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At least 19 recordsLinked to original sources

Joint action of elevated ambient nitrite and nitrate on hemolymph nitrogenous compounds and nitrogen excretion of tiger shrimp Penaeus monodon.

Penaeus monodon (12.13+/-1.14 g) exposed individually to six different nitrite and nitrate regimes (0.002, 0.36 and 1.46 mM nitrite combined with 0.005 and 7.32 mM nitrate), at a salinity of 25 ppt, were examined for hemolymph nitrogenous compounds and whole shrimp's nitrogen excretions after 24 h. Nitrogen excretion increased directly with ambient nitrite and nitrate. Hemolymph nitrite, nitrate, urea and uric acid levels increased, while hemolymph ammonia, oxyhemocyanin and protein were inversely related to ambient nitrite. Exposure of P. monodon to elevated nitrite in the presence of 7.32 mM nitrate did not alter hemolymph nitrite, ammonia, uric acid, oxyhemocyanin and protein levels, but caused an increase in hemolymph nitrate and a decrease in hemolymph urea as compared to exposure to elevated nitrite only. Following exposure to elevated nitrite, nitrite was oxidized to nitrate and P. monodon showed uricogenesis and uricolysis. The shrimp also used strategies to avoid joint toxicities of nitrite and metabolic ammonia by removing ammonia or reducing ammonia production under the stress of elevated nitrite.

Ammonia↗

Splanchnic metabolism of nitrogenous compounds and urinary nitrogen excretion in steers fed alfalfa under conditions of increased absorption of ammonia and L-arginine supply across the portal-drained viscera.

Effects of increased ammonia and/or arginine absorption across the portal-drained viscera (PDV) on net splanchnic (PDV and liver) metabolism of nitrogenous compounds and urinary N excretion were investigated in six catheterized Hereford x Angus steers (501 +/- 1 kg BW) fed a 75% alfalfa:25% (as-fed basis) corn-soybean meal diet (0.523 MJ of ME/[kg BW(0.75).d]) every 2 h without (27.0 g of N/kg of dietary DM) and with 20 g of urea/kg of dietary DM (35.7 g of N/kg of dietary DM) in a split-plot design. Net splanchnic flux measurements were obtained immediately before beginning and ending a 72-h mesenteric vein infusion of L-arginine (15 mmol/h). For 3 d before and during arginine infusion, daily urine voided was measured and analyzed for N composition. Feeding urea increased PDV absorption (P < 0.01) and hepatic removal (P < 0.01) of ammonia N, accounting for 80% of increased hepatic urea N output (P < 0.01). Numerical increases in net hepatic removal of AA N could account for the remaining portion of increased hepatic urea N output. Arginine infusion increased hepatic arginine removal (P < 0.01) and hepatic urea N output (P < 0.03) and switched hepatic ornithine flux from net uptake to net output (P < 0.01), but numerical changes in net hepatic removal of ammonia and AA N could not account fully for the increase in hepatic urea N output. Increases in urine N excretion equaled quantities of N fed as urea or infused as arginine. Estimated salivary urea N excretion was not changed by either treatment. Urea cycle regulation occurs via a complex interaction of mechanisms and requires N sources other than ammonia, but the effect of increased ammonia absorption on hepatic catabolism of individual AA in the present study was not significant.

Amino Acids↗

Homopolyatomic Nitrogen Compounds.

New nitrogen compounds with high energy density are getting closer, now that Christe et al. have achieved the synthesis of the N(5)(+) ion. Here the current experimental and theoretical knowledge is presented. According to calculations molecules containing the pentazole unit are the most promising.

Journal Article↗

Stimulation of the activity of horseradish peroxidase by nitrogenous compounds.

A variety of nitrogenous compounds broaden the activity versus pH profile for the peroxidation of dianisidine catalyzed by horseradish peroxidase (HRP), but not by myeloperoxidase, chloroperoxidase, Escherichia coli hydroperoxidase I, methemoglobin, or microperoxidases. The peroxidation of dianisidine catalyzed by cytochrome c peroxidase was affected by the nitrogenous compounds, but to a lesser extent than was the action of HRP. The peroxidations of a variety of phenols by HRP exhibited broad activity versus pH profiles and were unaffected by the nitrogenous compounds. The energy of activation for the peroxidation of dianisidine by HRP was unaffected by changes of pH in the range 6.5-8.5 and was unchanged by the presence of the nitrogenous compounds. The nitrogenous compounds markedly increased Vm for the peroxidation of dianisidine by HRP, but did not change the slope of Lineweaver-Burk plots of kinetic data. These results are accommodated by a mechanism in which nitrogenous compounds hydrogen-bond to the distal histidine of HRP and in so doing raise its pK alpha. Since the acid form of the distal histidine is thought to facilitate peroxidations catalyzed by HRP by hydrogen bonding to the ferryl oxygen of compound II, raising its pK alpha broadens the activity versus pH profile for the peroxidation of anilino substrates, such as dianisidine. We propose that phenolic substrates hydrogen-bond directly to the ferryl oxygen, thus displacing the distal histidine and eliminating the possibility of being influenced by nitrogenous compounds.

Amines↗

Membrane rejection of nitrogen compounds.

Rejection characteristics of nitrogen compounds were examined for reverse osmosis, nanofiltration, and low-pressure reverse osmosis membranes. The rejection of nitrogen compounds is explained by integrating experimental results with calculations using the extended Nernst-Planck model coupled with a steric hindrance model. The molecular weight and chemical structure of nitrogen compounds appear to be less important in determining rejection than electrostatic properties. The rejection is greatest when the Donnan potential exceeds 0.05 V or when the ratio of the solute radius to the pore radius is greater than 0.8. The transport of solute in the pore is dominated by diffusion, although convective transport is significant for organic nitrogen compounds. Electromigration contributes negligibly to the overall solute transport in the membrane. Urea, a small organic compound, has lower rejection than ionic compounds such as ammonium, nitrate, and nitrite, indicating the critical role of electrostatic interaction in rejection. This suggests that better treatment efficiency for organic nitrogen compounds can be obtained after ammonification of urea.

Membranes, Artificial↗

[Presence of nitrogen compounds in well water].

INTRODUCTION: Nitrogen compounds in drinking waters have been related to groundwater contamination and inadequate sanitary conditions. Nitrite and nitrate are etiologic agents of methemoglobinemia. In acid solution, nitrous acid formed from nitrite can react with secondary amines to form carcinogenic nitrosamines. The survey of ammoniacal and albuminoid nitrogen, nitrite and nitrate in groundwater supplies as regards the extent of the contamination they cause and discussion of the drinking water regulation regarding nitrogen compounds. MATERIAL AND METHOD: Samples collected predominantly in the Metropolitan Region of S. Paulo City was analysed for nitrogen compounds using colorimetric methods: N-NH3 and N-albuminoid by the Nessler method, nitrite by diazoted sulfanilamide with N-(1-naphthyl)-ethylenediamine, and nitrate by reaction with phenoldisuplhonic acid. RESULTS: Federal and S. Paulo State drinking water regulations, respectively, Portaria 36/90 and Decreto n degree 12.486, were applied to interpret the results obtained. Of the 607 samples analysed. 15% of them had at least one of the concentrations of nitrogen compounds exceeding the maximum contaminant level (MCL) of the S. Paulo State Regulation. Otherwise, as regards the Federal Regulation, only 4% of the samples exceeded the MCL requirement for nitrate. CONCLUSION: In federal drinking water regulation only MCL for nitrate is reported. Otherwise, S. Paulo State regulation requirements report MCLs for all the compounds that have been analysed in this work. The observed results showed that concentrations of ammonia and albuminoid nitrogen, and nitrite, as well as nitrate, gave rise to water of inadequate quality, further they may have adverse effects on human health. The inclusion of nitrogen compounds other than nitrate in federal regulation is recommended.

Ammonia↗