Results of the Generalized Linear Model (binomial) of annual presence for six mosquito species (<i>Cx</i>. <i>theileri</i> is not analysed) vs hydroperiod and NDVI estimated at five buffers of different size.

<p>NDVI² is the quadratic effect of NDVI.</p

Results of the GLM binomial analysis of the influence of Hydroperiod and NDVI on annual mosquito presences in the five different buffers.

<p>Results of the GLM binomial analysis of the influence of Hydroperiod and NDVI on annual mosquito presences in the five different buffers.</p

Map of the study area with an ortophotograph of the area.

<p>Ecological units are described in Material and Methods. Urban areas correspond to the villages situated at the border of the study area. White circles indicate the locations of the traps.</p

Results of the Generalized Linear Model (binomial) of monthly mosquito presence for seven mosquito species vs Inundation surface and NDVI estimated at five buffers of different size.

<p>Results of the Generalized Linear Model (binomial) of monthly mosquito presence for seven mosquito species vs Inundation surface and NDVI estimated at five buffers of different size.</p

Relationships between Shannon diversity Index and monthly NDVI, and between monthly mosquito abundance and inundation area.

<p>Relationships between Shannon diversity Index and monthly NDVI, and between monthly mosquito abundance and inundation area.</p

Number of female mosquitoes captured in each ecological unit.

<p>Number of female mosquitoes captured in each ecological unit.</p

Relationships among annual hydroperiod, NDVI, <i>Cx</i>.<i>theileri</i>, <i>Cx</i>. <i>pipiens</i>, <i>Cx</i>.<i>modestus</i>, <i>Cx</i>.<i>perexiguus</i> and <i>Oc</i>.<i>caspius</i> annual abundances.

<p>Relationships among annual hydroperiod, NDVI, <i>Cx</i>.<i>theileri</i>, <i>Cx</i>. <i>pipiens</i>, <i>Cx</i>.<i>modestus</i>, <i>Cx</i>.<i>perexiguus</i> and <i>Oc</i>.<i>caspius</i> annual abundances.</p

Monthly number of captures of the different mosquito species from March to November 2010 in the different ecological units studied.

<p><i>Cx</i>. <i>theileri</i> was more abundant in marshland, but also in other landscape units. <i>Cx</i>. <i>perexiguus</i> was more abundant in ricefields, scrubland and other landscapes. <i>Cx</i>. <i>modestus</i> was more abundant in marshland and in June. <i>Cx</i>.<i>pipiens</i> was abundant in marshland, sand dunes and scrubland, <i>Oc</i>. <i>caspius</i> was abundant in all landscapes, while <i>Oc</i>. <i>detritus</i> was significantly more abundant in halophytic marshes of sand dunes and fish ponds.</p

Structural and Photophysical Study on Alkynyl Cyclometalated Pt₂Pb₂ and Pt₂Pb Clusters

Neutralization reactions of (NBu₄)­[Pt­(bzq)­(CCR)₂] (bzq = 7,8-benzoquinolinyl) with [Pb­(HBpz₃)]­Cl (pz = pyrazolyl) afford tetranuclear neutral Pt₂Pb₂ derivatives [{Pt­(bzq)­(CCR)₂}­{Pb­(HBpz₃)}]₂ (R = Ph, <b>1</b>; C₆H₄OMe-3, <b>2</b>) or the anionic trinuclear Pt₂Pb cluster (NBu₄)­[{Pt­(bzq)­(CCC₆H₄CF₃-4)₂}₂­{Pb­(HBpz₃)}], <b>3</b>, stabilized by Pt–Pb and Pb^II···η²-(CCR) bonding interactions in the solid state, as confirmed by X-ray crystallography. The variable-temperature ¹H NMR spectra of <b>3</b> confirm the existence of a dynamic equilibrium that averages the “Pt­(bzq)­(CCC₆H₄CF₃-4)₂” groups in solution. 1D ¹H PGSE-NMR, 2D DOSY, and ¹H variable-temperature NMR experiments for the tetranuclear clusters <b>1</b> and <b>2</b> indicate that in solution these dimers generate mainly binuclear [{Pt­(bzq)­(CCR)₂}­{Pb­(HBpz₃)}] units by cleavage of the Pb^II···η²-(CCR) interactions. All clusters exhibit phosphorescent emission in rigid media (solid, glasses) and <b>3</b> also in CH₂Cl₂ solution. The emission maxima of <b>1</b> and <b>2</b> are slightly blue-shifted in relation to the precursors, being assigned to a mixed ³MLCT/³LC (L = bzq) excited state, perturbed by the Pt–Pb bond. However, the emission maximum of <b>3</b> coincides with that of its precursor, indicating little or no involvement of the Pt–Pb bonds in the emissive state

Spatial interpolation by kriging of annual mosquito abundances of: total female mosquitoes (a), <i>Cx</i>. <i>theileri</i> (b), <i>Cx</i>. <i>pipiens</i> (c), <i>Cx</i>. <i>perexiguus</i> (d), <i>Cx</i>. <i>modestus</i> (e), <i>Oc</i>. <i>caspius</i> (f), <i>Oc</i>. <i>detritus</i> (g), and <i>An</i>. <i>atroparvus</i> (h) with an ortophotograph of the area.

<p>Spatial interpolation by kriging of annual mosquito abundances of: total female mosquitoes (a), <i>Cx</i>. <i>theileri</i> (b), <i>Cx</i>. <i>pipiens</i> (c), <i>Cx</i>. <i>perexiguus</i> (d), <i>Cx</i>. <i>modestus</i> (e), <i>Oc</i>. <i>caspius</i> (f), <i>Oc</i>. <i>detritus</i> (g), and <i>An</i>. <i>atroparvus</i> (h) with an ortophotograph of the area.</p