Bio recuperación de suelos salinos con el uso de materiales orgánicos.

El suelo es un importante recurso natural que necesita ser preservado y mejorado para permitirle mantener su calidad y capacidad productiva, para ello se deben proponer y aplicar prácticas sostenibles que permitan recuperar aquellos suelos degradados por un mal manejo del hombre, como por ejemplo la salinización. El objetivo planteado fue evaluar la biorecuperación de un suelo con problemas salino-sódico con la aplicación de dos proporciones (1,5 y 3% (p/p)) de tres enmiendas orgánicas: compost, vermicompost sólido y Lemna mesclados o no con el 100% de los requerimientos de fosfoyeso, generándose 15 tratamientos (incluyendo tres controles). La evaluación se realizó a través de tres ensayos: 1. Columnas simuladas de suelo. 2. Evolución de CO2 y 3. Crecimiento de plántulas de tomate. El suelo objeto de estudio está clasificado my como Fluventic Haplustepts, y fue tomado de una zona de la Hacienda Alto Viento, con una latitud de 10° 2' 15 N y una longitud de 72 ° 34' 15 W, en el estado de Zulia – Venezuela. Se tomó una muestra compuesta por 20 submuestras de 20 cm de profundidad del área problema, se secó al aire (2,3% de humedad), se tamizó y homogenizó. El suelo y las enmiendas orgánicas fueron caracterizadas. Los materiales orgánicos; compost y vermicompost fueron procesados en la misma Hacienda con el uso de estiércol de ganado bovino; la Lemna fue recolectada de orillas del Lago de Maracaibo en la ciudad de Maracaibo. El suelo se mezcló a las proporciones indicadas se le midió respiración basal y el efecto sobre la germinación de semillas de tomate y se empaquetó en un tubo de polietileno de 7,1 cm de diámetro y 70 a 90 cm de longitud, según la altura de la mezcla del suelo con la enmienda. El fondo de cada columna fue rellenado con 40 cm de arena lavada para facilitar el drenaje. En cada columna se utilizó la misma cantidad de suelo (1055 mg), la altura que ocupó dentro de las columnas dependió del tipo de enmienda orgánica y su proporción, la cual modificó la Da del suelo (1,328±0,05 g•cm-3). La altura dentro de la columna varió desde 20 cm para el suelo sin enmienda hasta 38,33±0,8 cm para el suelo enmendado con Lemna al 3,0%. Transcurrido el periodo de tres meses tiempo en el cual el suelo enmendado y colocado en las columnas fue lavado con una cantidad de agua que equivalente a la tasa de infiltración, la cual se calculó a partir de la precipitación anual de la zona y las perdidas por evaporación y escorrentía; se fraccionó en tres secciones de 7, 7 y 6 cm de longitud, y el suelo de cada fracción se secó al aire y se tamizó, y se le midió CEextr, pH, cationes en solución y cationes extraíbles para calcular el RAS y el PSI. Se tomó una cantidad equivalente de cada sección para conformar una muestra de 50 g de suelos a los cuales se le midió respiración basal e igualmente se tomó suelo para evaluar la germinación y crecimiento de plántulas de tomate. Se detectaron diferencias significativa (p<0,05) entre tratamientos, según la prueba de Tukey, para la variables evaluadas, aunque no hubo diferencias entre las proporciones ni entre la utilización del fosfoyeso mezclado con las enmiendas orgánicas. La enmienda que mostró menos potencial en la bio remediación fue la Lemna por sus altos contenidos de Na+. La metodología de las columnas simuladas del suelo, bajo las condiciones de estudio, no fue del todo adecuada para evaluar la bio remediación debido que en el suelo control por efecto de la aplicación de agua también hubo recuperación del mismo por su disminución en el la CE, RAS y PSI y en algunas variables su recuperación fue mayor que en aquellos enmendados con Lemna. Tomando en la respuesta del cultivo la mejor enmienda fue el vermicompost Abstract The soil is an important natural resource that needs to be preserved and improved to maintain its quality and production potential. Therefore, it is necessary to propose and apply sustainable practices that permit the recovery of soils that have been degraded by inadequate management, among these saline soils. The objective of this study was to evaluate the bioremediation of a saline-sodic soil through the application of two proportions (1,5 and 3% (p/p) of three organic amendments: compost, vermicompost and Lemna, mixed or not with gypsum phosphate, resulting in 15 treatments (including 3 controls). The evaluation was conducted through three tests: 1. Simulated soil columns. 2. Evolution of CO2 and 3. Growth of tomato seedlings The soil under evaluation was classified as Fluventic Haplustepts and was collected from the Alto Viento farm located at 10° 2' 15 North Latitude and 72° 34' 15 West longitude, in Zulia State, Venezuela. A composite soil sample, integrated of 20 subsamples taken to a depth of 20 cm collected in the problem area, was air dried (2.3 % moisture), sieved and homogenized. Soil and organic amendments were characterized. Organic material for the compost and vermicompost were obtained on the farm using cattle manure, whereas the Lemna was collected from the shores of Lake Maracaibo outside Maracaibo city. The soil was mixed in the above-mentioned proportions and its baseline respiration rate and effect on the germination of tomato seeds were recorded. Soil was packed in a PVC pipe (7,1 cm diameter and 70-90 cm length) to simulate a soil column. The bottom of each column was filled out with 40 cm of washed sand to facilitate drainage. The same amount of soil was used in each column (1,055 mg), but the height of the column varied according to the organic amendment and its proportion, which modified the apparent density of the soil (1,328±0,05 g•cm-3). The height of each column varied from 20 cm for the soil without amendment to 38,33±0,8 cm for the soil with 3% Lemna. After three months, the soil was treated with water (using the equivalent of the problem area infiltration rate), and was divided into three sections (7, 7 and 6 cm length). The soil from each section was air dried, sieved and its cationic exchange capacity, pH, cation solutions and extractable cations were measured to estimate RAS and PSI. An equivalent portion of each section was collected to compose a 50 g soil sample, and baseline respiration rate and tomato seedlings growth were recorded. Statistical differences (p<0,05) were observed among treatments for the variables under evaluation. Tukey test showed no differences among the proportions of organic amendments nor with the addition of gypsum phosphate to the organic amendments. The amendment which showed the lowest bioremediation potential was the Lemna, as a result of its high Na+ concentration. Under the conditions of this study, the soil column methodology used showed limitations to evaluate bioremediation because the control soil column, after being rinsed with water, also showed improvements as CE, RAS and PSI values were reduced. For some variables, the improvement noted in the control soil column surpassed those obtained with the soil amended with Lemna. Based on the best crop response amendment was vermicompost 3%.

Assessment of oral bioaccessibility of arsenic in playground soil in Madrid (Spain): A three-method comparison and implications for risk assessment

Three methodologies to assess As bioaccessibility were evaluated using playgroundsoil collected from 16 playgrounds in Madrid, Spain: two (Simplified Bioaccessibility Extraction Test: SBET, and hydrochloric acid-extraction: HCl) assess gastric-only bioaccessibility and the third (Physiologically Based Extraction Test: PBET) evaluates mouth–gastric–intestinal bioaccessibility. Aqua regia-extractable (pseudo total) As contents, which are routinely employed in riskassessments, were used as the reference to establish the following percentages of bioaccessibility: SBET – 63.1; HCl – 51.8; PBET – 41.6, the highest values associated with the gastric-only extractions. For Madridplaygroundsoils – characterised by a very uniform, weakly alkaline pH, and low Fe oxide and organic matter contents – the statistical analysis of the results indicates that, in contrast with other studies, the highest percentage of As in the samples was bound to carbonates and/or present as calcium arsenate. As opposed to the As bound to Fe oxides, this As is readily released in the gastric environment as the carbonate matrix is decomposed and calcium arsenate is dissolved, but some of it is subsequently sequestered in unavailable forms as the pH is raised to 5.5 to mimic intestinal conditions. The HCl extraction can be used as a simple and reliable (i.e. low residual standard error) proxy for the more expensive, time consuming, and error-prone PBET methodology. The HCl method would essentially halve the estimate of carcinogenic risk for children playing in Madridplaygroundsoils, providing a more representative value of associated risk than the pseudo-total concentrations used at present

Diffuse Soil Co2 Flux To Assess The Reliability Of Co2 Storage In The Mazarrón-Gañuelas Tertiary Basin (Spain)

Geological storage of CO2 is nowadays internationally considered as the most effective method for greenhouse gas emission mitigation, in order to minimize its effects on the global climatology. One of the main options is to store the CO2 in deep saline aquifers at more than 800 m depth, because it achieves its supercritical state. Among the most important aspects concerning the performance assessment of a deep CO2 geological repository is the evaluation of the CO2 leakage rate from the chosen storage geological formation. Therefore, it is absolutely necessary to increase the knowledge on the interaction among CO2, storage and sealing formations, as well as on the flow paths for CO2 and the physico-mechanical resistance of the sealing formation. Furthermore, the quantification of the CO2 leakage rate is essential to evaluate its effects on the environment. One way to achieve this objective is to study of CO2 leakage on natural analogue systems, because they can provide useful information about the natural performance of the CO2, which can be applied to an artificial CO2 geological storage. This work is focused on the retention capacity of the cap-rock by measuring the diffuse soil CO2 flux in a site selected based on: i) the presence of a natural and deep CO2 accumulation; ii) its structural geological characteristics; and iii) the nature of the cap-rocks. This site is located in the so-called Mazarrón-Gañuelas Tertiary Basin, in the Guadalentin Valley, province of Murcia (Spain) Therefore the main objective of this investigation has been to detect the possible leakages of CO2 from a deep saline aquifer to the surface in order to understand the capability of this area as a natural analogue for Carbon Capture and Sequestration (CCS). The results obtained allow to conclude that the geological sealing formation of the basin seems to be appropriate to avoid CO2 leakages from the storage formation.

CO2 soil flux baseline at the technological development plant for CO2 injection at Hontomin (Burgos, Spain)

From the end of 2013 and during the following two years, 20 kt of CO2sc are planned to be injected in a saline reservoir (1500 m depth) at the Hontomín site (NE Spain). The target aquifers are Lower Jurassic limestone formations which are sealed by Lower Cretaceous clay units at the Hontomín site (NE Spain). The injection of CO2 is part of the activities committed in the Technology Development phase of the EC-funded OXYCFB300 project (European Energy Program for Recovery – EEPR, http://www.compostillaproject.eu), which include CO2 injection strategies, risk assessment, and testing and validating monitoring methodologies and techniques. Among the monitoring works, the project is intended to prove that present-day technology is able to monitor the evolution of injected CO2 in the reservoir and to detect potential leakage. One of the techniques is the measurement of CO2 flux at the soil–atmosphere interface, which includes campaigns before, during and after the injection operations. In this work soil CO2 flux measurements in the vicinity of oil borehole, drilled in the eighties and named H-1 to H-4, and injection and monitoring wells were performed using an accumulation chamber equipped with an IR sensor. Seven surveys were carried out from November 2009 to summer 2011. More than 4000 measurements were used to determine the baseline flux of CO2 and its seasonal variations. The measured values were low (from 5 to 13 g m−2 day−1) and few outliers were identified, mainly located close to the H-2 oil well. Nevertheless, these values cannot be associated to a deep source of CO2, being more likely related to biological processes, i.e. soil respiration. No anomalies were recognized close to the deep fault system (Ubierna Fault) detected by geophysical investigations. There, the CO2 flux is indeed as low as other measurement stations. CO2 fluxes appear to be controlled by the biological activity since the lowest values were recorded during autumn-winter seasons and they tend to increase in warm periods. Two reference CO2 flux values (UCL50 of 5 g m−2 d−1 for non-ploughed areas in autumn–winter seasons and 3.5 and 12 g m−2 d−1 for in ploughed and non-ploughed areas, respectively, in spring–summer time, and UCL99 of 26 g m−2 d−1 for autumn–winter in not-ploughed areas and 34 and 42 g m−2 d−1 for spring–summer in ploughed and not-ploughed areas, respectively) were calculated. Fluxes higher than these reference values could be indicative of possible leakage during the operational and post-closure stages of the storage project.

Diffuse soil CO2 flux to assess the reliability of CO2 storage the reliability of CO2 storage in the Mazarrón-Gañuelas Tertiary Basin (Spain)

In the framework of a global investigation of the Spanish natural analogues of CO2 storage and leakage, four selected sites from the Mazarrón?Gañuelas Tertiary Basin (Murcia, Spain) were studied for computing the diffuse soil CO2 flux, by using the accumulation chamber method. The Basin is characterized by the presence of a deep, saline, thermal (?47 ?C) CO2-rich aquifer intersected by two deep geothermal exploration wells named ?El Saladillo? (535 m) and ?El Reventón? (710 m). The CO2 flux data were processed by means of a graphical?statistical method, kriging estimation and sequential Gaussian simulation algorithms. The results have allowed concluding that the Tertiary marly cap-rock of this CO2-rich aquifer acts as a very effective sealing, preventing any CO2 leak from this natural CO2 storage site, being therefore an excellent scenario to guarantee, by analogy, the safety of a CO2 storage.

Approach to the potential production of giant reed in surplus saline lands of Spain

Growing energy crops on marginal land has been promoted as a way of ensuring that biomass production involves an acceptable and sustainable use of land. Saline and saline-prone agricultural lands represent an opportunity for growing energy crops avoiding the displacement of food production and contributing to restoration of degraded land. Giant reed (Arundo donax L.) is a perennial grass that has been proposed as a promising energy crop for lignocellulosic biomass production while its tolerance to salinity has been proved. In this work, the identification of surplus saline lands that could be irrigated with saline waters for growing tolerant-energy crops (giant reed) in the mainland of Spain and the assessment of the agronomically attainable yield in these limiting growing conditions were undertaken. To this purpose, a GIS analysis was conducted using geodatabases related to saline areas, agro-climatic conditions, irrigation water requirements, agricultural land availability, restrictions regarding the range of electrical conductivity tolerated by the crop, competition with agro-food crops and irrigation water provisions. According to the approach developed, the irrigated and saline agricultural area available and suitable for biomass production from giant reed amounted up to 34 412 ha. The agronomically attainable yield in these limiting conditions was estimated at 12.7 – 22.2 t dm ha−1 yr−1 and the potential production of lignocellulosic biomass, 597 338 t dm yr−1. The methodology followed in this study can be applied to other target regions; it allows the identification of this type of marginal lands, where salinity-tolerant plant species could be grown for bioenergy purposes, avoiding competition with agro-food crops, and where soil restoration measurements should be undertaken.