This study aimed to test this assumption in soil-based systems. In a short (24 h) incubation experiment, soils were treated with artificially (18)O

and (15)N enriched NO(3)(-). Production of Vorinostat purchase NO(3)(-) from nitrification during the incubation would affect both the (18)O and the (15)N enrichment. Oxygen exchange could therefore be studied by examining the change in (18)O relative to the (15)N. In two out of the three soils, we found that the imposed (18)O enrichment of the NO(3)(-) declined relatively more than the imposed (15)N-NO(3)(-) enrichment. This implies that O exchange indeed affected the O isotopic signature of NOT, which has important implications for NO(3)(-) source determination studies. We suggest that O exchange between NO(3)(-) and H(2)O

should be taken into consideration when interpreting the O isotopic signature to study the origin and fate of NO(3)(-) in ecosystems. (C) 2011 Elsevier Ltd. All rights reserved.”
“Sheppard, S.C., Bittman, S. and Tait, J. 2009. Monthly NH3 emissions from poultry in 12 Ecoregions of Canada. Can J. Anim. Sci. 89: 21 35. Management of ammonia (NH3) is a multi-faceted issue for farmers. It is simultaneously a toxicant that can affect farm-worker and find more animal health, volatile plant nutrient that is expensive to replace if lost, and a potential contributor to environmental degradation. The environmental implications have important spatial and temporal dimensions, beyond the farm. This paper describes a model development to estimate NH3 emissions from poultry (broiler, layer and turkey) production in 2780

mapping units across Canada on a monthly see more time scale. It includes estimates of daily emission peaks within critical months. The results will contribute to estimates of haze and atmospheric aerosol production, as well as contriubutions to other potential impacts such as eutrophication of sensitive ecosystems. The model is based on a detailed survey of farm practices. Emissions vary strongly throughout the year, and in many regions there are peak emissions in early spring and late fall, associated with landspreading of manure. There are also markedly different nitrogen excretion rates among regions, and these and bird populations are the key factors controlling emissions. On average, 22% of excreted uric acid or ammoniacal N is emitted from barns, 2% from storage and 26% from landspreading, resulting in a total loss of 50%.”
“The standardization of surgical techniques supplemented with appropriate neoadjuvant chemoradiation has led to the decline in local recurrence rates of rectal cancer (LRRC) from 25-50% to 5-10%. The outcomes reported for surgical intervention in LRRC is encouraging, however, a number of controversies exist especially in the ultra-advanced and palliative setting.