Implementation of enhanced biological phosphorus removal (ebpr) wastewater treatment processes enriched with different microbial communities

The EBPR (Enhanced Biological Phosphorus Removal) is a type of secondary treatment in WWTPs (WasteWater Treatment Plants), quite largely used in full-scale plants worldwide. The phosphorus occurring in aquatic systems in high amounts can cause eutrophication and consequently the death of fauna and flora. A specific biomass is used in order to remove the phosphorus, the so-called PAOs (Polyphosphate Accumulating Organisms) that accumulate the phosphorus in form of polyphosphate in their cells. Some of these organisms, the so-called DPAO (Denitrifying Polyphosphate Accumulating Organisms) use as electron acceptor the nitrate or nitrite, contributing in this way also to the removal of these compounds from the wastewater, but there could be side reactions leading to the formation of nitrous oxides. The aim of this project was to simulate in laboratory scale a EBPR, acclimatizing and enriching the specialized biomass. Two bioreactors were operated as Sequencing Batch Reactors, one enriched in Accumulibacter, the other in Tetrasphaera (both PAOs): Tetrasphaera microorganisms are able to uptake aminoacids as carbon source, Accumulibacter uptake organic carbon (volatile fatty acids, VFA). In order to measure the removal of COD, phosphorus and nitrogen-derivate compounds, different analysis were performed: spectrophotometric measure of phosphorus, nitrate, nitrite and ammonia concentrations, TOC (Total Organic Carbon, measuring the carbon consumption), VFA via HPLC (High Performance Liquid Chromatography), total and volatile suspended solids following standard methods APHA, qualitative microorganism population via FISH (Fluorescence In Situ Hybridization). Batch test were also performed to monitor the NOx production. Both specialized populations accumulated as a result of SBR operations; however, Accumulibacter were found to uptake phosphates at higher extents. Both populations were able to remove efficiently nitrates and organic compounds occurring in the feeding. The experimental work was carried out at FCT of Universidade Nova de Lisboa (FCT-UNL) from February to July 2014.

The role of DNA damage in the pathogenesis of nitrate tolerance - nitrosative versus oxidative DNA damage

6. Summary Despite the lack of direct evidence from large clinical trials for mutagenic and genotoxic effects of GTN therapy, the present study show s the induction of pre-mutagenic lesions, such as 8- oxo - G and O 6 - me - G by GTN t reatment as well as increased formation of DNA strand breaks. These results were obtained in an in vitro (EA.hy 926 – human endothelial cell line) and in vivo (Wistar rats and C57BL/6 mice) setting. However, GTN - induced DNA damage had no effect on the degr ee of nitrate tolerance but only on other pathological side effects such as oxidative stress, as confirmed by studies in MGMT knockout mice. Of clinical importance , this study establishes potent apoptotic properties of organic nitrates, which has been demo nstrated by the levels of the novel apoptotic marker and caspase - 3 substrate, fractin, as well as levels of cleaved caspase - 3 , the activated form of this pro - apoptotic enzyme . The p rotein analy tical data ha ve been confirmed by an independent assay for the apoptosis , Cell death detection assay (TUNEL) . First, these GTN - mediated apoptotic effects may account for the previously reported anti - cancer effects of GTN therapy (probably based on induction of apoptosis in tumor cells). Second, these GTN - mediated apop totic effects may account for the increased mortality rates observed in the group of organic nitrate - treated patients as reported by two independent meta - analysis (probably due to induction of apoptosis in highly beneficial endothelial progenitor cells as well as in cardiomyocytes during wound healing and cardiac remodeling) . Summary of the current investigations can be seen in Figure 18.

Ground Water Impact Assessment in Rural Areas of North-Eastern Part of Ukrain

Protecting ground water from pollution in the rural areas of Ukraine is a priority, particularly because the largely unconfined aquifers are used by local people for potable water supply. The most important aim of this project was to characterise the scale and impact of pollution sources on groundwater quality according to the nature of groundwater vulnerability and of the particular sources of pollution. Analysis of 50 different maps of Ukraine according to geochemical, natural and landscape features, together with field studies made it possible to identify areas with different pollution risk factors. The most harmful sources of groundwater contamination providing nitrates, petrol, heavy metals and other pollutants were identified and an integral method of groundwater quality assessment was worked out. The main sources of groundwater contamination in rural areas of Ukraine were identified and listed in order of importance. Magmedov also puts forward recommendations for improving monitoring of groundwater quality as an essential part of sustainable development in rural areas of Ukraine.

Dating groundwater in the Bohemian Cretaceous Basin: Understanding tracer variations in the subsurface

The northern section of the Bohemian Cretaceous Basin has been the site of intensive U exploitation with harmful impacts on groundwater quality. The understanding of groundwater flow and age distribution is crucial for the prediction of the future dispersion and impact of the contamination. State of the art tracer methods (3H, 3He, 4He, 85Kr, 39Ar and 14C) were, therefore, used to obtain insights to ageing and mixing processes of groundwater along a north–south flow line in the centre of the two most important aquifers of Cenomanian and middle Turonian age. Dating of groundwater is particularly complex in this area as: (i) groundwater in the Cenomanian aquifer is locally affected by fluxes of geogenic and biogenic gases (e.g. CO2, CH4, He) and by fossil brines in basement rocks rich in Cl and SO4; (ii) a thick unsaturated zone overlays the Turonian aquifer; (iii) a periglacial climate and permafrost conditions prevailed during the Last Glacial Maximum (LGM), and iv) the wells are mostly screened over large depth intervals. Large disagreements in 85Kr and 3H/3He ages indicate that processes other than ageing have affected the tracer data in the Turonian aquifer. Mixing with older waters (>50 a) was confirmed by 39Ar activities. An inverse modelling approach, which included time lags for tracer transport throughout the unsaturated zone and degassing of 3He, was used to estimate the age of groundwater. Best fits between model and field results were obtained for mean residence times varying from modern up to a few hundred years. The presence of modern water in this aquifer is correlated with the occurrence of elevated pollution (e.g. nitrates). An increase of reactive geochemical indicators (e.g. Na) and radiogenic 4He, and a decrease in 14C along the flow direction confirmed groundwater ageing in the deeper confined Cenomanian aquifer. Radiocarbon ages varied from a few hundred years to more than 20 ka. Initial 14C activity for radiocarbon dating was calibrated by means of 39Ar measurements. The 14C age of a sample recharged during the LGM was further confirmed by depleted stable isotope signatures and near freezing point noble gas temperature. Radiogenic 4He accumulated in groundwater with concentrations increasing linearly with 14C ages. This enabled the use of 4He to validate the dating range of 14C and extend it to other parts of this aquifer. In the proximity of faults, 39Ar in excess of modern concentrations and 14C dead CO2 sources, elevated 3He/4He ratios and volcanic activity in Oligocene to Quaternary demonstrate the influence of gas of deeper origin and impeded the application of 4He, 39Ar and 14C for groundwater dating.

Placing unprecedented recent fir growth in a European-wide and Holocene-long context

Forest decline played a pivotal role in motivating Europe's political focus on sustainability around 35 years ago. Silver fir (Abies alba) exhibited a particularly severe dieback in the mid-1970s, but disentangling biotic from abiotic drivers remained challenging because both spatial and temporal data were lacking. Here, we analyze 14 136 samples from living trees and historical timbers, together with 356 pollen records, to evaluate recent fir growth from a continent-wide and Holocene-long perspective. Land use and climate change influenced forest growth over the past millennium, whereas anthropogenic emissions of acidic sulfates and nitrates became important after about 1850. Pollution control since the 1980s, together with a warmer but not drier climate, has facilitated an unprecedented surge in productivity across Central European fir stands. Restricted fir distribution prior to the Mesolithic and again in the Modern Era, separated by a peak in abundance during the Bronze Age, is indicative of the long-term interplay of changing temperatures, shifts in the hydrological cycle, and human impacts that have shaped forest structure and productivity.

Springtime Nutrient and Phytoplankton Dynamics on Georges Bank

The dynamics of phytoplankton and nutrients before, during and after the winter-spring bloom on Georges Bank were studied on 6 monthly survey cruises from January to June 1999. We measured hydrography, phytoplankton cell densities, chlorophyll a, dissolved inorganic nutrients (NO3 + NO2, NH4, Si(OH)(4), PO4), dissolved organic nitrogen (DON) and phosphorus (DOP), particulate organic carbon (POC) and nitrogen (PON) and total particulate phosphorus (TPP). We present evidence that phytoplankton production may be significant year-round, and that the winter-spring bloom may have started in January. From January to April the phytoplankton was comprised almost exclusively of diatoms, reaching cell densities in March and April of ca. 450 cells ml(-1); chlorophyll a concentrations exceeded 10 mug l(-1) in April. Diatoms decreased to relatively low levels in May (< 50 x 10(3) cells l(-1)) and increased again in June (>300 x 10(3) cells l(-1)). Densities of dinoflagellates and nanoflagellates were low (< 10 x 10(3) cells l(-1)) from January to April, and increased in May and June to nearly 300 x 10(3) cells l(-1). Nitrate + nitrite concentrations in January were <3 muM in the shallow, central portion of the bank and decreased steadily each month. Silicate was also <3 muM over an even larger area of the central bank in January and declined to <1.5 muM over most of the Bank in April. The data suggest that silicate depletion, not DIN, contributed to the cessation of the diatom bloom. Regeneration of silicate occurred in May and June, presumably as a result of rising water temperatures in late spring which increased the dissolution rate of diatom frustules from the earlier diatom bloom. Dissolved organic nitrogen may have been utilized at the start of the winter-spring bloom; concentrations were ca, 14 muM in January, dropping to < 6 mug l(-1) in February, after which DON concentrations steadily rose to > 15 mug l(-1) in June. Overall micro-and nanoplankton biomass, measured as POC, PON and TPP, increased over the 6 mo period, as did nutritional quality of that biomass as indicated by declining C:N ratios. Our results suggest there may have been an increase in the heterotrophic component of the plankton in May and June which coincided with a second burst in diatom abundance. We discuss general features of planktonic production and nutrient dynamics with respect to year-round production on the Bank.

Relationships between soil nitrate desorbed from anion-exchange membranes, canopy reflectance and nitrate leaching losses from cool-season lawn turf.

Nutrient leaching studies are expensive and require expertise in water collection and analyses. Less expensive or easier methods that estimate leaching losses would be desirable. The objective of this study was to determine if anion-exchange membranes (AEMs) and reflectance meters could predict nitrate (NO3-N) leaching losses from a cool-season lawn turf. A two-year field study used an established 90% Kentucky bluegrass (Poa pratensis L.)-10% creeping red fescue (Festuca rubra L.) turf that received 0 to 98 kg N ha-1 month-1, from May through November. Soil monolith lysimeters collected leachate that was analyzed for NO3-N concentration. Soil NO3-N was estimated with AEMs. Spectral reflectance measurements of the turf were obtained with chlorophyll and chroma meters. No significant (p > 0.05) increase in percolate flow-weighted NO3-N concentration (FWC) or mass loss occurred when AEM desorbed soil NO3-N was below 0.84 µg cm-2 d-1. A linear increase in FWC and mass loss (p < 0.0001) occurred, however, when AEM soil NO3-N was above this value. The maximum contaminant level (MCL) for drinking water (10 mg L-1 NO3-N) was reached with an AEM soil NO3-N value of 1.6 µg cm-2 d-1. Maximum meter readings were obtained when AEM soil NO3 N reached or exceeded 2.3 µg cm-2 d-1. As chlorophyll index and hue angle (greenness) increased, there was an increased probability of exceeding the NO3-N MCL. These data suggest that AEMs and reflectance meters can serve as tools to predict NO3-N leaching losses from cool-season lawn turf, and to provide objective guides for N fertilization.

Anion exchange membrane soil nitrate predicts turfgrass color and yield.

Desirable nitrogen (N) management practices for turfgrass supply sufficient N for high quality turf while limiting excess soil N. Previous studies suggested the potential of anion exchange membranes (AEMs) for predicting turfgrass color, quality, or yield. However, these studies suggested a wide range of critical soil nitrate-nitrogen (NO3-N) values across sample dates. A field experiment, in randomized complete block design with treatments consisting of nine N application rates, was conducted on a mixed species cool-season turfgrass lawn across two growing seasons. Every 2 wk from May to October, turfgrass color was assessed with three different reflectance meters, and soil NO3-N was measured with in situ AEMs. Cate-Nelson models were developed comparing relative reflectance value and yield to AEM desorbed soil NO3-N pooled across all sample dates. These models predicted critical AEM soil NO3-N values from 0. 45 to 1.4 micro g cm-2 d-1. Turf had a low probability of further positive response to AEM soil NO3-N greater than these critical values. These results suggest that soil NO3-N critical values from AEMs may be applicable across sample dates and years and may serve to guide N fertilization to limit excess soil NO3-N.

An evaluation of a Lake Houston tributary, Cypress Creek, for contamination and water quality

Introduction. Lake Houston serves as a reservoir for both recreational and drinking water for residents of Houston, Texas, and the metropolitan area. The Texas Commission on Environmental Quality (TCEQ) expressed concerns about the water quality and increasing amounts of pathogenic bacteria in Lake Houston (3). The objective of this investigation is to evaluate water quality for the presence of bacteria, nitrates, nitrites, carbon, phosphorus, dissolved oxygen, pH, turbidity, suspended solids, dissolved solids, and chlorine in Cypress Creek. The aims of this project are to analyze samples of water from Cypress Creek and to render a quantitative and graphical representation of the results. The collected information will allow for a better understanding of the aqueous environment in Cypress Creek.^ Methods. Water samples were collected in August 2009 and analyzed in the field and at UTSPH laboratory by spectrophotometry and other methods. Mapping software was utilized to develop novel maps of the sample sites using coordinates attained with the Global Positioning System (GPS). Sample sites and concentrations were mapped using Geographic Information System (GIS) software and correlated with permitted outfalls and other land use characteristic.^ Results. All areas sampled were positive for the presence of total coliform and Escherichia coli (E. coli). The presences of other water contaminants varied at each location in Cypress Creek but were under the maximum allowable limits designated by the Texas Commission on Environmental Quality. However, dissolved oxygen concentrations were elevated above the TCEQ limit of 5.0 mg/L at majority of the sites. One site had near-limit concentration of nitrates at 9.8 mg/L. Land use above this site included farm land, agricultural land, golf course, parks, residential neighborhoods, and nine permitted TCEQ effluent discharge sites within 0.5 miles upstream.^ Significance. Lake Houston and its tributary, Cypress Creek, are used as recreational waters where individuals may become exposed to microbial contamination. Lake Houston also is the source of drinking water for much of Houston/Harris and Galveston Counties. This research identified the presence of microbial contaminates in Cypress Creek above TCEQ regulatory requirements. Other water quality variables measured were in line with TCEQ regulations except for near-limit for nitrate at sample site #10, at Jarvis and Timberlake in Cypress Texas.^

Determinación de nitratos en vegetales : comparación de cuatro métodos analíticos

Para la cuantificación de nitratos hay numerosas técnicas y no existe entre los analistas unanimidad en la selección de la más adecuada. Por tal motivo, se compararon cuatro métodos para la determinación de nitratos en muestras vegetales con el fin de evaluar la correlación entre los mismos y establecer pautas para su utilización. Se utilizaron 690 muestras de lechuga (Lactuca sativa L. var. capitata), pertenecientes a los tipos arrepollado y mantecoso, recolectadas a lo largo de un año en el Mercado Cooperativo de Guaymallén (Mendoza, Argentina). Según los tenores de nitratos encontrados en la población estudiada se efectuó un sub-muestreo aleatorio estratificado proporcional para lograr un número de muestras que representaran la variabilidad del total de la población. Se utilizaron cuatro métodos para la determinación de nitratos: 1. destilación por arrastre con vapor, considerado como método de referencia 2. colorimetría por nitración con ácido salicílico 3. colorimetría modificada 4. potenciometría con electrodo selectivo Se probaron diferentes modelos de regresión entre el método de referencia y los otros tres, siendo el lineal el que mejor se ajustó en todos los casos. Los métodos estudiados tuvieron comportamiento semejante. La mayor correlación (r2 = 93 %) se observó entre la destilación por arrastre con vapor y la potenciometría; no obstante, los restantes también presentaron alta correlación. Consecuentemente, la elección del procedimiento analítico dependerá principalmente del número de muestras a analizar, del tiempo requerido por el análisis y del costo del mismo.

Variación de la concentración de nitratos en un suelo franco limoso del Alto Valle de Río Negro.

La abundancia y bajo costo del recurso hídrico en el Alto Valle de Río Negro combinados con un manejo ineficiente del mismo, principalmente durante la primera parte de la primavera, época en la que los productores riegan con mayor frecuencia para luchar pasivamente contra las probables heladas tardías, permiten inferir que los nitratos presentes en el suelo, así como el aportado por los fertilizantes nitrogenados, están sujetos al lixiviado durante una gran parte del ciclo productivo. En la actualidad no existen estudios regionales que ilustren la variación estacional de la concentración de nitratos en la zona de exploración radical de frutales, por lo que se inició el presente trabajo con el propósito de: a) medir la concentración de los nitratos en el perfil del suelo cultivado con manzanos, desde el período de floración hasta el inicio de caída de hojas, con fertilización nitrogenada en dos dosis y sin fertilización a distintas profundidades de extracción; b) determinar la eficiencia del riego a manto de dicho monte. Se ensayaron dos concentraciones de nitrógeno, adicionado como nitrato de amonio en dos oportunidades: el 50% a la caída de los pétalos y el 50% restante cercano a la cosecha, correspondiendo a dosis de 100 kg ha-1 (N1), 200 kg ha-1 (N2) y un testigo sin agregado de N (N0), durante el período 2004-2005 y 2005-2006. Para determinar los niveles de N en el suelo, expresado como nitratos, se extrajeron muestras del mismo a tres profundidades 0-30; 30-60; 60-90 cm, al inicio de floración, antes del primer riego y después de cada riego. La lámina de agua empleada para el riego a manto osciló entre 1712 y 2400 mm, con un aprovechamiento a campo del 30%. La concentración de nitratos fue baja cuando no se fertilizó, manteniéndose alrededor de 22 mg kg-1 en superficie y reduciéndose a la mitad a la profundidad de 30-60 cm, durante el período de muestreo. En ambas dosis empleadas, el contenido de nitratos del suelo fue mayor llegando a 175 y 300 mg kg-1, respectivamente. Estos valores se igualan a los del testigo a los 30 días en el caso de N1 y a los 60 días para N2. Los resultados permiten inferir que la concentración de nitratos fue efímera en el perfil del suelo y mejoró la eficiencia de riego, principalmente durante la primavera con el fin de minimizar pérdidas de nitrógeno.

Aplicación de nitratos y cloruros en Amaranthus tricolor L. : efecto sobre la producción de materia verde, materia seca, contenidos de nitratos y cloruros.

Se evaluó la incidencia del agregado de cloruros (Cl-) adicionado como NaCl, y de nitrógeno (N) como KNO3, sobre la producción de materia verde (MV), materia seca (MS) y contenido de nitratos (NO3 -) y Cl- en la parte aérea cosechada de Amaranthus tricolor L. El ensayo se realizó en el invernáculo de la Facultad de Agronomía, UNLPam., Santa Rosa, La Pampa, Argentina, en macetas que contenían 5 kg de suelo. Las dosis de fertilizante agregado en kg ha-1 fueron: 50 y 100 de N y 100, 200 y 300 de Cl-. Se realizaron todas las combinaciones posibles originando 12 tratamientos, incluido el testigo. Para el análisis estadístico se empleó ANOVA doble y los tests de Tukey y Tukey-Kramer. No se encontraron diferencias significativas para MS para ningún agregado. Tampoco se encontraron diferencias significativas en la producción de MV entre las dosis de N (N50 y N100) pero sí entre éstas y el testigo. No hubo diferencias entre las dosis de Cl- aplicadas para esta variable. Los NO3 - mostraron diferencias significativas frente a las distintas dosis de N, como así también entre las medias de los tratamientos con el agregado de Cl- y la no incorporación de éstos. Los valores promedio de NO3 - variaron entre 0,51 y 3,56% base seca (bs) y 445,4 y 2916,1 mg kg-1 fresco. Se encontraron diferencias significativas en el % Cl- (bs) frente a las diferentes dosis de NaCl adicionado. Bajo las condiciones del ensayo, los valores promedio de NO3 - se encuentran dentro de los límites establecidos por la Comunidad Económica Europea.

Prótidos y nitratos en A. Tricolor L. fertilizado con NPK

Se evaluó la incidencia de la fertilización de nitrógeno (N), fósforo (P) y potasio (K) sobre el contenido de prótido crudo (Pr.C.) y acumulación de nitratos (NO3 -) en hojas de Amaranthus tricolor L. El ensayo, realizado en el invernáculo de la Facultad de Agronomía (UNLPam, Santa Rosa, Argentina), se efectuó en macetas utilizando un suelo con baja fertilidad. Las dosis de fertilizantes agregados -en kg/ha- fueron: 50 y 100 para N; 60 y 90, para P y 120, para K. Se practicaron todas las combinaciones posibles, originando 18 tratamientos, incluido el testigo. Para el análisis estadístico se empleó ANOVA triple y los tests de Tukey y Tukey- Kramer. Las variables analizadas fueron % Pr.C., base seca (b.s.) y contenido de NO3 -,expresado en % NO3 - (b.s.) y NO3 - mg/kg fresco. ¬ Para % Pr.C. se encontraron diferencias altamente significativas (p < 0.01) para las distintas dosis de N y diferencias significativas (p < 0.05) para la interacción PxK. ¬ Para NO3 - expresado como % (b.s.) y mg/kg fresco se encontraron diferencias altamente significativas para el factor N, significativas para P y no significativas para K. ¬ Las diferencias fueron altamente significativas para % (b.s.) en las interacciones dobles NxP y PxK y significativas, para NxK , así como diferencias significativas para todas las interacciones dobles en mg/kg fresco. ¬No se encontró significancia en la interacción triple.

Impactos en el agua subterránea de un sistema de efluentes para riego : el Sistema Paramillos (Lavalle, Mendoza, Argentina)

En este trabajo se evalúa el impacto de un sistema de aprovechamiento de efluentes domésticos para riego en la calidad del agua subterránea. Los puntos de muestreo seleccionados son parte de un monitoreo a mayor escala del cual sólo se incluyeron aquellos relacionados con el sistema de la planta depuradora Paramillos, ubicada al Norte del aglomerado Mendoza. Esta planta consiste en una laguna de estabilización facultativa. Los resultados, presentados en gráficos, mapas y tablas, se discuten a partir del comportamiento de tres componentes del sistema hídrico: agua superficial (efluente), agua subterránea del nivel superior del acuífero (freática) y agua subterránea del acuífero profundo (confinado/ semiconfinado) y su interacción con el perfil del suelo. Se concluye que el acuífero profundo no es alcanzado por nitratos ni nitritos productos de la degradación biológica de la materia orgánica del efluente, lo que se atribuye a la capa impermeable subyacente. En el nivel superior o freático, el perfil del suelo remueve parte del N total y P total ingresado, entre el 39 y 90%. La remoción de DBO varía entre 30 y 90% y la remoción de E. coli remanente en efluente es total.

Evaluación de la contaminación de acuíferos producida por actividades de saneamiento y re-uso de efluentes en el norte de la provincia de Mendoza

En la zona norte de la provincia de Mendoza se desarrollan actividades que pueden afectar la calidad natural del agua subterránea: disposición y re-uso de efluentes industriales para riego agrícola, utilización de fertilizantes, saneamiento in-situ, fugas de redes de alcantarillado, etc. En esta región, surcada superficialmente por los ríos Mendoza y Tunuyán, la sedimentación cuaternaria determinó la formación de dos grandes unidades hidrogeológicas: acuíferos libres (sector de conos aluviales), y acuífero freático superior y acuíferos subyacentes confinados y/o semiconfinados. El área de estudio se encuentra ubicada en esta última unidad hidrogeológica donde se ha detectado contaminación de acuíferos por nitratos. El objetivo de este trabajo es identificar el origen de la contaminación, utilizando metodología hidroquímica mediante la evaluación de diversos parámetros físicoquímicos y biológicos, y técnicas isotópicas para corroborar la procedencia del agua subterránea y el origen de los nitratos. Los resultados obtenidos muestran que la presencia de nitratos en los acuíferos semiconfinado y confinado no proviene de la influencia del acuífero libre suprayacente, afectado por el re-uso de efluentes, sino que se relaciona con el ingreso de flujo horizontal de aguas subterráneas contaminadas provenientes del área del Gran Mendoza, debido a las pérdidas en las redes de alcantarillado y obras de saneamiento in situ.