Challenges in quantifying biosphere-atmosphere exchange of nitrogen species

Recent research in nitrogen exchange with the atmosphere has separated research communities according to N form. The integrated perspective needed to quantify the net effect of N on greenhouse-gas balance is being addressed by the NitroEurope Integrated Project (NEU). Recent advances have depended on improved methodologies, while ongoing challenges include gas-aerosol interactions, organic nitrogen and N(2) fluxes. The NEU strategy applies a 3-tier Flux Network together with a Manipulation Network of global-change experiments, linked by common protocols to facilitate model application. Substantial progress has been made in modelling N fluxes, especially for N(2)O, NO and bi-directional NH(3) exchange. Landscape analysis represents an emerging challenge to address the spatial interactions between farms, fields, ecosystems, catchments and air dispersion/deposition. European up-scaling of N fluxes is highly uncertain and a key priority is for better data on agricultural practices. Finally, attention is needed to develop N flux verification procedures to assess compliance with international protocols.     

Lethal and sublethal effects of the natural and healthy spinosad-based formulation Tracer™ on tadpoles of two neotropical species

Environmental Science and Pollution Research - This paper presents the first acute toxicity data of the natural insecticide spinosad in amphibians. The sensitivity of two neotropical sympatric...     

Transcriptional activation of plant defence genes by short-term air pollutant stress

The expression of defence genes was monitored by RNA blot analyses in tobacco plants (Nicotiana tabacum cv. SR-1) treated with various air pollutants at realistic concentrations that prevail in urban areas. Six-week-old plants responded with an increase in the steady-state mRNA levels of phenylalanine ammonia-lyase (PAL), chalcone synthase (CHS), chitinase and beta-1,3-glucanase, when exposed to defined and subnecrotic concentrations of automobile exhaust and/or ozone over a period of 48 h. An enhanced expression of genes encoding mitochondrial and cytosolic superoxide dismutases suggested that air pollutants induced considerable oxidative stress. Moreover, wounding or elicitor treatment of plants already exposed to automobile exhaust and/or ozone additionally increased the expression of the above defence genes, but not so in NO(2). Since the main difference between NO(2) and exhaust gas is the absence of the hydrocarbon compounds in the former, we regard hydrocarbons as favourite candidates for the toxic effect of exhaust gas, and they possibly act by generating an enhanced oxidative stress.