emission
Differences in resource use lead to coexistence of seed-transmitted microbial populations
Seeds are involved in the vertical transmission of microorganisms in plants and act as reservoirs for the plant microbiome. They could serve as carriers of pathogens, making the study of microbial interactions on seeds important in the emergence of plant diseases. We studied the influence of biological disturbances caused by seed transmission of two phytopathogenic agents, Alternaria brassicicola Abra43 (Abra43) and Xanthomonas campestris pv. campestris 8004 (Xcc8004), on the structure and function of radish seed microbial assemblages, as well as the nutritional overlap between Xcc8004 and the seed microbiome, to find seed microbial residents capable of outcompeting this pathogen. According to taxonomic and functional inference performed on metagenomics reads, no shift in structure and function of the seed microbiome was observed following Abra43 and Xcc8004 transmission. This lack of impact derives from a limited overlap in nutritional resources between Xcc8004 and the major bacterial populations of radish seeds. However, two native seed-associated bacterial strains belonging to Stenotrophomonas rhizophila displayed a high overlap with Xcc8004 regarding the use of resources; they might therefore limit its transmission. The strategy we used may serve as a foundation for the selection of seed indigenous bacterial strains that could limit seed transmission of pathogens
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