Challenges for future of Natural Spaces of Canary Islands, Spain

The preservation of biodiversity is a fundamental objective of a ll policies related to a more sustainable development in any modern society. The rain forest and pine forests are two unique Canarian ecosystems with high importance to global biodiversity, holding a large number of endemic species and subspecies that is a priority to preserve. In this work the challenges that will face the natural areas of the Canary Islands are studied, as well as their fundamental value for economic and environmental development of the islands.

Discrete Multi-Criteria Methods for lands use and conservation planning on La Colacha in Arroyos Menores (Río Cuarto, Province of Córdoba, Argentina)

The study area is La Colacha sub-basins from Arroyos Menores basins, natural areas at West and South of Río Cuarto in Province of Córdoba of Argentina, fertile with loess soils and monsoon temperate climate, but with soil erosions including regressive gullies that degrade them progressively. Cultivated gently since some hundred sixty years, coordinated action planning became necessary to conserve lands while keeping good agro-production. The authors had improved data on soils and on hydrology for the study area, evaluated systems of soil uses and actions to be recommended and applied Decision Support Systems (DSS) tools for that, and were conducted to use discrete multi-criteria models (MCDM) for the more global views about soil conservation and hydraulic management actions and about main types of use of soils. For that they used weighted PROMETHEE, ELECTRE, and AHP methods with a system of criteria grouped as environmental, economic and social, and criteria from their data on effects of criteria. The alternatives resulting offer indication for planning depending somehow on sub basins and on selections of weights, but actions for conservation of soils and water management measures are recommended to conserve the basins conditions, actually sensibly degrading, mainly keeping actual uses of the lands.

Uso de una red inalámbrica de sensores para estimar riesgo de incendio

Una red inalámbrica de sensores (Wireless Sensor Network, WSN) constituye un sistema de comunicación de datos flexible utilizado como alternativa a las redes cableadas o como extensión de éstas y está compuesta por elementos de cómputo, medición y comunicación, que permiten al administrador instrumentar, observar y reaccionar a eventos y fenómenos en un ambiente específico. Una de las aplicaciones de estas redes es su uso en sistemas de predicción y prevención de incendios en áreas naturales. Su implementación se basa en el despliegue de sensores inalámbricos, realizado en una zona de riesgo de incendio para que puedan recolectar información sobre parámetros ambientales como temperatura, humedad, luz o presión, entre otros. Desde una estación base (o nodo "sumidero"), se suministra la información de los sensores a un centro de monitorización y control de forma estructurada. En este centro la información recibida puede ser analizada, procesada y visualizada en tiempo real. Desde este centro de control se puede controlar también la red WSN modificando el comportamiento de los sensores según el nivel de riesgo de incendio detectado. Este proyecto se basa en el diseño, implementación y despliegue de una red inalámbrica de sensores en un entorno simulado para observar su comportamiento en diferentes situaciones y mostrar su eficacia ante un posible caso de incendio. La implementación de este sistema denominado Sistema de Estimación de Riesgo de Incendio Utilizando una WSN (SERIUW) , junto con el desarrollado, en paralelo, de otro proyecto denominado Sistema de Control y Visualización de Información sobre Riesgo de Incendio (SCVIRI) que implementa las funciones de los centros de monitorización y control, conforman un Sistema de Anticipación y Seguimiento de Fuegos (SASF). Se han realizado pruebas de funcionalidad y eficacia, incluidas en la presente memoria del sistema unitario de en conjunto (ambos proyectos), en un entorno controlado simulado. Este sistema es una solución para la lucha contra los incendios forestales ya que predice y previene, de forma temprana, posibles incendios en las áreas naturales bajo supervisión. Ante un evento de incendio declarado este sistema es un poderoso instrumento de apoyo permitiendo, por un lado, generar alertas automáticas (con localización y gravedad de fuegos detectados) y por el otro, hacer un seguimiento del incendio con mapas en tiempo real (con su consecuente apoyo para la protección e información con las brigadas de bomberos en las zonas activas). ABSTRACT. A wireless sensor network (WSN) is a flexible data communication system used as an alternative to wired networks or as an extension of them and consists of nodes that perform calculation, measurement and communication activities. This allows the administrator to observe and react to events and phenomena in a specific environment. One application of these networks is fire prediction and prevention in natural areas. Its implementation is based on a deployment of wireless sensors, in a fire risk area, capable of collecting information such as temperature, humidity, luminance and pressure. A base station (or "sink") sends the collected information to a monitoring and control center following a structured format. At this center, the information received can be analyzed, processed and displayed in real time with monitoring systems. From this control center the WSN can also be controlled by changing the sensors behavior according to the level of fire risk detection. This project is based on the design, implementation and deployment of a Wireless Sensor Network (WSN) in a simulated environment in order to observe its behavior in different situations and show its effectiveness against a possible fire environment. The implementation of this system called SERIUW, has been done in parallel with other system, called SCVIRI, which has been developed in another project that implements the functions of monitoring and control center. Together, these two systems, make up a general system of anticipation and monitoring of fires. Functionality and performance tests have been performed on the overall system, in a controlled and simulated environment. The results of these tests are included in this document. The global system is a solution to fight the forest fires because it makes it easier to predict and prevent, early, possible fires in natural areas under supervision. This sytem can be a powerful tool since, before a fire event is declared, it generates automatic alerts (including location and severity information) and allows the real-time motorization of fire evolution integrated with maps. This could be also very useful for the support protection and information of fire brigades in zones in which a fire is already active.

Sistema de control y visualización de información sobre riesgo de incendios

Una red inalámbrica de sensores (Wireless Sensor Network, WSN) constituye un sistema de comunicación de datos flexible utilizado como alternativa a las redes cableadas o como extensión de éstas. Una de las aplicaciones de estas redes es para su uso en sistemas de predicción y prevención de incendios en áreas naturales. Su implementación se basa en el despliegue de sensores inalámbricos, realizado en una zona de riesgo de incendio que puedan recolectar información tal como temperatura, humedad y presión. Desde una estación base (o nodo "sumidero"), se suministra la información de los sensores a un centro de monitorización y control de forma estructurada. En estos centros la información recibida puede ser analizada, procesada y visualizada en tiempo real. Desde este centro de control se puede controlar también la red WSN modificando el comportamiento de los sensores según el nivel de riesgo de incendio detectado. Este proyecto se basa en el diseño, desarrollo e implementación de un Sistema de Control y Visualización de Información sobre Riesgo de Incendio (SCVIRI), que implementa las funciones de los centros de monitorización y control. La implementación de este sistema, junto con el desarrollado, en paralelo, de otro proyecto denominado Sistema de Estimación de Riesgo de Incendio Utilizando una WSN (SERIUW) que implementa la emulación de la red WSN, conforman un sistema general de anticipación y seguimiento de Fuegos. Se han realizado pruebas de funcionalidad y eficacia, incluidas en la presente memoria del sistema general (ambos proyectos), en un entorno controlado simulado. Este sistema es una solución para la lucha contra los incendios forestales ya que predice y previene, de forma temprana, posibles incendios en las áreas naturales bajo supervisión. Ante un evento de incendio declarado este sistema es un poderoso instrumento de apoyo permitiendo, por un lado, generar alertas automáticas (con localización y gravedad de fuegos detectados) y por el otro, hacer un seguimiento del incendio con mapas en tiempo real (con su consecuente apoyo para la protección e información con las brigadas de bomberos en las zonas activas). ABSTRACT. A wireless sensor network (WSN) is a flexible data communication system used as an alternative to wired networks or as an extension of them. One possible application of these networks is related to fire prediction and prevention in natural areas. Its implementation is based on a deployment of wireless sensors, in an area with high or moderate fire risk, to collect information such as temperature, humidity, luminance and pressure. A base station (or "sink") sends the collected information to a monitoring and control center according to an agreed structured format. At this center, the information received can be analyzed, processed and displayed in real time by using monitoring systems. From this control center the WSN can also be controlled by changing the sensors behavior in consistence with the detected level of fire risk. The work carried out in this project consists on the design, development and implementation of a system named SCVIRI, which implements the functions of the aforementioned monitoring and control center. This system works in connection with other one, called SERIUW, which has been developed in a different project and implements the WSN in an emulated environment. These two systems working together make up a general system of anticipation and monitoring of fires. This document also includes the functionality and performance tests performed on the overall system in a controlled and simulated environment. The global system is a solution that makes it easier to predict and prevent possible fires in natural areas under supervision. This system can be a powerful tool since, before a fire event is declared, it generates automatic alerts (including location and severity information) and allows the real-time motorization of fire evolution and its graphical visualization on maps. This could be also very useful for providing fire brigades with support, protection and information in zones in which a fire is already active.

Land use modelling and the role of stakeholders in natural protected areas: the case of Doñana national park, Spain

Doñana, a National Park since 1969, a UNESCO site since 1994 among other protected area designations of national and international character, is a coastal dune and marshland ecosystem of outstanding importance for biodiversity and conservation at the mouth of the Guadalaquivir River, Southwest Spain. However, the Doñana natural area is seriously threatened by global change factors such as humanly induced climate change, habitat loss, overexploitation of ecosystem services, and pollution. Not all stakeholders are convinced of the benefits of the national park, and management of Doñana, its environs and watershed are the subject of intense disagreement. This interplay between natural characteristics of great value with intense human pressure makes Doñana a fascinating workshop for the study of global human environment interactions. Here, we discuss the role of stakeholders in the application of a cellular automatabased model to Doñana and its environs and present the results of a series of exercises undertaken with stakeholders to parametrize the model, something often done by researchers without stakeholder engagement. By engaging with stakeholders early in the project, feedback generated from workshops contributes to model development. Stakeholders are therefore contributors of empirical data for the model as well as independent evaluators providing local and specialist knowledge.

Cálculo de la recarga natural en grandes áreas, en función de la litología y la precipitación = Calculation of natural recharge in large areas, as a function of lithology and rainfall

En una región amplia como España se demuestra —mediante inferencias estadísticas sobre una muestra completa de 875 manantiales en los que se conoce su caudal medio y la litología de su área de alimentación y que han sido agrupados en regiones de distinta pluviometría— que la recarga media anual es una fracción fija de la precipitación media para cada litología. Se han establecido así unas tasas de recarga respecto de la precipitación para seis grupos litológicos de diferente permeabilidad: arenas, gravas y formaciones aluviales en general, 8.3%; conglomerados, 5.6%; areniscas, 7.3%; calizas y dolomías, 34.3%; margas, margocalizas, limos y arcillas, 3.3%; otras rocas, 1.3%. Teniendo en cuenta la representatividad de España, la cual tiene una gran variabilidad de litología, pluviometría, topografía, etcétera, estas tasas de recarga respecto de la precipita-ción son probablemente valores cuasi universales que pueden ser utilizados para estimar la recarga media o los recursos hídricos subterráneos medios de regiones amplias en cualquier parte del mundo, salvo en regiones especiales, como las que tienen permafrost, por ejemplo. En todo caso, estas tasas de recarga podrían ser retocadas para cada región según sus particulares características. Los datos de precipitación y litología son muy corrientes, por lo que el método puede ser ampliamente utilizado para completar balances hidráulicos.In a region as large as Spain, annual mean recharge is shown to be a fixed proportion of the mean rainfall for each lithology. This determination is based on statistical inferences from a complete sample of 875 springs for which mean flow and catchment areas are known and which have been grouped into distinct rainfall regions. Recharge rates have thus been established with respect to rainfall for six lithological groups with different permeability: sands, gravels and generally alluvial formations, 8.3%; conglomerates, 5.6%; sandstones, 7.3%; limestone and dolomite 34.3%; marls, marly limestones, silts and clays, 3.3%; and hard rocks, 1.3%. Considering the representativeness of Spain, which is large in size and has a highly varied lithology, topography and rainfall, these recharge rates for rainfall are probably quasi-universal values that can be used to estimate average recharge or average groundwater resources of large regions in any part of the world (except in special cases such as areas with permafrost, for example). For any case, these recharge rates can be adapted to each region according to its particular characteristics. Rainfall and lithology data are very common, and so the method can be widely used to calculate hydraulic balances.

Volume, Surface, Connectivity and Size Distribution of Soil Pore Space in CT Images: Comparison of Samples at Different Depths from Nearby Natural and Tillage Areas

The study of soil structure, i.e., the pores, is of vital importance in different fields of science and technology. Total pore volume (porosity), pore surface, pore connectivity and pore size distribution are some (probably the most important) of the geometric measurements of pore space. The technology of X-ray computed tomography allows us to obtain 3D images of the inside of a soil sample enabling study of the pores without disturbing the samples. In this work we performed a set of geometrical measures, some of them from mathematical morphology, to assess and quantify any possible difference that tillage may have caused on the soil. We compared samples from tilled soil with samples from a soil with natural vegetation taken in a very close area. Our results show that the main differences between these two groups of samples are total surface area and pore connectivity per unit pore volume.

Planning and Management of Mobility in Natural Protected Areas

The paper describes some relevant results of an on-going research aiming to elaborate a methodology to help the mobility management in natural parks, compatible with their protection missions: it has been developed a procedure to reproduce the mobility-environment relationships in various operational conditions. The final purpose is the identification of: a) the effects of various choices in transport planning, both at long term and strategic level; b) the most effective policies of mobility management. The work is articulated in the following steps: 1) definition of protected area on the basis of ecological and socio-economic criteria and legislative constraints; 2) analysis of mobility needs in the protected areas; 3) reconstruction of the state of the art of mobility management in natural parks at European level; 4) analysis of used traffic flows measurement methods; 5) analysis of environmental impacts due to transport systems modelling (air pollution and noise only); 6) identification of mitigation measures to be potentially applied. The whole methodology has been tested and validated on Italian case studies: i) the concerned area has been zoned according to the land-use peculiarities; ii) the local situations of transport infrastructure (roads and parking), services (public transport systems) and rules (traffic regulations) have been mapped with references to physical and functional attributes; iii) the mobility, both systematic and touristic, has been represented in an origin-destination matrix. By means of an assignment model the flows have been distributed and the corresponding average speeds to quantify gaseous and noise emissions was calculated, the criticalities in the reference scenario have been highlighted, as well as some alternative scenarios, including both operational and infrastructural measures have been identified. The comparison between projects and reference scenario allowed the quantification of effects (variation of emissions) for each scenario and a selection of the most effective management actions to be taken.

Planning and management of mobility in natural protected areas

The final purpose is the identification of: a) the effects of various choices in transport planning, both at long term and strategic level; b) the most effective policies of mobility management. The preliminary work was articulated in the following steps: 1) definition of protected area on the basis of ecological and socio-economic criteria and legislative constraints; 2) analysis of mobility needs in the protected areas; 3) reconstruction of the state of the art of mobility management in natural parks at European level; 4) analysis of used traffic flows measurement methods; 5) analysis of environmental impacts due to transport systems modelling (limited to air pollution and noise); 6) identification of mitigation measures to the potentially applied. The whole methodology has been firstly tested on the case study of the National Park of ?Gran Sasso and Monti della Laga? and further validated on the National Park of ?Gargano?, both located Italy: i) the concerned area has been zoned according to the land-use peculiarities; ii) the local situations of transport infrastructure (roads and parking), services (public transport systems) and rules (traffic regulations) have been mapped with references to physical and functional attributes; iii) the mobility, both systematic and touristic, has been synthetically represented in an origin-destination matrix. By means of an assignment model it has been determined the distribution of flows and the corresponding average speeds to quantify gaseous and noise emissions. On this basis the environmental criticalities in the reference scenario have been highlighted, as well as some alternative scenarios including both operational and infrastructural measures have been identified. The comparison between the projects and the reference scenario allowed the quantification of the effects (variation of emissions) for each scenario and a selection of the most effective management actions to be taken.

An integral model for natural regeneration of Pinus pinea L. in the Northern Plateau (Spain) = Modelo integral de regeneración natural para Pinus pinea L. en la Meseta Norte (España)

Natural regeneration is an ecological key-process that makes plant persistence possible and, consequently, it constitutes an essential element of sustainable forest management. In this respect, natural regeneration in even-aged stands of Pinus pinea L. located in the Spanish Northern Plateau has not always been successfully achieved despite over a century of pine nut-based management. As a result, natural regeneration has recently become a major concern for forest managers when we are living a moment of rationalization of investment in silviculture. The present dissertation is addressed to provide answers to forest managers on this topic through the development of an integral regeneration multistage model for P. pinea stands in the region. From this model, recommendations for natural regeneration-based silviculture can be derived under present and future climate scenarios. Also, the model structure makes it possible to detect the likely bottlenecks affecting the process. The integral model consists of five submodels corresponding to each of the subprocesses linking the stages involved in natural regeneration (seed production, seed dispersal, seed germination, seed predation and seedling survival). The outputs of the submodels represent the transitional probabilities between these stages as a function of climatic and stand variables, which in turn are representative of the ecological factors driving regeneration. At subprocess level, the findings of this dissertation should be interpreted as follows. The scheduling of the shelterwood system currently conducted over low density stands leads to situations of dispersal limitation since the initial stages of the regeneration period. Concerning predation, predator activity appears to be only limited by the occurrence of severe summer droughts and masting events, the summer resulting in a favourable period for seed survival. Out of this time interval, predators were found to almost totally deplete seed crops. Given that P. pinea dissemination occurs in summer (i.e. the safe period against predation), the likelihood of a seed to not be destroyed is conditional to germination occurrence prior to the intensification of predator activity. However, the optimal conditions for germination seldom take place, restraining emergence to few days during the fall. Thus, the window to reach the seedling stage is narrow. In addition, the seedling survival submodel predicts extremely high seedling mortality rates and therefore only some individuals from large cohorts will be able to persist. These facts, along with the strong climate-mediated masting habit exhibited by P. pinea, reveal that viii the overall probability of establishment is low. Given this background, current management –low final stand densities resulting from intense thinning and strict felling schedules– conditions the occurrence of enough favourable events to achieve natural regeneration during the current rotation time. Stochastic simulation and optimisation computed through the integral model confirm this circumstance, suggesting that more flexible and progressive regeneration fellings should be conducted. From an ecological standpoint, these results inform a reproductive strategy leading to uneven-aged stand structures, in full accordance with the medium shade-tolerant behaviour of the species. As a final remark, stochastic simulations performed under a climate-change scenario show that regeneration in the species will not be strongly hampered in the future. This resilient behaviour highlights the fundamental ecological role played by P. pinea in demanding areas where other tree species fail to persist.

Development of mathematical models to elaborate strategies, select alternatives and development of plans for adaptation of communities to climate change in different geographical areas including costs to implement it.

There is evidence that the climate changes and that now, the change is influenced and accelerated by the CO2 augmentation in atmosphere due to combustion by humans. Such ?Climate change? is on the policy agenda at the global level, with the aim of understanding and reducing its causes and to mitigate its consequences. In most countries and international organisms UNO (e.g. Rio de Janeiro 1992), OECD, EC, etc . . . the efforts and debates have been directed to know the possible causes, to predict the future evolution of some variable conditioners, and trying to make studies to fight against the effects or to delay the negative evolution of such. The Protocol of Kyoto 1997 set international efforts about CO2 emissions, but it was partial and not followed e.g. by USA and China . . . , and in Durban 2011 the ineffectiveness of humanity on such global real challenges was set as evident. Among all that, the elaboration of a global model was not boarded that can help to choose the best alternative between the feasible ones, to elaborate the strategies and to evaluate the costs, and the authors propose to enter in that frame for study. As in all natural, technological and social changes, the best-prepared countries will have the best bear and the more rapid recover. In all the geographic areas the alternative will not be the same one, but the model must help us to make the appropriated decision. It is essential to know those areas that are more sensitive to the negative effects of climate change, the parameters to take into account for its evaluation, and comprehensive plans to deal with it. The objective of this paper is to elaborate a mathematical model support of decisions, which will allow to develop and to evaluate alternatives of adaptation to the climatic change of different communities in Europe and Latin-America, mainly in especially vulnerable areas to the climatic change, considering in them all the intervening factors. The models will consider criteria of physical type (meteorological, edaphic, water resources), of use of the ground (agriculturist, forest, mining, industrial, urban, tourist, cattle dealer), economic (income, costs, benefits, infrastructures), social (population), politician (implementation, legislation), educative (Educational programs, diffusion) and environmental, at the present moment and the future. The intention is to obtain tools for aiding to get a realistic position for these challenges, which are an important part of the future problems of humanity in next decades.

Development of mathematical models to elaborate strategies, to select alternatives and the development of plans for the adaptation of communities to climate change in different geographical areas including costs to implement it

Climate change is on the policy agenda at the global level, with the aim of understanding and reducing its causes and to mitigate its consequences. In most of the countries and international organisms UNO, OECD, EC, etc … the efforts and debates have been directed to know the possible causes, to predict the future evolution of some variable conditioners, and trying to make studies to fight against the effects or to delay the negative evolution of such. Nevertheless, the elaboration of a global model was not boarded that can help to choose the best alternative between the feasible ones, to elaborate the strategies and to evaluate the costs. As in all natural, technological and social changes, the best-prepared countries will have the best bear and the more rapid recover. In all the geographic areas the alternative will not be the same one, but the model should help us to make the appropriated decision. It is essential to know those areas that are more sensitive to the negative effects of climate change, the parameters to take into account for its evaluation, and comprehensive plans to deal with it. The objective of this paper is to elaborate a mathematical model support of decisions, that will allow to develop and to evaluate alternatives of adaptation to the climatic change of different communities in Europe and Latin-America, mainly, in vulnerable areas to the climatic change, considering in them all the intervening factors. The models will take into consideration criteria of physical type (meteorological, edaphic, water resources), of use of the ground (agriculturist, forest, mining, industrial, urban, tourist, cattle dealer), economic (income, costs, benefits, infrastructures), social (population), politician (implementation, legislation), educative (Educational programs, diffusion), sanitary and environmental, at the present moment and the future.

El cemento natural en el Madrid del S. XIX

El cemento natural fue patentado en Inglaterra en 1796, pero no llegó a España hasta 1835, aunque todavía se discute dónde comenzó la producción nacional, ya que surgió casi simultáneamente en el País Vasco (Zumaya y Rezola) y en Cataluña (San Celoní y San Juan de las Abadesas). Desde entonces fue ampliamente utilizado en la ornamentación arquitectónica durante el siglo XIX y principios del siglo XX en Madrid. Con su llegada reemplazó materiales tradicionales que se utilizaban anteriormente, como las cales aéreas e hidráulicas, y el yeso. Sin embargo, su uso no se alargó en el tiempo, pues pronto fue sustituido por el cemento Portland. En la actualidad, lo que queda de el son cientos de " testimonios de piedra" que hay que conservar y reparar ocasionalmente de la mejor manera posible. Las propiedades finales del cemento natural dependían en gran medida de las materias primas utilizadas y su temperatura de obtención y en general, se caracterizaba por un fraguado rápido (aproximadamente de 15 minutos), una buena resistencia y un agradable color ocre. Esta comunicación muestra las características de las fachadas madrileñas del S.XIX recubiertas con morteros de cemento natural, su estado de conservación y deterioro, así como los daños producidos como resultado de intervenciones desafortunadas en las que han empleado materiales no compatibles con este cemento.

Conservation of endangered Lupinus mariae-josephae in its natural habitat by inoculation with selected, native Bradyrhizobium strains

Lupinus mariae-josephae is a recently discovered endemism that is only found in alkaline-limed soils, a unique habitat for lupines, from a small area in Valencia region (Spain). In these soils, L. mariae-josephae grows in just a few defined patches, and previous conservation efforts directed towards controlled plant reproduction have been unsuccessful. We have previously shown that L. mariae-josephae plants establish a specific root nodule symbiosis with bradyrhizobia present in those soils, and we reasoned that the paucity of these bacteria in soils might contribute to the lack of success in reproducing plants for conservation purposes. Greenhouse experiments using L. mariae-josephae trap-plants showed the absence or near absence of L. mariae-josephae-nodulating bacteria in ‘‘terra rossa’’ soils of Valencia outside of L. mariaejosephae plant patches, and in other ‘‘terra rossa’’ or alkaline red soils of the Iberian Peninsula and Balearic Islands outside of the Valencia L. mariae-josephae endemism region. Among the bradyrhizobia able to establish an efficient symbiosis with L. mariae-josephae plants, two strains, LmjC and LmjM3 were selected as inoculum for seed coating. Two planting experiments were carried out in consecutive years under natural conditions in areas with edapho-climatic characteristics identical to those sustaining natural L. mariae-josephae populations, and successful reproduction of the plant was achieved. Interestingly, the successful reproductive cycle was absolutely dependent on seedling inoculation with effective bradyrhizobia, and optimal performance was observed in plants inoculated with LmjC, a strain that had previously shown the most efficient behavior under controlled conditions. Our results define conditions for L. mariae-josephae conservation and for extension to alkaline-limed soil habitats, where no other known lupine can thrive.

CO2and Rn degassing from the natural analog of Campo de Calatrava(Spain): Implications for monitoring of CO2storage sites

Natural analogs offer a valuable opportunity to investigate the long-term impacts associated with thepotential leakage in geological storage of CO2.Degassing of CO2and radon isotopes (222Rn?220Rn) from soil, gas vents and thermal water dischargeswas investigated in the natural analog of Campo de Calatrava Volcanic Field (CCVF; Central Spain) todetermine the CO2?Rn relationships and to assess the role of CO2as carrier gas for radon. Furthermore,radon measurements to discriminate between shallow and deep gas sources were evaluated under theperspective of their applicability in monitoring programs of carbon storage projects.CO2flux as high as 5000 g m?2d?1and222Rn activities up to 430 kBq m?3were measured;220Rn activi-ties were one order of magnitude lower than those of222Rn. The222Rn/220Rn ratios were used to constrainthe source of the Campo de Calatrava soil gases since a positive correlation between radon isotopic ratiosand CO2fluxes was observed. Thus, in agreement with previous studies, our results indicate a deepmantle-related origin of CO2for both free and soil gases, suggesting that carbon dioxide is an efficientcarrier for Rn. Furthermore, it was ascertained that the increase of222Rn in the soil gases was likely pro-duced by two main processes: (i) direct transport by a carrier gas, i.e., CO2and (ii) generation at shallowlevel due to the presence of relatively high concentrations of dissolved U and Ra in the thermal aquiferof Campo de Calatrava.The diffuse CO2soil flux and radon isotopic surveys carried out in the Campo de Calatrava VolcanicFields can also be applicable to geochemical monitoring programs in CCS (Carbon Capture and Storage)areas as these parameters are useful to: (i) constrain CO2leakages once detected and (ii) monitor both theevolution of the leakages and the effectiveness of subsequent remediation activities. These measurementscan also conveniently be used to detect diffuse leakages.