Le nitrite est un intermédiaire de nombreuses voies du cycle de l’azote, mais est toxique pour la plupart des formes de vies aquatiques. Sa toxicité agit au niveau cellulaire pour les microorganismes, et au niveau de la respiration pour les organismes plus complexes. Il est généralement supposé que ce composé est éliminé rapidement dans l’environnement, et que les microorganismes responsables de son élimination sont efficaces. Cependant les concentrations de nitrite dépassent la norme européenne (1 µM) dans la Seine entre Paris et l’estuaire. Le nitrite est apporté dans la Seine en aval de Paris par les stations d’épuration (STEP), malgré l’ajout de traitements d’élimination de l’azote (nitrification et dénitrification). En plus de leur contenu chimique et organique, les eaux de sorties de STEP contiennent des microorganismes qui peuvent coloniser l’environnement en aval. Dans la colonne d’eau, les mesures de cinétique de nitrification ont montré que les oxydant du nitrite avaient une activité potentielle plus élevée que les oxydant de l’ammonium. De plus, la quantification des microorganismes nitrifiants par qPCR a montré que les oxydants du nitrite (Nitrobacter dans la Seine et Nitrospira dans les rejets de STEP) étaient plus abondants que les oxydants de l’ammonium. Malgré cela, les taux in situ d’oxydation du nitrite étaient similaires aux taux in situ d’oxydation de l’ammonium dans la Seine, bien qu’ils augmentent e tous deux en aval de la STEP. Cet équilibre entre production du nitrite (oxydation de l’ammonium) et élimination du nitrite (oxydation du nitrite) résulte en une très lente élimination du nitrite dans la colonne d’eau. Les hypothèses pouvant expliquer la faible efficacité de l’oxydation du nitrite seraient une inhibition des microorganismes oxydants le nitrite par des polluants présents en Seine, ou le basculement de leur métabolisme vers un comportement mixotrophe de ces oxydants du nitrite. En plus de l’impact significatif sur la concentration du nitrite dans la colonne d’eau, il a été observé un fort impact des STEP sur la composition et la distribution des microorganismes présents dans le sédiment. Les communautés microbiennes du sédiment étaient fortement modifiées par les rejets de STEP, et étaient fortement colonisés par les bactéries du genre Nitrospira. L’étude du sédiment a montré que ce compartiment de la Seine était une source de nitrite pour la colonne d’eau, bien que les taux étaient très faibles par rapport aux concentrations dans la Seine. Le nitrite était produit en conditions anoxiques en amont de la STEP (3-4 cm), mais en surface en aval de la STEP (0-1 cm). En conséquence, le sédiment parait plus sensible à l’influence de la STEP que la colonne d’eau. Dans son ensemble, le cycle de l’azote semble avoir un impact limité sur la dynamique du nitrite dans la Seine, dans la mesure où ses différentes étapes sont équilibrées. Il pourrait donc être supposé que la pollution en nitrite de la Seine est suffisamment peut importante pour ne pas déstabiliser le cycle de l’azote dans la Seine d’une façon mesurable. / Nitrite is an intermediate in many microbial pathways of the nitrogen cycle, but is also toxic for most form of aquatic life. It is toxic at a cellular level for microorganisms, and for the respiration of complex organisms. In general the elimination of this compound is assumed to be fast in the environment, and the microorganisms responsible efficient. In the Seine River however, nitrite concentrations exceed the European norm of 1 µM between Paris and the estuary. The nitrite is released in the Seine River downstream of Paris by the waste water treatment plants (WWTP) despite the addition of nitrogen removal treatments (nitrification and denitrification). In addition to its content chemical compounds and organic matter, the WWTP outlets also contain microorganisms which can colonize the environment downstream. In the water column, measurements of nitrification kinetics showed that nitrite oxidizers had a higher potential activity than ammonia oxidizers. Quantification of nitrifiers by qPCR showed that nitrite oxidizers, Nitrobacter in the environment and Nitrospira in the WWTP outlets were more abundant than ammonia oxidizers. Despite these facts, in situ nitrite oxidation rates were similar to ammonia oxidation rates in the Seine River, even if both were higher downstream of the WWTP. This balance between nitrite production (ammonia oxidation) and elimination (nitrite oxidation) results in a very slow elimination of nitrite in the water column. This led to hypothesize that low nitrite oxidizing’s efficiency was caused by either inhibition by pollutants in the Seine River, or use a mixotrophic metabolism by nitrite oxidizers. In addition to the significant impact on nitrite concentration in the water column, the WWTP were shown to have a significant impact on the composition and distribution of the microorganisms present in the sediment. The microbial communities of the sediment were shown to be highly modified by the WWTP outlets, and were heavily colonized by the Nitrospira genera. The study of the sediment showed that this compartment of the Seine River was a source of nitrite for the water column, even though the rates of production were not significant in relation to the concentrations of nitrite. The nitrite was produced in the anoxic zone upstream of the WWTP (3-4 cm) when it was produced near the surface downstream of the WWTP (0-1 cm). As a consequence, the sediment appears to be more sensitive to the impact of the WWTP than the water column. As a whole the nitrogen cycle in the Seine River was observed to have a very limited impact on the nitrite concentration in the Seine River as its different steps are balanced. This could be viewed as the fact that this nitrite pollution is low enough to not unbalance the nitrogen cycle of the Seine River in a measurable way.

A research program was developed to investigate basic and applied aspects of toxicity, both lethal and sublethal, of hemoxidants, particularly nitrite, on fish, non-fish aquatic vertebrates, and crayfish. The major objectives of this research were to determine A) acute and sublethal toxicity of nitrite to selected aquatic organisms: 1. aquatic salamander larvae, Ambystoma texanum, 2. swamp crayfish, Procambarus simulans, 3. bluegill, Lepomis macrochirus, 4. bullfrog, tadpoles, Rana catesbiana, 5. channel catfish, Ictalurus punctatus, B) the influence of environmental chloride on acute and sublethal exposures to hemoxidants: 1. on acute nitrite toxicity to salamander larvae, crayfish, and bluegill, 2. on nitrite-induced methemoglobinemia in bullfrog tadpoles, Rana catesbian, C) the effect of environmental hydrogen ion concentrations (pH) on acute nitrite toxicity 1. to the crayfish, Procambarus simulans, 2. to the bluegill, Lepomis macrochirus, D) the effect of temperature in sublethal exposures to nitrite 1. methemoglobin formation in channel catfish exposed at different acclimation temperatures, 2. recovery from methemoglobinemia at different acclimation temperatures, E) the effect of the fish anesthetic TMS-222 on nitrite-induced methemoglobinemia in channel catfish 1. supression of nitrite-induced methemoglobinemia, 2. dose-response curve for TMS-222 induced methemoglobinemia, and F) if a methemoglobin reductase system is present in channel catfish.

Nitrification, a key step in biological nitrogen removal processes, is the oxidation of ammonia into nitrate performed by ammonia oxidizing bacteria (AOB) and nitrite oxidizing bacteria (NOB) under aerobic condition. Researchers have focused on factors affecting the performance of nitrification for decades, but the inorganic carbon limitation on nitrification had been neglected. However, the increase in nitrogen in wastewater has increased the need to evaluate and improve our understanding of this limitation. In a previous research, the hypothesis that different inorganic carbon concentrations would enrich different AOB populations has been examined. In this study, the focus was on the effect of inorganic carbon concentration on NOB, which has a close relationship with AOB. Two 5L lab–scale continuous–flow stirred tank reactors (CSTR) were operated to evaluate the nitrification performance and microbial ecology of nitrifier populations acclimated under inorganic carbon sufficient (high–IC) and limited (low–IC) conditions for approximately 700 days. During the operation period, both bioreactors were able to maintain satisfactory nitrification efficiency higher than 95% at an influent ammonium concentration of 250 mg–N/L. Nitrate was the major end product and no significant nitrite accumulation was observed. To evaluate the effects of inorganic carbon on NOB community structures, cloning/sequencing and real–time PCR were applied to target and quantify the two common NOB genera, Nitrospira and Nitrobacter, as no molecular probe targeting all known NOB is available presently. The results showed that these two genera were both found in the two reactors. Nitrospira was the dominant NOB population in the high–IC bioreactor, while Nitrobacter was dominant in the low–IC one after one year acclimation. Kinetic analysis revealed that NOB enriched in the two reactors have different kinetic performances. However, IC concentration did not show a significant impact on the nitrite oxidizing kinetics of NOB in the batch tests.

Cardiovascular disease (CVD) such as hypertension and stroke are serious illnesses that impact on the lives of millions all over the world, with 972 million (26% of the world’s population) suffering from hypertension in year 2000, and an estimated 1.56 billion to be affected by 2025. Hypertension, being one of the most common CVD is associated with the development of stroke, peripheral vascular diseases, myocardial infarction, renal failure as well as cardiac failure. Several studies have shown a seasonal correlation for both the systolic and diastolic blood pressure in mankind. A hypertension trial done by the Medical Research Council in the 1980s showed the average blood pressure being lower in summer than winter, and this difference was more significant in the elderly than the younger population. Other than seasonal variation, blood pressure (including hypertension prevalence) is also noted to correlate with latitude, being higher at places further away from the equator. Other cardiovascular related diseases such as stroke and acute coronary syndrome are also shown occur more frequently in winter. The morbidity and mortality of CVD could be due to various factors including diet, culture, race and social status, but within the United Kingdom, all cause mortality (with cerebral-vascular disease being the major one) correlates with latitude even after accounting for all known risk factors, with CVD risks highest in the north. We propose that this difference in cardiovascular mortality is caused by variations in ultraviolet exposure other than temperature. Known mechanisms of sunlight exposure that affect cardiovascular health include temperature and the ultraviolet B (UVB) mediated photolysis of 7-dehydrocholesterol in the skin to produce 1,25 dihydroxycholecalciferol (Vitamin D). UVB is however a potent skin carcinogen, and calculating risk-benefit ratios for exposure will be important. We believe that independently of vitamin D, nitric oxide plays an important role in blood pressure regulation and cardiovascular health, accounting for seasonal and latitude variation. In 1961, Furchgott demonstrated relaxation of rabbit aorta by irradiating them with ultraviolet light, and in later research he noted this effect is most significant in the ultraviolet A (UVA) spectrum. Recently, Mowbray showed a rich store of various nitro-species within human skin and Oplander showed a reduction of blood pressure in human after giving whole body UVA irradiation. We therefore hypothesize that independently of vitamin D, NO mediates the UVA induced beneficial effects on cardiovascular health. To support our hypothesis, in vivo as well as in vitro studies were conducted. We recruited a total of 63 healthy volunteers and monitored blood pressure, forearm blood flow as well as other cardiovascular parameters before and after UVA irradiation. Blood samples were also taken for the measurement of circulatory nitro-species. We have noted a significant reduction of blood pressure (from 84.5±1.76 to 81.33±1.37 mmHg) and increased forearm blood flow (1.95±0.28 to 2.94±0.47 mL/100mL of tissue/min) after UVA irradiation of human skin; simultaneously, we also noted a rise in circulatory nitrite (0.5±0.04 μM before irradiation to 0.72±0.04 μM) and a drop in circulatory nitrate (11.79±0.64 μM before irradiation and 8.99±0.4 μM). For us to further clarify the role of nitric oxide in different latitude, a monochromator machine that generates specific wavelength of light was been used to irradiate aqueous nitrite solution, and the total amount of nitric oxide release at different latitude was then calculated according to the irradiance of various wavelength across the globe. The results of our studies provide evidence suggesting that nitric oxide release induced by UVA irradiation of the skin can account for the difference in cardiovascular mortality and morbidity by latitude. The current public health advice of avoiding sun exposure to reduce the risk of developing skin cancer may need to be modified.

Nitrite (NO2-) substrate under certain conditions can cause failure of N-removal processes relying on anaerobic ammonium oxidizing (anammox) bacteria. Detoxification of NO2- can potentially be achieved by using exogenous nitrate (NO3-). In this work, continuous experiments in bioreactors with anammox bacteria closely related to “Candidatus Brocadia caroliniensis” were conducted to evaluate the effectiveness of short NO3- additions to reverse NO2- toxicity. The results show that a timely NO3- addition immediately after a NO2- stress event completely reversed the NO2- inhibition. This reversal occurs without NO3- being metabolized as evidence by lack of any 30N2 formation from 15N-NO3-. The maximum recovery rate was observed with 5 mM NO3- added for 3 days; however, slower but significant recovery was also observed with 5 mM NO3- for 1 day or 2 mM NO3- for 3 days. Without NO3- addition, long-term NO2- inhibition of anammox biomass resulted in irreversible damage of the cells. These results suggest that a short duration dose of NO3- to an anammox bioreactor can rapidly restore the activity of NO2--stressed anammox cells. On the basis of the results, a hypothesis about the detoxification mechanism related to narK genes in anammox bacteria is proposed and discussed.

Master of Science / Food Science / Terry Houser / The objective of this research was to evaluate the effect of natural nitrites on objective color of vacuum packaged fresh pork. Sections of longissimus dorsi muscle (approximately 18 cm) were injected with solutions containing 0, 3, 6, 9 or 12 ppm of natural nitrite. Sections were sliced into chops (2.54 cm) and individually vacuum packaged. Raw chop surface L*, a* and b* values were measured at 1, 5, 15 and 30 days post packaging. At 1, 15 and 30 days post packaging chops were cooked and surface L*, a* and b* values were measured. Hue and Chroma values were calculated for all color measurements. Linear and quadratic contrasts were evaluated on treatments for all measured and calculated color values. A linear (P<0.05) increase was detected on the L* values for days of vacuum storage treatment, all other raw color measurements and calculations for levels of natural nitrite and days of vacuum package storage were found to be quadratic (P<0.05). Cooked L* and Hue values for days of vacuum storage were found to decrease linearly (P<0.05), all other days of storage and levels of nitrite treatments were found to be quadratic (P<0.05) in relationship to the measured and calculated cooked color values. All raw chops containing nitrite had higher a* and Chroma values at all evaluation days than those containing no added nitrite. Raw chops containing nitrite had lower L*, higher b* and Hue values than the 0 ppm chops (P<0.05). Raw chops containing natural nitrite were darker, redder, more yellow and more intense in color than those without nitrite. The longer the chops were vacuum packaged and then cooked, the lower the L* values were (P<0.05). Cooked chops containing nitrite were redder, less yellow and lower in Hue and Chroma values than cooked chops with no added nitrite P(<0.05). These results indicate that low levels of nitrite can alter fresh and cooked pork color during vacuum storage. To balance the increased redness and darkness of the raw chops with the increased redness of the cooked chops, 3 ppm of natural nitrite was found to be the optimal treatment.

Multi-electron multi-proton reactions form the basis of nearly every chemical reaction involved in energy storage and manipulation. Despite their importance, the basic properties of these chemical transformations, such as the details of how electron transfer and proton-coupled redox events that must occur during these reactions are controlled, remain poorly understood. The sulfite and nitrite reductase family of enzymes are responsible for carrying out the six-electron reduction of sulfite to sulfide and nitrite to ammonia, respectively. These enzymes play fundamental roles in microbial metabolism and are either dissimilatory or assimilatory in nature. Multi-electron multi-proton reactions are investigated by the study of the catalytic mechanisms of two enzymes that are structurally different, but carry out similarly complex chemistry: the dimeric multi heme cytochrome c nitrite reductase from Shewanella oneidensis and the monomeric siroheme and [4Fe-4S] cluster containing sulfite reductase from Mycobacterium tuberculosis. Employing protein electrochemistry the properties of electron transfer steps and proton-coupled redox steps that occur throughout the catalytic cycle of cytochrome c nitrite reductase during its reduction of substrate revealed the strategies employed by this enzyme. The results presented indicate the reduction of substrate by the enzyme occurs in a series of one electron steps rather than coupled two-electron transfers. Mutational analysis of active site amino acids reveals their role in governing proton coupled redox events, which likely involves a hydrogen bonding network consisting of these residues and water molecules. Additionally, steady state kinetics assays coupled to site-directed mutagenesis of M. tuberculosis sulfite reductase identify a tyrosine residue adjacent to the active site which partially controls substrate preference, by influencing the electronic environment of the active site siroheme cofactor. Stopped-flow absorbance spectroscopy and rapid freeze quench electron paramagnetic resonance studies provide a first glimpse of a potential reaction intermediate during reduction of sulfite by sulfite reductase. Overall, our fundamental understanding of how sulfite and nitrite reductase enzymes catalyze complex multi-electron multi-proton reactions is advanced, and insight into the different approaches Nature employs to govern such powerful chemistry is revealed.

As atividades humanas vêm aumentando dramaticamente a quantidade de nitrogênio inorgânico liberado nos ecossistemas, seja através da aplicação de fertilizantes na agricultura, da descarga de dejetos humanos e de seus rebanhos, ou da queima de combustíveis fósseis. Os excessos de nitrogênio são eventualmente transportados para corpos d´água, onde podem, na forma de nitrato, nitrito e amônio, atingir concentrações tóxicas para organismos aquáticos. Nesta pesquisa tive dois objetivos principais. O primeiro foi testar em laboratório a toxicidade relativa dos íons nitrato, nitrito e amônio, e a variação interespecífica na sensibilidade a esses íons, em larvas de cinco espécies de anuros (Rhinella ornata, Hypsiboas faber, Hypsiboas pardalis, Physalaemus cuvieri e Physalaemus olfersii ). Para isso utilizei bioensaios seguindo protocolos internacionalmente padronizados para testes de ecotoxicidade com organismos aquáticos, e que portanto permitem máximas reprodutibilidade e comparabilidade de resultados entre compostos, espécies, e laboratórios. No entanto, estes bioensaios carecem de realismo uma vez que simulam um cenário de exposição aguda a altas concentrações de contaminantes quando na natureza o cenário de exposição tende a ser crônico e prolongado a baixas concentrações. Além disso, bioensaios usam mortalidade como principal variável de resposta, quando também efeitos subletais podem influenciar a persistência de populações ao modular o sucesso dos indivíduos. Por isso, meu segundo objetivo foi testar em laboratório se concentrações relativamente baixas e ecologicamente relevantes de nitrato, nitrito e amônio podem afetar a sobrevivência, o crescimento, o desenvolvimento e o comportamento das larvas de R. ornata, P. cuvieri e H. faber. Demonstrei através dos bioensaios de exposição aguda que nitrato, a forma mais abundante na natureza, é de baixa toxicidade quando comparada a nitrito e amônio. Demonstrei também que há significativa variação interespecífica na sensibilidade ao nitrogênio inorgânico, e que o ranqueamento de sensibilidade das espécies ao nitrato e ao nitrito foram similares, possivelmente por conta de mecanismos comuns de ação tóxica. Através de experimentos de exposição crônica demonstrei que concentrações relativamente baixas de nitrogênio inorgânico podem causar efeitos letais e subletais às larvas de anuros se houver exposição prolongada. O nitrato causou redução no desenvolvimento larval de P. cuvieri e o amônio na sobrevivência e nas taxas de atividade nos girinos de H. faber. A exposição crônica ao nitrito também reduziu significativamente a sobrevivência das três espécies testadas, o crescimento de H. faber e as taxas de atividade de R. ornata. Contudo, é improvável que as concentrações de nitrito que manipulei em laboratório sejam comuns na natureza, especialmente em condições aeróbicas. Esta pesquisa, além de fornecer importantes informações sobre os possíveis efeitos da poluição por nitrogênio em larvas de anuros, contribui para o avanço da ecotoxicologia no Brasil ao estabelecer as bases para o emprego de espécies nativas de anfíbios como sistema-modelo experimental. Estudos futuros que almejem avaliar o risco ambiental da contaminação por nitrogênio deverão por um lado monitorar concentrações em hábitats naturais e por outro avaliar as consequências das interações sinérgicas entre nitrogênio inorgânico e outros estressores físicos, químicos ou biológicos para larvas de anfíbios. / Human activities dramatically increased the amount of inorganic nitrogen released in ecosystems through the application of fertilizers in agriculture, the generation of human and livestock waste, and the combustion of fossil fuels. This nitrogen eventually reaches water bodies where it can, in the form of nitrate, nitrite and ammonium, be toxic to aquatic organisms. In this study I had two main objectives. The first was to test the relative toxicity of nitrate, nitrite and ammonium, and the interspecific variation in sensitivity to these ions, in tadpoles of five anuran species (Rhinella ornata, Hypsiboas faber, Hypsiboas pardalis, Physalaemus cuvieri and Physalaemus olfersii ). This objective was accomplished by laboratory bioassays following internationally standardized protocols for ecotoxicity tests with aquatic organisms, therefore allowing maximum reproducibility and comparability of results among compounds, species and laboratories. However, these bioassays lack realism for simulating a scenario of acute exposure to high concentrations of contaminants, while exposure in nature tends to be chronic and prolonged at low concentrations. Furthermore, bioassays use mortality as the main response variable, whereas sublethal effects may also influence the persistence of populations by modulating individual success. My second objective was therefore to test in the laboratory if low and environmentally relevant concentrations of nitrate, nitrite and ammonium affect survival, growth, development and behavior of R. ornata, P. cuvieri and H. faber larvae. Through acute exposure bioassays I demonstrated that nitrate, the most abundant N form in nature, has low toxicity when compared to nitrite and ammonium. I also demonstrated that there is significant interspecific variation in the sensitivity to inorganic nitrogen, and that the ranking of species sensitivity to nitrate and nitrite were similar, possibly due to common mechanisms of toxic action. Through chronic exposure I demonstrated that relatively low concentrations of inorganic nitrogen can cause lethal and sublethal effects on anuran larvae if there is extended exposure. Nitrate decreased developmental rate in P. cuvieri and ammonia decreased survival and activity rates in H. faber tadpoles. Chronic exposure to nitrite also significantly reduced survival of all three species tested, growth of H. faber and activity rates of R. ornata. However, it is unlikely that the concentrations of nitrite manipulated in the laboratory are common in nature, especially in aerobic conditions. This is the first study to document deleterious effects of nitrogen pollution to Brazilian amphibian species, and contributes to the development of ecotoxicology in Brazil by establishing the basis for the employment of native amphibians as model experimental system. Future studies that aim to assess the environmental risk of nitrogen contamination should monitor concentrations in natural habitats and evaluate the effects of synergistic interactions between inorganic nitrogen and other physical, chemical or biological stressors to amphibian larvae.

O nitrito pode ser reduzido a NO de forma dependente do pH ácido do estômago ou por enzimas com atividade nitrito-redutase. O tratamento com omeprazol, previne parte dos efeitos anti-hipertensivos do nitrito administrado por via oral por aumentar o pH gástrico. Contudo, nenhum estudo até o momento avaliou se, assim como o omeprazol, a ranitidina também é capaz de atenuar os efeitos anti-hipertensivos do nitrito de sódio por aumentar o pH gástrico. Nesse estudo, examinamos se a administração oral de ranitidina poderia prejudicar os efeitos anti-hipertensivos do nitrito de sódio administrados por via oral, por interferir na formação de NO e espécies nitrosiladas a partir do nitrito. A fim de verificar a influência da ranitidina no efeito hipotensor do nitrito de sódio, utilizamos animais tratados agudamente com LNAME pré-tratados com ranitidina, omeprazol e veículo e, posteriormente, com nitrito de sódio 15mg/kg. Como esperado, o tratamento com L-NAME resultou em aumento na pressão arterial média (PAM). O pH gástrico foi diferente entre os grupos, tendo um aumento no pH dos animais tratados com ranitidina e omeprazol, quando comparado ao veículo, e os tampões tinham o mesmo pH do veículo e das drogas. O nitrito de sódio exerceu efeitos anti-hipertensivos significativos nos grupos estudados. No entanto, foram observadas menores diminuições na PAM em ratos tratados com omeprazol e ranitidina em comparação aos ratos que receberam veículo. Esses achados foram associados a diminuições nas concentrações gástricas de NO e diminuições nos níveis plasmáticos de espécies nitrosiladas. Além disso, houve aumento nas concentrações de nitrito no estômago. Não foram observadas diferenças nas concentrações de nitrito no plasma. Além disso, não foram observadas diferenças nos níveis de NOx no plasma e estômago entre os grupos do estudo. Os animais tratados com tampão apresentaram resultados similares aos tratados com as drogas. Nossos resultados sugerem que a ranitidina, ao aumentar o pH gástrico, afeta as respostas anti-hipertensivas ao nitrito de sódio oral por diminuir a formação de NO e espécies nitrosiladas. Este fato é reforçado pelo aumento do nitrito no estômago, sugerindo uma diminuição na conversão de nitrito a NO e espécies nitrosiladas no ambiente gástrico. / Nitrite can be reduced to NO depending on acidic pH of the stomach or by enzymes with nitrite reductase activity. Treatment with omeprazole attenuates the antihypertensive effects of oral nitrite by increasing of gastric pH. However, studies are still necessary to further evaluate wheter ranitidine is also able to attenuate the antihypertensive effects of sodium nitrite by increasing gastric pH. In this study, we examined whether oral administration of ranitidine could impair oral antihypertensive effects of sodium nitrite by interfering with the formation of NO and nitrosylated species from nitrite. In order to analyze the influence of ranitidine under hypotensive effect of sodium nitrite, rats were treated with L-NAME and pretreated with ranitidine, omeprazole, vehicle or buffer, subsequently all the groups were treated with sodium nitrite 15 mg/kg. The L-NAME treatment increase mean arterial pressure (MAP). The gastric pH was different among the groups, there was an increased in rats gastric pH treated with ranitidine and omeprazole compared to the vehicle. The buffer group had the same pH of vehicle and drugs treatment. Sodium nitrite exerted significant antihypertensive effects in the groups studied. However, lesser decreases in MAP were observed in rats treated with omeprazole and ranitidine compared to rats that received vehicle. These findings were associated with a lower NO gastric concentrations as well as nitrosylated species plasma levels. In addition, there was an increased in nitrite concentrations in the stomach. No differences were observed in plasma nitrite levels. Moreover, there was not any significant difference in plasma and stomach NOx levels among the studied groups. The rats treated with buffer showed similar results to those treated with the drugs. Together these data demonstrated that ranitidine, through increased gastric pH, affects antihypertensive responses to oral sodium nitrite by reducing the formation of NO and nitrosylated species. This fact is reinforced by higher levels in nitrite concentrations in the stomach, thereby it suggests a lower conversion of nitrite to NO and nitrosylated species in the gastric environment.

Recently, it has emerged that the NO metabolites, nitrite and nitrate can be chemically reduced in vivo to biologically active nitric oxide (NO). This generation of NO is dependent on reduction of nitrate to nitrite by facultative anaerobes on the dorsal surface of the tongue, entry of the nitrite into the enterosalivary circuit, transit to the stomach, and absorption through the gut wall into the circulation. Conversion of nitrite to NO is then facilitated by vascular nitrite reductase enzymes. This nitrate-nitrite-NO pathway has been shown to exert a number of beneficial effects in healthy volunteers e.g. lowering of blood pressure, however whether this pathway is affected by cardiovascular disease (CVD) is currently unknown. Ozone chemiluminescence was used to determine and compare nitrite and nitrate levels in 2 models of CVD. To study atherosclerosis wild type (WT) and apolipoprotein E knock out (ApoE KO) mice were used and for hypertension wistar kyoto (WKY) rats as controls vs. spontaneously hypertensive rats (SHR). Assessment of nitrite reductase activity was conducted in the compartment which showed the most consistent differences in distribution, the red blood cell (RBC) and in homogenates of liver tissue. The impact of dietary nitrite and nitrate on distribution of the 2 anions throughout the cardiovascular system was assessed to determine the utility of this approach in restoring levels of these anions in CVD. Finally, using flow cytometry I investigated whether dietary nitrate supplementation could be used to influence inflammatory responses as a mechanism to improve CVD. Compared to WT mice, nitrate levels were reduced in ApoE KO mice in the plasma and across most of the tissues. In contrast in SHRs, reduction of the anions was only apparent in RBCs with no differences compared to WKY in all other tested tissues. Furthermore I have demonstrated that the most efficient way to restore nitrate levels back up to baseline is through a dietary nitrate strategy and that a dose of 15mM nitrate in the drinking water is sufficient to achieve this. In addition I have shown that nitrite reductase activity is enhanced in CVD particularly at the level of the RBC in both atherosclerosis and hypertension and that this enhanced activity is due, in part, to upregulation of xanthine oxidoreductase (XOR). Finally I have shown that dietary nitrate is an effective way to modulate an acute inflammatory response. This modulation is mediated through interfering with the ability of the neutrophil to firmly adhere to the vascular endothelium. These changes were shown to be dose-dependent and concomitant with dose-dependent increases in plasma nitrite and plasma nitrate. These data suggest that utilization of the nitrate-nitrite-NO pathway with dietary nitrate may represent an effective approach for the treatment of CVD.