128 results on '"Valladolid, María"'
Search Results
2. N and P behaviour in alluvial aquifers and in the soil solution of their catchment areas: How land use and the physical environment contribute to diffuse pollution
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Arauzo, Mercedes, Valladolid, María, García, Gema, and Andries, Delia M.
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- 2022
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3. A histological procedure for the study of insect chitinized tissues in light microscopy
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Gallardo, Manuela and Valladolid, María
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- 2025
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4. Assessment of the risks of N–loss to groundwater from data on N–balance surplus in Spanish crops: An empirical basis to identify Nitrate Vulnerable Zones
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Arauzo, Mercedes, García, Gema, and Valladolid, María
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- 2019
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5. Diffuse Pollution Pathways are not the same for N and P Compounds
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Arauzo, Mercedes [0000-0003-4113-8797], Valladolid, María [0000-0002-7405-1105], Arauzo, Mercedes, Valladolid, María, Arauzo, Mercedes [0000-0003-4113-8797], Valladolid, María [0000-0002-7405-1105], Arauzo, Mercedes, and Valladolid, María
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- 2023
6. El derecho a ser padres: Rompiendo los paradigmas del derecho de familia, bajo una concepción legal o ilegal
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Samaniego-Quiguiri, Delia Paulina, primary, Bonilla-Morejón, Diego Marcelo, additional, Martínez-Tapia, José David, additional, Navarrete-Valladolid, María Isabel, additional, Solis-Miranda, Diego Fernando, additional, Zambrano-Villacrés, Dayana Estefanya, additional, Bucheli-Cárdenas, Cristhian Marcelo, additional, Murillo-Ramos, Franklin Remigio, additional, Erazo-Zela, Víctor Hugo, additional, and Guala-Agualongo, Carlos Javier, additional
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- 2023
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7. Complete data of the DNA sequences used for the study of the Rhyacophila fasciata Group (Insecta, Trichoptera, Rhyacophilidae) in Europe
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Valladolid, María [0000-0002-7405-1105], Arauzo, Mercedes [0000-0003-4113-8797], Dorda, Beatriz A. [0000-0002-2741-1841], París, Mercedes [0000-0002-0161-7278], Rey Fraile, Isabel [0000-0002-2122-5124], Valladolid, María, Arauzo, Mercedes, Dorda, Beatriz A., París, Mercedes, Fraile, Isabel, Valladolid, María [0000-0002-7405-1105], Arauzo, Mercedes [0000-0003-4113-8797], Dorda, Beatriz A. [0000-0002-2741-1841], París, Mercedes [0000-0002-0161-7278], Rey Fraile, Isabel [0000-0002-2122-5124], Valladolid, María, Arauzo, Mercedes, Dorda, Beatriz A., París, Mercedes, and Fraile, Isabel
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The table lists all the DNA sequences (COI mit) studied to date, of specimens belonging to the Rhyacophila fasciata Group and published in different articles. Due to the progressive increase of sequences obtained in successive publications, they have been compiled in this table for consultation by researchers interested in this material. The document will be updated with new sequences as the following studies are published., The table includes the following information: species and specimen number, sex, locality of collection, latitudinal and longitudinal geographical coordinates, altitude, accession numbers to GenBank, voucher number from Tissues and DNA Collection, voucher number of Entomological Collection, both from Museo Nacional de Ciencias Naturales, Consejo Superior de Investigaciones Científicas (MNCN-CSIC), accession number and/or collection in other Collections, and legit (Leg.) of specimens.
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- 2022
8. The Rhyacophila fasciata Species Complex (Trichoptera: Rhyacophilidae) in Central Europe with description of a new species, Rhyacophila loeffleri Valladolid & Waringer, n. sp., based on morphological, genetic and ecological evidence
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Ministry of Culture (Czech Republic), Consejo Superior de Investigaciones Científicas (España), Valladolid, María, Waringer, Johann, Arauzo, Mercedes, Chvojka, Pavel, Dorda, Beatriz A., Komzák, Petr, Lodovici, Omar, Rey, Isabel, Ministry of Culture (Czech Republic), Consejo Superior de Investigaciones Científicas (España), Valladolid, María, Waringer, Johann, Arauzo, Mercedes, Chvojka, Pavel, Dorda, Beatriz A., Komzák, Petr, Lodovici, Omar, and Rey, Isabel
- Abstract
[EN] The morphology of the larva, pupa, male, and female of Rhyacophila loeffleri Valladolid & Waringer, n. sp., from Austria, Czech Republic, France, and Italy is described. Data from molecular analysis are also provided, based on mitochondrial cytochrome c oxidase subunit I (mtCOI), including sequences from German and Swiss specimens, and compared with those of samples of the nominate species R. fasciata Hagen 1859, as well as with other species and subspecies in the Rhyacophila fasciata Species Complex: R. septentrionis McLachlan 1865, R. denticulata McLachlan 1879, R. sociata Navás 1916, R. kykladica Malicky & Sipahiler 1993, R. delici Kučinić & Valladolid 2020, R. fasciata viteceki Valladolid & Kučinić 2020 and R. macedonica Karaouzas, Valladolid & Ibrahimi 2022. Our study revealed morphological differences between R. fasciata and R. loeffleri, as well as genetic differences among the other taxa of the R. fasciata Complex, supporting the recognition of R. loeffleri as a new species. Also, Rhyacophila fasciata viteceki is recognized as a distinct species, R. viteceki (status promotus), based on results of the molecular analysis., [ES] Se ha estudiado la morfología de la larva, pupa, macho y hembra de Rhyacophila loeffleri Valladolid & Waringer (n. sp.) de Austria, República Checa, Francia e Italia. Se incluyen datos del análisis molecular del gen mitocondrial citocromo oxidasa subunidad I (COImt), incluidas secuencias de especímenes alemanes y suizos, que se compararon con muestras de la especie nominal R. fasciata Hagen 1859, así como con otras muestras de especies y subespecies del Complejo Rhyacophila fasciata: R. septentrionis McLachlan, 1865, R. denticulata McLachlan 1879, R. sociata Navás 1916, R kykladica Malicky & Sipahiler 1993, R. delici Kučinić & Valladolid 2020, R. fasciata viteceki Valladolid & Kučinić 2020 y R. macedonica Karaouzas, Valladolid & Ibrahimi 2022. Nuestro estudio reveló diferencias morfológicas entre R. fasciata y R. loeffleri, así como diferencias genéticas entre los otros taxones del Complejo R. fasciata, lo que apoya el reconocimiento de R. loeffleri como una nueva especie. Además, se reconoce a Rhyacophila fasciata viteceki como una especie distinta, R. viteceki (status promotus), basada en los resultados del análisis molecular.
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- 2023
9. Estudio del estado ecológico del río Yaga (Parque Nacional de Ordesa y Monte Perdido, verano de 2020) mediante índices de macroinvertebrados
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Valladolid, María, Rodríguez Cejas, Marina, Valladolid, María, and Rodríguez Cejas, Marina
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[ES] Como resultado de los requerimientos de la Directiva Marco del Agua es necesario llevar a cabo la evaluación y seguimiento de la calidad de las aguas de un territorio para su diagnóstico y protección. En el presente trabajo se determina el estado ecológico del río Yaga, situado en el Parque Nacional de Ordesa y Monte Perdido, en los meses de verano del año 2020 mediante el uso de macroinvertebrados acuáticos como indicadores biológicos. Se obtuvieron las muestras durante un programa de voluntariado realizado por la Asociación de Ciencias Ambientales, en el cual se seleccionaron tres puntos de muestreo a lo largo del río, aunque solo se pudieron muestrear dos. A partir de estas muestras, se calcularon los índices IBMWP, IASPT, NFAM, NPLE y EPT; los cuales mostraron un estado Muy Bueno-Bueno en el punto OR-YA2 y Muy Bueno en el punto OR-YA3. Esto nos indica que el río Yaga presenta una buena calidad de sus aguas y no se encuentra significativamente contaminado ni perturbado., [EN] As the Water Framework Directive establishes, it is necessary to implement an evaluation and monitoring of one territory’s rivers water quality in order to elaborate a diagnosis and guarantee its protection. The current study determines the ecological status of Yaga River, located in the Ordesa y Monte Perdido National Park, in the summer of the year 2020, using aquatic macroinvertebrates as biological indicators. The macroinvertebrate samples were collected during a volunteering program of the Association of Environmental Sciences, in which three points were selected to obtain samples, although it was possible to sample in only two of them. Several indexes were calculated from these samples: IBMWP, IASPT, NFAM, NPLE and EPT; whose results indicated a Very Good-Good status in the OR-YA2 point and a Very Good status in the OR-YA3 point. This shows the good quality of the Yaga River’s water, which means this river is not contaminated nor perturbated.
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- 2023
10. Estudio del estado ecológico del río Arazas (Parque Nacional de Ordesa y Monte Perdido, verano de 2020) mediante índices de macroinvertebrados
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Valladolid, María, Sanz Sobrino, Laura, Valladolid, María, and Sanz Sobrino, Laura
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[ES] En el presente trabajo se ha llevado a cabo un estudio basado en la determinación del estado ecológico del río Arazas mediante el uso de indicadores biológicos, concretamente macroinvertebrados acuáticos. El río estudiado forma parte del parque Nacional de Ordesa y Monte Perdido en Huesca, Aragón. Las muestras con las que se trabaja fueron tomadas en el año 2020 en dos meses distintos, julio y septiembre. Se cuenta con un total de seis botes de muestras que recogen información de tres puntos diferentes; Cola de Caballo, Soaso y As Fuens. Una vez las muestras se filtran y se separan todos los individuos encontrados en ellas, se procede a la clasificación taxonómica a nivel de orden y familia. Gracias a este último paso se calculan una serie de índices biológicos (IBMWP, IASTP, NFAM, PLE, TRI, EST), que permiten determinar la calidad que presenta el agua del río Arazas. De forma general, se concluye que el río presenta una calidad adecuada, principalmente en los puntos de muestreo OR – AR2 y OR – AR3., [EN] In the present work, a study has been done based on the determination of the ecological status of the Arazas river through the use of bioindicators, specifically aquatic macroinvertebrates. The river that has been studied is part of the Ordesa y Monte Perdido National Park in Huesca, Aragón. The samples used were taken in the year 2020 in two different months, July and September. There is a total of six samples that collect information of three different sampling – points; Cola de Caballo, Soaso and As Fuens. Once the samples are filtered and all the organisms found in them are separeted, taxonomic classification at order and family level is carried out. After this step, we can calculate a series of biological indexes (IBMWP, IASTP, NFAM, PLE, TRI, EST), which allow us to determinate the quality of the water of the Arazas river. In general, we conclude that the river presents an adequate quality, mainly in the sampling points OR – AR2 and OR – AR3.
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- 2023
11. Estudio del estado ecológico del río Bellós (P.N. Ordesa y Monte Perdido, España) mediante el uso de macroinvertebrados acuáticos como bioindicadores
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Valladolid, María, Baz Ramos, Arturo, Martín Herreros, Hugo, Valladolid, María, Baz Ramos, Arturo, and Martín Herreros, Hugo
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[ES] Se presentan los resultados de algunos índices como bioindicadores del estado ecológico del río Bellós (Parque Nacional Ordesa y Monte Perdido) en el 2020, utilizando macroinvertebrados acuáticos para su cálculo. Se introduce la legislación vigente que rige la metodología de este tipo de estudios. Se comentan las características del área de estudio y el procedimiento realizado durante el muestreo y la identificación de los invertebrados bentónicos. Se exponen los resultados de los índices IBMWP, IASPT, NFAM, NFPLE, EPT y sus ratios de calidad ecológica (RCE) en dos puntos de muestreo, para dos fechas distintas (una en julio y otra en septiembre) en cada punto, y se observa que en el 90% de los casos la calidad del agua se puede clasificar en la categoría de “Muy Buena”. Por último, se analizan gráficamente los resultados de los índices y se aprecia un ligero descenso del estado ecológico desde julio a septiembre., [EN] The results of some indexes as bioindicators of the ecologic status of the Bellós River (Ordesa y Monte Perdido National Park) in 2020 are presented, using aquatic macroinvertebrates for their calculation. The current legislation that rules the methodology of this type of studies is introduced. The charecteristics of the study area and the procedure carried out during sampling and indentification of benthic invertebrates are commented. The results of the IBMWP, IASPT, NFAM, NFPLE, EPT indexes and their ecological quality ratios (EQR) are exposed at two sampling points for two different dates (one in july and the other one in september) at each point, and is observed that in 90% of cases the quality of the water can be classified in the category “Very Good”. Finally, the results of the indexes are analized graphically and have a slight decrease in the ecological status can be seen from july to september.
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- 2023
12. An evaluation of freshwater monitoring programs in ILTER nodes and mountain national parks: identifying key variables to monitor global change effects
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European Commission, Consejo Superior de Investigaciones Científicas (España), Conferencia de Rectores de las Universidades Españolas, Peñas, Francisco J., Álvarez-Cabria, Mario, Sáinz-Bariáin, Marta, Mata Campo, Maria Pilar, Pérez-Haase, Aaron, Ventura, Marc, Polo-Gómez, María José, Alonso, Carlos, Granados, Ignacio, Morellón, Mario, Pérez-Martínez, Carmen, Rubio-Romero, Ángel, Carillo, Presentación, Zamora-Muñoz, Carmen, Valladolid, María, Camero, Lluís, Gacia, Esperança, Puig, Mariàngels, Buchaca, Teresa, Barquín, José, European Commission, Consejo Superior de Investigaciones Científicas (España), Conferencia de Rectores de las Universidades Españolas, Peñas, Francisco J., Álvarez-Cabria, Mario, Sáinz-Bariáin, Marta, Mata Campo, Maria Pilar, Pérez-Haase, Aaron, Ventura, Marc, Polo-Gómez, María José, Alonso, Carlos, Granados, Ignacio, Morellón, Mario, Pérez-Martínez, Carmen, Rubio-Romero, Ángel, Carillo, Presentación, Zamora-Muñoz, Carmen, Valladolid, María, Camero, Lluís, Gacia, Esperança, Puig, Mariàngels, Buchaca, Teresa, and Barquín, José
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Identifying and quantifying global change impacts on biotic and abiotic components of ecosystems is critical to promote an effective adaptation that increases the success of conservation strategies. To achieve this goal, global and regional assessment efforts require certain degree of harmonization on local monitoring programs to establish relevant comparisons at different spatio-temporal scales. Otherwise, the lack of harmonization might hinder the detection and assessment on the effects of human impacts. In this work we have compiled information on freshwater monitoring programs located in areas of intensive research and conservation interest: International Long Term Ecological Research (ILTER) nodes and mountain National Parks. We aimed at evaluating the quality and robustness of these programs to assess the impact of global change, addressing from the worldwide to the European and Spanish national scale. Results highlighted that freshwater monitoring programs lack a common strategy to monitor these ecosystems. Even at the continental and national scales, contrasting strategies and level of detail have been historically applied. Water quality, habitat and biodiversity are more commonly monitored than community structure and ecosystem functioning. Monitoring efforts on the Spanish Mountain National parks indicated differences on the targeted aquatic ecosystems. Rivers and lakes received a higher attention, while mires were rarely considered. Our results provide evidence that greater efforts should be directed towards constructing a coordinated strategy to monitor freshwater ecosystems at national, continental, and global scales. This strategy should involve a shared backbone of biophysical and biogeochemical variables for each habitat type on agreed protocols that are implemented across regions and administrative borders. Achieving this will support a substantial advance on the ecological research to further delineate proper conservation strategies to face the cha
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- 2023
13. Study of sedentary behaviour analysed by self-report questionnaire and accelerometry, and its association with cardiovascular risk factors in an adult population from a health centre
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Portella, Fernando Salom, primary, Sintes, Virginia Dorado, additional, Mercadal, David Mercadal, additional, Febrer, Pau Sintes, additional, Caparrós Pons, Toni, additional, Valladolid, María Barona, additional, and Salort, Antonia Pons, additional
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- 2022
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14. Drainage and N-leaching in alluvial soils under agricultural land uses: Implications for the implementation of the EU Nitrates Directive
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Arauzo, Mercedes and Valladolid, María
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- 2013
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15. Genetic study with 21 autosomal STRs in five Peruvian macro regions for human identification purposes
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Bermejo Valladolid, María E., Ge, Jianye, Budowle, Bruce, Infante Valdez, Cesar, and Neyra-Rivera, Carlos David
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- 2022
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16. Estudio del estado ecológico del río Arazas (Parque Nacional de Ordesa y Monte Perdido, verano de 2019) mediante índices de macroinvertebrados
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Valladolid, María, Montero Aparicio, Verónica, Valladolid, María, and Montero Aparicio, Verónica
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[EN] The ecological status of the Arazas River (Ordesa and Monte Perdido National Park) has been evaluated using benthic macroinvertebrate indices of samples collected during July and September 2019. Samples from three sections of the river are analyzed: upper section, middle section and low, for each of the months sampled. All points belong to Type 27: High mountain rivers. For each point, a series of macroinvertebrate indices (IBMWP, IASPT, NFAM, NFPLE and EPT) have been calculated and the temporal variability of the ecological status has been analyzed, comparing it with the values obtained in previous studies. In total, we observe that in 2019, 86.67% of the indices indicate a Very Good – Good status with a minimum in the two months in the middle section and in July in the upper section of the river. 13.33% belong to a Moderate - Deficient state in 80% of the measures of the high section in September. The analysis of the evolution of the river in comparison with the data from previous studies shows that the values of ecological quality have decreased with respect to the trend they presented during previous years., [ES] Se ha evaluado el estado ecológico del río Arazas (Parque Nacional de Ordesa y Monte Perdido) mediante índices de macroinvertebrados bentónicos de muestras recogidas durante julio y septiembre de 2019. Se analizan las muestras de tres tramos del río: tramo alto, tramo medio y tramo bajo, para cada uno de los meses muestreados. Todos los puntos pertenecen al Tipo 27: Ríos de alta montaña. Para cada punto se ha calculado una serie de índices de macroinvertebrados (IBMWP, IASPT, NFAM, NFPLE y EPT) y se ha analizado la variabilidad temporal del estado ecológico, comparándolo con los valores obtenidos en estudios previos. En total, observamos que en 2019 el 86,67% de los índices indican un estado Muy Bueno - Bueno con un mínimo en los dos meses en el tramo medio y en julio en el tramo alto del río. Un 13,33% pertenece a un estado Moderado - Deficiente en el 80% de las medidas del tramo alto en septiembre. El análisis de la evolución del río en comparación con los datos de estudios previos deja ver que los valores de calidad ecológica han disminuido respecto a la tendencia que presentaban durante los años anteriores.
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- 2022
17. Would delineation of nitrate vulnerable zones be improved by introducing a new parameter representing the risk associated with soil permeability in the Land Use–Intrinsic Vulnerability Procedure?
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European Commission, Ministerio de Economía, Industria y Competitividad (España), Arauzo, Mercedes, Valladolid, María, Andries, Delia M., European Commission, Ministerio de Economía, Industria y Competitividad (España), Arauzo, Mercedes, Valladolid, María, and Andries, Delia M.
- Abstract
Most methods for mapping groundwater vulnerability are based on the excessively simplistic approach that aquifer recharge is produced by vertical infiltration. The novel Land Use–Intrinsic Vulnerability (LU–IV) procedure assesses groundwater vulnerability to nitrate pollution over the entire territory, including aquifers catchment areas. In this research, it was analysed if the delineation of nitrate vulnerable zones (NVZs) would be improved by introducing a new parameter representing the risk associated with soil permeability (parameter S) in the procedure. Different versions of parameter S were tested: S_HC (risk associated with soil hydraulic conductivity), S_St+G+S (risk associated with the stone, gravel and sand fraction of the soil) and S_C (risk associated with the clay fraction). The study was undertaken in the catchment areas of the Oja and Tirón alluvial aquifers (Spain). The efficacy of the following six models was compared: Model 1 (original LU–IV procedure), Model 2 (LU–IV’ procedure using parameter S_HC), Model 3 (LU–IV’ procedure using parameter S_St+G+S), Model 4 (LU–IV’ procedure using parameter S_C), Model 5 (LU–DRASTIC–COP procedure, based on DRASTIC–COP method), and Model 6 (designated NVZ). Catchment scale validations of the six models showed similar, highly significant correlations between the percent coverages of the estimated NVZs and those of the alluvial areas polluted by nitrate for Models 1 to 4. Models 5 and 6 did not show any significant results. In light of these results, Models 1 to 4 were considered the best predictors of nitrate pollution and the best methods for NVZ delineation. Results support the idea that including a parameter S in the LU–IV’ procedure is not essential since equivalent results were obtained from the original LU–IV procedure. So, the LU–IV procedure should be considered the best and simplest method of those tested for accurately delineating NVZ.
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- 2022
18. A new procedure to accurately define Nitrate Vulnerable Zones
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Arauzo, Mercedes, García, Gema, Valladolid, María, Arauzo, Mercedes, García, Gema, and Valladolid, María
- Abstract
The Nitrates Directive of the European Union (91/676/EEC) aims to reduce and prevent water pollution caused by nitrates from agricultural sources. It establishes that water resources should be considered polluted when nitrate concentration exceeds 50 mg L-1. The Directive requires the Member States to designate Nitrate Vulnerable Zones (NVZ), which are areas that drain into waters polluted or at risk of pollution by nitrates. InNVZ, farmers must follow mandatory measures within action programmes that include limiting N-fertilization and animal manure application to prevent nitrate leaching and runoff. One of the difficulties in implementing the European environmental policies for nitrate pollution control is the lack of a common standard criterion for NVZ designation, which in turn may limit the success of action programmes in poorly defined NVZ. Index-based groundwater vulnerability mapping has proven to be a useful tool to assist governments in establishing policies related to the planning of water resource management over the last few decades. There are still, however, research gaps in assessment techniques and scientific considerations behind the inclusion/exclusion of parameters and their relative weights and ratings. In addition, most methods for mapping groundwater vulnerability are based on the excessively simplistic idea that aquifer recharge is only produced by vertical infiltration. The Land Use-Intrinsic Vulnerability (LU-IV) procedure for assessing groundwater vulnerability to nitrate pollution and delimiting NVZ was recently developed to address the above-stated challenges.
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- 2022
19. Estudio del estado ecológico del río Yaga (P.N. Ordesa y Monte Perdido, verano de 2019) mediante índices de macroinvertebrados
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Valladolid, María, Mellado Pineda, Alicia, Valladolid, María, and Mellado Pineda, Alicia
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[EN] The WFD establishes measures to protect watercourses throughout the territory. Its entry into force entailed frequent monitoring and control of these water masses with the aim of guaranteeing their good ecological status. The use of biological indexes is a quick and easy way to determine the degree of alteration suffered by a freshwater ecosystem. Our study area is the Yaga River, which is part of the Ordesa y Monte Perdido National Park. In 2019, a volunteer program of the Association of Environmental Sciences was carried out, obtaining samples of benthic macroinvertebrates from the Yaga River. Three sampling points were selected in said river, of which only two could be sampled. From these samples, a series of indexes have been calculated to determine the status of the river: IBMWP, IASPT, NFAM, EPT and FPLE along with their ecological quality ratios (EQR). The IBMWP index has resulted in a Very Good quality status for the YA-3 point and a Good-Very Good quality for the YA-2 point. Therefore, we can affirm that the Yaga River is not altered., [ES] La DMA establece medidas para proteger los cursos de agua de todo el territorio. Su entrada en vigor supuso la realización de seguimientos y controles frecuentes de estas masas de agua con el objetivo de garantizar su buen estado ecológico. El uso de índices biológicos es una forma rápida y sencilla de determinar el grado de alteración sufrido por un ecosistema dulceacuícola. Nuestra zona de estudio es el río Yaga, que forma parte del Parque Nacional de Ordesa y Monte Perdido. En 2019 se llevó a cabo un programa de voluntariado por parte de la Asociación de Ciencias Ambientales, obteniéndose muestras de macroinvertebrados bentónicos del río Yaga. Se seleccionaron tres puntos de muestreo en dicho río, de los que solo se pudo muestrear en dos. A partir de estas muestras, se han calculado una serie de índices para conocer el estado de dicho río: IBMWP, IASPT, NFAM, EPT y FPLE junto a sus ratios de estado ecológico (EQR). El índice IBMWP ha dado como resultado un estado de calidad Muy Bueno para el punto YA-3 y un estado BuenoMuy Bueno para el punto YA-2. Por tanto, podemos afirmar que el río Yaga no se encuentra alterado.
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- 2022
20. The Rhyacophila fasciata Group in Europe: Rhyacophila macedonica Karaouzas, Valladolid & Ibrahimi (n. sp.) from Greece, Kosovo, Republic of North Macedonia and Serbia (Trichoptera: Rhyacophilidae)
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Valladolid, María, Karaouzas, Ioannis, Ibrahimi, Halil, Arauzo, Mercedes, Slavevska-Stamenković, Valentina, Dorda, Beatriz A., Hinic, Jelena, Bilalli, Astrit, Musliu, Milaim, Rey, Isabel, Valladolid, María, Karaouzas, Ioannis, Ibrahimi, Halil, Arauzo, Mercedes, Slavevska-Stamenković, Valentina, Dorda, Beatriz A., Hinic, Jelena, Bilalli, Astrit, Musliu, Milaim, and Rey, Isabel
- Abstract
The morphology of all postembryonic stages (larva, pupa, male, and female) of Rhyacophila macedonica Karaouzas, Valladolid, & Ibrahimi n. sp. from Greece, Republic of North Macedonia, Kosovo and Serbia was examined. Morphological data were supplemented by a molecular analysis of the mitochondrial cytochrome C oxidase subunit I (COI) and compared with samples of the nominate species Rhyacophila fasciata Hagen 1859, as well as with other species and subspecies in this group: Rhyacophila septentrionis McLachlan 1865, Rhyacophila denticulata McLachlan 1879, Rhyacophila sociata Navás 1916, Rhyacophila kykladica Malicky & Sipahiler 1993, Rhyacophila fasciata delici Kucinic & Valladolid 2020, and Rhyacophila fasciata viteceki Valladolid & Kucinic 2020. Our results revealed morphological differences between the nominate species and R. macedonica, as well as genetic differences among the taxa in the Rhyacophila fasciata Group, so we propose R. macedonica as a new species of the Group. Based on the new molecular data, we also elevate R. f. delici to the status of a distinct species, R. delici (status promotus).
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- 2022
21. An evaluation of freshwater monitoring programs in ILTER nodes and mountain national parks: identifying key variables to monitor global change effects
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Peñas, Francisco J., Álvarez-Cabria, Mario, Sáinz Bariáin, Marta, Mata Campo, Maria Pilar, Pérez-Haase, A., Ventura, Marc, Polo-Gómez, María José, Alonso, Carlos, Granados, Ignacio, Morellón, Mario, Pérez-Martínez, Carmen, Rubio-Romero, Ángel, Carrillo, Presentación, Zamora-Muñoz, Carmen, Valladolid, María, Camarero, Lluís, Gacia, Esperança, Puig, Mariàngels, Buchaca, Teresa, Barquín, José, Peñas, Francisco J., Álvarez-Cabria, Mario, Sáinz Bariáin, Marta, Mata Campo, Maria Pilar, Pérez-Haase, A., Ventura, Marc, Polo-Gómez, María José, Alonso, Carlos, Granados, Ignacio, Morellón, Mario, Pérez-Martínez, Carmen, Rubio-Romero, Ángel, Carrillo, Presentación, Zamora-Muñoz, Carmen, Valladolid, María, Camarero, Lluís, Gacia, Esperança, Puig, Mariàngels, Buchaca, Teresa, and Barquín, José
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Identifying and quantifying global change impacts on biotic and abiotic components of ecosystems is critical to promote an effective adaptation that increases the success of conservation strategies. To achieve this goal, global and regional assessment efforts require certain degree of harmonization on local monitoring programs to establish relevant comparisons at different spatio-temporal scales. Otherwise, the lack of harmonization might hinder the detection and assessment on the effects of human impacts. In this work we have compiled information on freshwater monitoring programs located in areas of intensive research and conservation interest: International Long Term Ecological Research (ILTER) nodes and mountain National Parks. We aimed at evaluating the quality and robustness of these programs to assess the impact of global change, addressing from the worldwide to the European and Spanish national scale. Results highlighted that freshwater monitoring programs lack a common strategy to monitor these ecosystems. Even at the continental and national scales, contrasting strategies and level of detail have been historically applied. Water quality, habitat and biodiversity are more commonly monitored than community structure and ecosystem functioning. Monitoring efforts on the Spanish Mountain National parks indicated differences on the targeted aquatic ecosystems. Rivers and lakes received a higher attention, while mires were rarely considered. Our results provide evidence that greater efforts should be directed towards constructing a coordinated strategy to monitor freshwater ecosystems at national, continental, and global scales. This strategy should involve a shared backbone of biophysical and biogeochemical variables for each habitat type on agreed protocols that are implemented across regions and administrative borders. Achieving this will support a substantial advance on the ecological research to further delineate proper conservation strategies to face the cha
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- 2022
22. N and P behaviour in alluvial aquifers and in the soil solution of their catchment areas: How land use and the physical environment contribute to diffuse pollution
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Agencia Estatal de Investigación (España), European Commission, Arauzo, Mercedes, Valladolid, María, García, Gema, Andries, Delia M., Agencia Estatal de Investigación (España), European Commission, Arauzo, Mercedes, Valladolid, María, García, Gema, and Andries, Delia M.
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The role of land use and the physical environment in N and P pollution of alluvial aquifers was analysed at three levels of information: (1) aquifer (N and P in groundwater), (2) soil transect (potentially leachable N and P in the soil solution) and (3) aquifer's catchment area. The study was carried out in the Oja and Tirón alluvial aquifers and their catchment areas (northern Spain). Nitrate was the dominant N form, both in groundwater and the soil solution of aquifers’ catchment areas. Orthophosphate and organic–P were the codominant P forms in the aquifers. Orthophosphate was the main form in the soil solution. During the period 2005–2017 no significant decrease in nitrate pollution was observed, suggesting the need to review current Nitrate Vulnerable Zone (NVZ) designations. Since nitrate is highly mobile, it tended to accumulate in stagnation zones at the lower reaches of the aquifers. P did not accumulate in the same zones due to its low solubility. Principal component analyses (PCAs) of the aquifers, soil transects and aquifers’ catchment areas revealed that the observation scale influences the environmental factors that can be detected as intervening in groundwater pollution. At the aquifer scale, links were found between nitrates and land use, topographic, hydrogeological and climatic factors. The protective effect of natural areas against nitrate pollution was noteworthy, while agriculture was associated with pollution. At the soil transect scale, an altitudinal gradient governed soil particle size distribution and land use, separating mountain forest soils from agricultural soils. The negative relationship between clay contents vs. nitrate and orthophosphate in the soil solution pointed to a regulatory role of clay. At the catchment scale, the size and physical characteristics of the catchments and land use distribution determined macronutrient availability in the soil solution and, in turn, N and P groundwater distribution.
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- 2022
23. Rhyacophila septentrionis MacLachlan 1865
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Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, and Stojanović, Katarina
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Insecta ,Arthropoda ,Trichoptera ,Rhyacophila septentrionis ,Rhyacophila ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy - Abstract
Rhyacophila septentrionis McLachlan 1865 Description of the larva Colour: Live specimen golden-olive (Hickin 1954), pale ventrally. Specimens preserved in ethanol reddish brown, dorsum dark, ventrally pale; on abdomen, semicircular-triangular pale anterior dorsolateral areas, dorsocentral area of segments with darker circular pale spots, connected caudally with anterior dorsolateral areas through pale lines, forming W-shape. Sclerotized areas of head and thorax dark brown with pale areas, black in some places (Fig 22a). Head (Figs 14, 22b). Maximum width in posterior third of head, lateral margins almost parallel (tapering slightly towards anterior end, but not constricted at level of eyes, Mackereth 1954, fig 1S; Hickin 1967, fig 40; tapering anteriorly, Edington & Hildrew 1981). Cephalic capsule (Figs 14a, 14b), dorsally and dorsolaterally dark brown, anterior third and areas adjacent to frontoclypeal and anterior coronal sutures and anterior dorsolateral areas paler (dorsal posterior region of head with conspicuous pattern of dark spots on lighter background, Edington & Hildrew 1981, Fig 33, arrow a); ventral side pale, with central and slightly darker U-shape area from middle to posterior end of protogula covered with pale spots (Fig 14c), aboral margins of genae just before union with small black fold (Hickin 1954, fig 4B, 1967, fig 54); in lateral view anterior edge and submentum reddish brown, posterior edge black; oval brown area with dark spots extending laterally from anterior edge of occipital foramen to anterior third of head (Fig 14b). Frontoclypeal apotome (Fig 14d) pale; 2 oval dark brown submesal muscle attachment spots in anterior third between setae #4; dark brown pigmentation in posterior third heart-shaped (crescent shaped, Mackereth 1954, fig 1S; Hickin 1967, fig 40), including pits #4 but not setae #6, with pair of oval lateral and 2–3 circular mesal paler brown muscle attachment spots with dark borders, anterocentral area pale with two oval pale brown spots in anteromesal position (Figs 14a, 22a, 22b). Two-thirds of posterior dorsal area of head brown, marked with darker and paler muscle attachment spots; submesally one pair of dark brown triangular patches with paler spots with dark borders outside posterior edges of frontal sutures; light triangular area on juncture of frontal and coronal sutures, small pale area around pit #9; three pale spots around setae #15, #16, and #19–21, last one connected with posterior pale areas; dark brown dots in posterior area of genae (Mackereth 1954, fig 1S; Hickin 1967, fig 40); dorsal head pits with dark brown borders, posteromesal edge of occipital foramen black. Mandibles (Fig 15) asymmetrical, as in other rhyacophilids; left one bigger than right one. Subapicomesal blade of left mandible slightly concave, right mandible with small tooth in middle, both with darker apices (Figs 15, 22a). Labrum and maxillolabium as in other Rhyacophila species. Mentum rectangular, its anterior half slightly sclerotized. Labrum with small transparent area in central anterior edge. Thorax (Figs 16, 22c): Anterior half of pronotum pale or very light coloured, posterior half with three darker areas, one median and two lateral (Edington & Hildrew 1981, fig 35; Hickin 1954, fig 5B, 1967 fig 56), in darker specimens posterior half brown, with mesal area darker. Sinuous posterior margin bordered by black band, posteriorly and posterolaterally light brown submesally; posterior half of pronotum (Fig 16a) dark, with narrow semicircular area extending anterolaterally and small area laterally, lateral area pale in each pronotal plate; central dark region triangular, tapered posteriorly and reaching posterior edge of sclerite, anteriorly truncate and wider than posteriorly, pale brown spots inside triangular region reaching posterior edge; each side of pronotal plate with two or three lines of pale brown spots with dark border of different shapes and parallel to posterior border; pale areas around setae 2–3#, 5# and 6#, four–six brown spots around setae #5; curved row of two or three dark dots extending from setae #5 toward anterolateral corner, two pale brown spots with dark borders anterolateral and posterolateral of seta 6#, circular and elongate respectively (Figs 16b, 22c); with narrow black band in anterolateral angles, extending posterad laterally above lateral margins to posterolateral corners (Fig 16b); anterior margin light brown, with a line of black spots near anterior angle; mesal area of posterior marginal band black (Fig 16b, 22c). Legs: Similar to those of other Rhyacophila species. Colour pale yellowish, each with tarsus and claw darker, proximal parts of coxa, femur and distal parts of trochanters of fore- and midlegs black or dark brown. Narrow pale dark brown band in proximal dorsolateral area of tibia and distal dorsolateral area of femur of each pair of legs, each inner and outer face of each femur with band of dark brown circular spots. Forelegs each ventrally with spicules, extending from distal half of trochanter, all of femur, tibia and tarsus. Setae black or dark brown, some transparent in ventral area. Abdomen (Figs 17, 18, 22d, 22e): Similar to other Rhyacophila species. Colour as for meso- and metathoracic segments, in preserved larvae semicircular-triangular pale anterior dorsolateral areas, dorsocentral area of each segment with darker circular pale spots, connected caudally with anterior dorsolateral areas through pale lines, forming W-shape, pale yellow ventrally. Widths of anterior abdominal segments similar, narrower in posterior segments. Lateral abdominal gills in tufts of 25–30 filaments. Dorsal sclerite of segment IX (Figs 17, 22d) light coloured, darker in central area, with continuous black band on anterior edge and two discontinuous black bands on posterior edge, posterior to setae #2; band of anterior edge narrower in center, surrounding anteriorly pit #1; pale spots inside central area, two pale areas laterally. Anal prolegs typical of group, each with long sword process (Figs 18a, 18b, 22e). Anal claws each with three short teeth on ventral edge (Figs 18a, 18c, 22e), basoventral hook black basally and reddish brown apically (Figs 18a, 18b). Description of the pupa Biometrics of pupa and cocoon. Male pupa: 10.00 mm (1 specimen); female pupa: 11.60 mm (1 specimen). Cocoon length: 14.40 mm (1 specimen). Head: Distribution of setae on dorsal head similar to R. fasciata. Mandibles dark brown, left one with two large teeth and right one with three, anterior tooth bigger, with numerous fine teeth on inner blade. Antennae of variable length, reaching posterior edge of segment VII and posterior edge of segment IV in male and female studied, respectively. Thorax: Tubercles of prothorax each with 6 setae on male and 4 setae on female studied. Hind wing pads reaching posterior edge of abdominal segment III of male and posterior edge of segment IV of female studied. Abdomen: Paired anterior hook plates pedunculated, almost circular and present from abdominal terga IV to VII (Fig 11), more elongated on segment VII, each with more than 30 spines; also tergum III with pair of small flat hook plates each with 10–15 spines. Paired posterior hook plates sessile on terga III–V, almost circular, each with more than 30 spines. Description of the imago Male body length: 7.70 mm (1 specimen) each forewing: 12.20 mm, each hind wing: 10.60 mm; female, length: 8 mm (1 specimen), each forewing: 11.50 mm, each hind wing: 10.30 mm. Colour: Specimens preserved in ethanol dark brown dorsally, yellowish ventrally, spurs yellowish brown, setae brown, females generally darker than males; small black or dark brown spots dorsally. Forewings dark with small pale spots, pale in preserved specimens, darker in females, hind wings pale; each with dark area on leading edge between subcostal (Sc) and middle space between first radial (R 1) and second radial (R 2) veins in fore- and hind wings, with some darker stripes; each forewing hyaline in circular-oval zone, connecting medial (M) and medio-cubital (m-cu) veins and in distal area of second cubital vein (Cu 2) (Holzenthal et al. 2007); in each hind wing proximal segment of medial veins and connection area (M 1-4), not conspicuous, second cubital (Cu 2) vein not conspicuous either totally or partially. Male genitalia (Figs 19, 24, 31b, 31c, 34): Apical segment of each inferior appendage (Figs 19A, 24a, 34c) with basal and distal edges diverging, dorsal and ventral edges slightly diverging, posterior edge of 2nd segment of each inferior appendage slightly concave, ventral edge slightly convex, 2.5 times longer that dorsal edge (Figs 19A, 24a). Apicodorsal vertex angular, apicoventral angle rounded, projecting as thick lobe narrowing progressively to apex. Parameres in ventral view curved posteromesad in apical half (Figs 19 BV p, 24c, 34d). In lateral view (Fig 19 BL) each constricted at short distance beyond base, dilated at middle, with rounded dorsal margin, without spines in midventral margin, few long and thick spines on lateroventral area; midlateral surface covered by fine spicules or setae from middle to ventral edge, absent in middle anteroventral and posterodorsal edges. Aedeagus (phallicata) in lateral view (Fig 19 CL) with dorsal margin concave and posterior corner of concavity hooked anterad, posterior edge of aedeagus straight, projected posteroventrad in small ventral apex (Fig 19 CL); ventral lobe of aedeagus semicircular (Fig 19 BV vl). Lateroventral lobes of phallus straight, posterior edges strongly convex, apicolateral margins semicircular (Fig 19 CD lvl). Apicodorsal lobe of segment IX dilated subapicolaterally (Figs 19 DD al, 24b, 31b, 34b), preanal appendages (Fig 19 DD pa, 24b, 31b, 34b) round, almost as long as apicodorsal lobe, covered partially by it, mainly posteriorly; in ventral view apical band (Fig 19 DV ab, 31c) V-shaped, longer than wide, posterior edges rounded, almost parallel, non-sclerotized inside area (Fig 19 DV va) straight, anal sclerites triangular (Fig 19 DV as). Female genitalia (Figs 20, 26, 32a, 35): In lateral view (Figs 20L, 26L, 32a, 35c), posterodorsal margin of segment VIII valves on each side round, posterolateral margin with small excision in middle, ventral edge convex, dorsal edge with dorsolateral triangular projection (Fig 20L). In dorsal view (Figs 20D, 26D, 35b), with indentation between segment VIII valves, projections triangular with rounded corners, delimiting oval space (Fig 20D). In ventral view (Fig 20V, 26V, 35d) segment VIII valves forming two elongate sclerites, distal 2/3 of proximal edges diverging, distal edges straight or slightly concave; intersegmental membrane with pair of deep-dark, slightly elongate sclerites. Morphological characters diagnosing larvae of R. fasciata and R. septentrionis Head: In R. fasciata ventral side of head pale, in some specimens one or two rows of low conspicuous pale spots from posterior edge to halfway up the head. In R. septentrionis central area with slightly darker U-shape area from middle to posterior end of protogula, covered with pale spots. In R. fasciata the pair of dark brown patches outside posterior edge of frontal suture in the shape of open wings, with dark spots inside. In R. septentrionis the pair of dark brown patches more nearly triangular, with paler spots with dark borders inside. In R. fasciata mandibles dark reddish brown, uniformly coloured, left mandible with inner blade slightly convex. In R. septentrionis mandibles reddish brown, with darker apices, left mandible with inner blade slightly concave. Thorax: In R. fasciata on posterior half three dark areas, one median and two lateral, two lines of dark spots inside median area, circular spot on anterior half; posterior area with two to three rows of brown spots with dark border in circular-oval shape and parallel to posterior border. In R. septentrionis on posterior half three dark areas (in Hickin 1954) or dark base with darker mesal stripe with two lines of pale spots inside, two pale brown spots with dark borders anterolateral and posteriolaterally to seta 6#, circular and elongate respectively; posterior area with two-three lines of darkly-bordered pale brown spots of different shapes and parallel to posterior border. In R. fasciata anterior margin with black spot near anterolateral angle; mesal area of posterior marginal band of sclerite dark brown or black posteriorly. In R. septentrionis anterior margin with a line of black spots near anterolateral angle, light brown in middle; mesal area of posterior marginal band of each sclerite black posteriorly. Abdomen: In R. fasciata dorsal sclerite of segment IX uniformly coloured, brown spots in posteromesal area, band of anterior edge with two extensions surrounding pit #1, connected with dark stripes in darker larvae. In R. septentrionis sclerite of segment IX light coloured, mesal area slightly darker, with paler spots inside. Morphological characters diagnosing pupae of R. fasciata and R. septentrionis Abdomen: In R. fasciata paired anterior hook plates palmate, pair of small flat anterior plates without spines on tergum III; paired posterior hook plates slightly oblong transversally. In R. septentrionis paired anterior hook plates almost circular, pair of small flat anterior plates on tergum III with 10–15 spines; paired posterior hook plates almost circular. Morphological characters diagnosing males of R. fasciata and R. septentrionis Genitalia: In R. fasciata, posterior edge of 2nd segment of each inferior appendage slightly concave dorsally and convex ventrally, ventral edge slightly concave and 2.0 times longer than dorsal edge, apicodorsal vertex slightly angular. In R. septentrionis, posterior edge of 2nd segment of each inferior appendage completely concave, ventral edge slightly convex and 2.5 times longer than dorsal edge, apicodorsal vertex more conspicuously angular. In R. fasciata parameres in lateral view each slender near base, dilated in middle, with almost parallel dorsal and ventral margins in central area (S-shape), with two rows of long and thick spines on midventral margin, pointing outward; midlateral surface with sparse fine spicules or setae, from middle posteroventral to posterodorsal edge, covering most of apex, absent on middle anteroventral and dorsal edges. In R. septentrionis, parameres each slender near base, dilated in middle, with rounded dorsal margin, without spines in midventral margin, few long and thick spines on lateroventral area; midlateral surface covered by fine spicules or setae, from middle to ventral edge, absent on middle anteroventral and posterodorsal edges. In R. fasciata posterior edge of aedeagus straight, projected posteroventrad and rounded at posteroventral apex; ventral lobe of aedeagus triangular, lateral edges nearly straight; lateroventral lobes of phallus straight, posterior edges convex, apicolateral margins rounded. In R. septentrionis posterior edge of aedeagus straight, projected posteroventrad in small posteroventral protrusion; ventral lobe of aedeagus semicircular; lateroventral lobes of phallus straight, posterior edges convex, apicolateral margins semicircular. In R. fasciata apicodorsal lobe of segment IX slightly dilated subapicolaterally, almost round, with small apicomesal excision in some specimens; preanal appendages round, shorter than apicodorsal lobe, almost covered by it; in ventral view, apical band V-shaped and 1.8 times as long as wide, posterior arms widely separated, nonsclerotized area between arms of apical band heart-shaped and with posteromesal excision and posterior edges rounded. In R. septentrionis apicodorsal lobe of segment IX strongly dilated subapicolaterally; preanal appendages round, almost as long as apicodorsal lobe, covered partially by it, mainly posteriorly; in ventral view, apical band V-shaped and 1.2 times as long as wide, posterior arms close together and almost parallel, non-sclerotized area between arms of apical band straight and narrow and without posteromesal excision. Morphological characters diagnosing females of R. fasciata and R. septentrionis Genitalia: In R. fasciata in lateral view with dorsal margin of segment VIII 3/4 as long as venter and with prominent dorsolateral projection, posterolateral margin of valve on each side irregular, with 1 or 2 posterior projections, posteroventral projection more conspicuous, ventral margin slightly concave near base and straight or convex distally, in some specimens slightly indented posteriorly. In R. septentrionis in lateral view, with dorsal margin of segment VIII half as long as venter and with prominent dorsolateral projection, posterolateral margin of valve on each side round and with small excision in middle, ventral margin convex. In R. fasciata in dorsal view with indentation between segment VIII valves nearly enclosed by pair of thick posterolateral projections, with rounded apical and subapical corners, small projection on apical corner of some specimens. In R. septentrionis with indentation between segment VIII valves nearly enclosed by pair of triangular projections, with more-nearly acute apical corners. In R. fasciata in ventral view segment VIII valves forming two elongate sclerites, basal third of proximal edges parallel, distal edges irregular, straight, diverging; intersegmental membrane with pair of dark ovoid or slightly elongate sclerites. In R. septentrionis in ventral view segment VIII valves forming two elongate sclerites, basal 1/3 of proximal edges converging, distal edges straight or slightly concave, diverging; intersegmental membrane with pair of deep-dark slightly elongate sclerites. Genetic analysis Rhyacophila fasciata has a wide area of distribution in northern and central Europe and there is no GeneBank entry from the type locality (Elberfeld, Germany), so we have included some sequences from localities around it (Belgium and Germany). In the first analysis, we used these sequences, together with others from localities that previously have been checked as R. fasciata from Bosnia and Herzegovina, Belgium, Croatia, Czech Republic, Estonia, Finland, Germany, Kosovo, Norway, Poland, Republic of Macedonia, Russia, Slovakia and Sweden, together with one sequence of R. cf. nubila from Russia and three of R. cf. obliterata from Poland and Russia. In the second analysis, to build the tree, we selected a total of 52 sequences: a maximum of two sequences of R. fasciata per country (25 in total), as well as 3 sequences of R. septentrionis, 3 sequences of R. denticulata, 4 sequences of R. sociata from Spain and France (promoted to species by Valladolid et al. 2018), 3 sequences of R. kykladica (promoted to species by Valladolid et al. 2019), 7 sequences of R. fasciata delici Kučinić & Valladolid (in Valladolid et al. 2020) and 3 sequences of R. fasciata viteceki Valladolid & Kučinić 2020 (in Valladolid et al. 2020), 1 sequence of R. cf. nubila from Russia and 3 of R, Published as part of Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska & Stojanović, Katarina, 2021, The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.)., pp. 1-57 in Zootaxa 4975 (1) on pages 23-33, DOI: 10.11646/zootaxa.4975.1.1, http://zenodo.org/record/4804044, {"references":["McLachlan, R. (1865) Trichoptera Britannica: A monograph of the British species of caddis-flies. Transactions of the Entomological Society of London, 3 rd Series, 5, 1 - 183. https: // doi. org / 10.1111 / j. 1365 - 2311.1967. tb 01433. x","Hickin, N. E. (1954) Larvae of the British Trichoptera. 42. Rhyacophila septentrionis McLachlan (Rhyacophilidae). Proceedings of the Royal Entomologica Society of London, Series A, General Entomology, 29 (4 - 6), 59 - 61. https: // doi. org / 10.1111 / j. 1365 - 3032.1954. tb 01199. x","Mackereth, J. C. (1954) Taxonomy of the larvae of the British species of the genus Rhyacophila (Trichoptera). Proceedings of the Royal Entomologica Society of London, Series A, General Entomology, 29 (10 - 12), 147 - 152. https: // doi. org / 10.1111 / j. 1365 - 3032.1954. tb 01189. x","Hickin, N. E. (1967) Caddis larvae. Larvae of the British Trichoptera. London, Hutchinson, 467 pp.","Edington, J. M. & Hildrew, A. G. (1981) A key to the caseless caddis larvae of the British Isles. Freshwater Biological Association, Scientific Publication No. 43, 91 pp.","Hagen, H. (1859) Die Phryganiden Pictet's. Entomologische Zeitung, 20 (4 - 6), 131 - 170.","Holzenthal, R. W., Blahnik, R. J., Prather, A. L. & Kjer, K. M. (2007) Order Trichoptera Kirby, 1813 (Insecta), Caddisflies. Zootaxa, 1668 (1), 639 - 698. https: // doi. org / 10.11646 / zootaxa. 1668.1.29","McLachlan, R. (1863) Notes on British Trichoptera, with description of a new species of Rhyacophila. The Entomologist's Annual, 1863, 129 - 136","Valladolid, M., Kucinic, M., Arauzo, M., Cerjanec, D., Cuk, R., Dorda, B. A., Lodovici, O., Stanic Kostroman, S., Vuckovic, I. & Rey, I. (2020) The Rhyacophila fasciata Group in Croatia and Bosnia and Herzegovina: Rhyacophila f. fa sciata Hagen 1859 and the description of two new subspecies, Rhyacophila fasciata delici Kucinic & Valladolid (ssp. nov.) from Croatia and Bosnia and Herzegovina and Rhyacophila fasciata viteceki Valladolid & Kucinic (ssp. nov.) from Bosnia and Herzegovina (Trichoptera: Rhyacophilidae). Zootaxa, 4885 (1), 051 - 075. https: // doi. org / 10.11646 / zootaxa. 4885.1.3","McLachlan, R. (1879) A Monographic Revision and Synopsis of the Trichoptera of the European Fauna, Part VIII. John Van Voorst, London, 1874 - 1880, pp. 429 - 500, plates 45 - 51. https: // doi. org / 10.5962 / bhl. title. 28556","Navas, L. (1916) Tricopteros nuevos de Espana. 1 ª Serie. Broteria, Serie Zoologica, 14, 5 - 11.","Malicky, H. & Sipahiler, F. (1993) Kocherfliegen (Trichoptera) aus der Turkei, mit Bemerkungen zu weiteren mediterranean Kocherfliegen. Bulletin de la Societe Entomologique Suisse, 66, 457 - 468.","Zetterstedt, J. W. (1840) Insecta lapponica. Voss, Lipsiae, 1068 pp.","Valladolid, M., Arauzo, M., Basaguren, A., Dorda, B. A. & Rey, I. (2018) The Rhyacophila fasciata Group in Western Europe: Confirmation of Rhyacophila denticulata McLachlan 1879 (stat. prom.) and Rhyacophila sociata Navas 1916 (stat. res.), based on morphological and molecular genetic evidence (Trichoptera: Rhyacophilidae). Zootaxa, 4418 (6), 526 - 544. https: // doi. org / 10.11646 / zootaxa. 4418.6.2","Valladolid, M., Karaouzas, I., Arauzo, M., Dorda, B. A. & Rey, I. (2019) The Rhyacophila fasciata Group in Greece: Rhyacophila kykladica Malicky & Sipahiler 1993 (stat. prom.) (Trichoptera: Rhyacophilidae). Morphological description, genetic and ecological features. Zootaxa, 4657 (3), 503 - 522. http: // dx. doi. org / 10.11646 / zootaxa. 4657.3.5"]}
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- 2021
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24. Rhyacophila fasciata Hagen 1859
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Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, and Stojanović, Katarina
- Subjects
Insecta ,Arthropoda ,Trichoptera ,Rhyacophila ,Rhyacophila fasciata ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy - Abstract
Rhyacophila fasciata Hagen 1859 Description of the larva (Figs 4–9, 21). The description of the specimens examined will be complemented with descriptions of previous authors, adding or confirming features. Biometrics of last instar larva and prepupa: Length: 14.25–19.00 mm ( = 16.09, n = 13). Maximum width: 2.98–3.90 mm ( = 3.28, n = 13) (Lepneva 1964, 5 th instar larval length: 23.00– 23.40 mm; Nielsen 1942, 5 th instar larval length: 12.00– 23.40 mm; Ulmer 1909, larval length: 22.00–24.00 mm, larval width: 3.00– 3.50 mm). Maximum width of larva at metathorax. Colour: Live specimen greenish, dorsally with dark areas and light stripes, pale ventrally. Specimens preserved in ethanol reddish brown, dorsum dark, ventrally pale; on abdomen, semicircular pale anterior dorsolateral areas, dorsocentral area of segments with irregular pale spots, connected with anterior dorsolateral areas. Sclerotized areas of head and thorax brown with pale areas and stripes, black in some places (Fig 21a). Head (Figs 4, 21b). Length: 1.49–2.20 mm ( = 1.90, n = 13). Width: 1.14–1.50 mm ( = 1.30, n = 13). Maximum width in posterior third of head, lateral margins almost parallel. Cephalic capsule (Figs 4a, 4b), dorsally and dorsolaterally light brown in anterior third, areas adjacent to frontoclypeal and anterior coronal sutures and anterior dorsolateral areas paler; ventral side variable (Silfvenius 1905), pale (Pitsch 1993), or with dark spots in middle central area (Sedlák 1985, p. 111, table 3, fig 10); anterior edge and submentum reddish brown, posterior edge black (Nielsen 1942); oval brown area with dark spots extending laterally from anterior edge of occipital foramen to anterior third of head (Fig 4b) (Klapálek 1893; Lepneva 1964, p. 223, figs 181, 182B). Frontoclypeal apotome (Fig 4c) pale; 2 oval dark brown muscle attachment spots in central anterior third, between setae #4; dark pigmentation in posterior third heart-shaped, including pits #4 but not setae #6, with 4–6 oval brown muscle attachment spots with dark borders (Klapálek 1893; Silfvenius 1905; Nielsen 1942; Lepneva 1964; Pitsch 1993). Two-thirds of posterior dorsal area of head light brown, marked with darker muscle attachment spots; centrally one pair of dark brown patches, wing-shaped, outside posterior edge of frontal suture; light circular area on juncture of frontal and coronal sutures; three pale spots around setae #15, #16, and #19–21; dorsal head pits with dark border, central posterior occipital foramen black. Mandibles (Fig 5) asymmetrical, as in other rhyacophilids; left one bigger than right one. Inner blade of left mandible irregular, convex, right mandible with small tooth in middle (Nielsen 1942, pl. 2, fig 13; Lepneva 1964, p. 223, fig 184). Labrum and maxillolabium as in other Rhyacophila species (Nielsen 1942, pl. 2, figs 12A, 12B, 14A, 14B; Lepneva 1964, p. 223, figs 183A, 183B, 185). Mentum rectangular, its anterior half slightly sclerotized. Labrum with small transparent area in central anterior edge. Thorax (Figs 6, 21c): Anterior half of pronotum pale or very light coloured. Sinuous posterior margin bordered by dark band, brown in middle of each half, black posteromesally and posterolaterally, light brown submesally; posterior half of pronotum (Fig 6a) with three dark areas separated by light zones, central dark region tapered posteriorly and reaching posterior edge of sclerite, anteriorly truncate, wider that posteriorly, two lines of dark brown spots inside central dark region and reaching posterior edge, several dark brown spots along posterior edge; each pronotal plate with lateral dark area almost triangular, from anterior submesal region to posterolateral edge of sclerite, posterior area with two–three rows of brown spots with dark borders distributed in circular-oval shape and parallel to posterior border. Four–six brown spots around setae #5; curved row of dark dots from setae #5 toward anterior submesal corner, curving around circular spot on anterior half (Fig 6a); pale posterior and median areas connected (Fig 6b); with narrow black band in anterolateral angles, extending posterad laterally to posterolateral margins, inner to margins (Fig 6b; Lepneva 1964); anterior margin light brown, with black spot near anterolateal angle; central area of posterior marginal band of each sclerite dark brown or black (Fig 6b) (Nielsen 1942, pl.3, fig 17A; Lepneva 1964, p. 223, fig 188). Legs (Fig 9): Similar to those other Rhyacophila species. Colour yellowish, proximal regions of coxa, femur and distal region of trochanter of fore- and midlegs black or dark brown. Narrow pale reddish-brown band in proximal dorsolateral area of tibia and distal dorsolateral area of femur of each pair of legs, each inner and outer face of each femur with band of circular spots. Forelegs each ventrally with spicules, extending from distal half of trochanter, all of femur, and distal two-thirds of tibia and tarsus. Setae black or dark brown, some transparent in ventral area. Abdomen (Figs 7, 8, 21d, 21e): Similar to other Rhyacophila species. Colour as for meso- and metathoracic segments, greenish with dark dorsal areas and light stripes in living larvae, in preserved specimens semicircular pale anterior dorsolateral areas, dorsocentral area of segments with irregular pale spots, connected with anterior dorsolateral areas, pale yellow ventrally. Widths of anterior abdominal segments similar, narrower in posterior segments. Lateral abdominal gills in tufts of 25–30 filaments (20–30 filaments, Lepneva 1964). Dorsal sclerite of segment IX (Figs 7, 21d) brown, with continuous black band on anterior edge and two small and widely separated black bands on posterior edge, under setae #2 (Lepneva 1964); band of anterior edge narrower in center, with pair of narrow extensions backward beyond and surrounding pit #1; with some brown spots submesally near posterior margin; in darker larvae, extensions of anterior edge and spots of posterocentral area connected by dark stripes, creating X-shape figure; three pale areas along posterior margin, on either side of two black bands and central area. Anal prolegs typical of group, each with long sword process (Figs 8a, 8b, 21e). Anal claws each with three short teeth on ventral edge (Figs 8a, 8c, 21e), basoventral hook black basally and reddish brown apically (Figs 8a, 8b). Description of the pupa Biometrics of pupa and cocoon. Pupal length (total): 9.70–15.70 mm ( = 12.20, n = 28); male pupa: 10.07– 12.28 mm ( = 11.06, n = 11) (length: 11.20–12.20, Lepneva 1964; Nielsen 1942); female pupa: 9.70–15.70 mm ( = 12.94, n = 17) (length: 12.40–15.50, Lepneva 1964; Nielsen 1942; up to 16.00 mm, Silfvenius 1905). Cocoon length (total): 12.37–18.35 mm ( = 15.11, n = 68) (length: 12.50–18.00 mm, Nielsen 1942); male cocoon length: 12.39–16.27 mm ( = 14.43, n = 10); female cocoon length: 13.43–17.73 mm ( = 15.99, n = 16). Head: Distribution of dorsal setae: four before, two between and two in middle of antennal pads, three on posterior edge of each cephalic tubercle. Mandibles brown, left one with two large teeth and right one with three, with numerous fine teeth on inner blade (Klapálek 1893; Nielsen 1942; Ulmer 1909). Antennae of variable length, reaching from middle of abdominal segment IV to posterior edge of segment VI (to anterior edge of segment IV in females and posterior edge of segment VI in males, Klapálek 1893; to abdominal segment VIII in males and V in females, Lepneva 1964; Nielsen 1942). Thorax: Tubercles of prothorax each with 5 setae, directed backwards, two central setae directed forwards. Hind wing pads variously reaching from anterior edge of abdominal segment III to posterior edge of segment IV (forewing pads reaching anterior edge of abdominal segment IV, Klapálek 1893; forewing pads reaching abdominal segment V in males and IV in females, Lepneva 1964; hind wing pads reaching end of segment IV in females, Silfvenius 1905). Abdomen: Paired anterior hook plates pedunculated, straight basally and dilated posteriorly, palmate, and present on abdominal terga IV to VII (Fig 10) (Lepneva 1964; Ulmer 1909), slightly bigger on segments V and VI, each with 15–20 spines; also, pair of inconspicuous small flat plates without spines on tergum III. Paired posterior hook plates sessile on terga III–V, slightly oblong tranversally (length: width = 1:1.3) (Klapálek 1893: paired anterior hook plates present on abdominal terga III to VIII, paired posterior hook plates on terga III to V; Silfvenius 1905: paired anterior hook plates present on abdominal terga IV to VII, sometimes without plates on segment III, paired posterior hook plates present on terga III to V), each with variable number of spines, more than 25. Description of the imago Male body length: 7.04–10.46 mm ( = 9.23, n = 36) each forewing: 10.16–13.54 ( = 11.67, n = 36), each hind wing: 8.52–11.99 mm ( = 10.25, n =36); females, length: 8.73–12.19 mm ( = 10.46, n = 19), each forewing: 10.05–13.90 mm ( = 12.14, n = 19), each hind wing: 8.24–12.03 mm ( = 10.68, n = 19) [Ulmer 1909: male length (R. fasciata) = 10.00 mm, wingspan = 27.00 mm; male length (R. septentrionis) = 6.50–9.00 mm, wingspan = 22.50– 29.00 mm; Malicky 2004: male forewing length = 10.00–14.00 mm, female forewing length = 11.00–14.00 mm]. Colour: Specimens preserved in ethanol reddish brown dorsally, yellowish ventrally, spurs reddish, setae golden brown, females generally darker than males; small black or dark brown spots in dorsal area; in lateral view, some specimens with large black spots marking border between dorsal and ventral areas. Forewings dark with small pale spots, three transversal dark bands (fascias) in dry specimens (Fig 30a), pale in preserved specimens, darker in females, hind wings pale: each with dark area on leading edge between subcostal (Sc) and second radial (R 2) veins in fore- and hind wings; each forewing hyaline in irregular zone connecting medial (M) and medio-cubital (m-cu) veins and in distal area of second cubital vein (Cu 2) (Holzenthal et al. 2007); in each hind wing proximal segment of medial veins and connection area (M 1-4) not conspicuous, second cubital (Cu 2) and first anal (A 1) veins not conspicuous either totally or partially, proximal portion of cubital vein (Cu) and distal portions of first cubital vein (Cu 1a-1b) thicker. Male genitalia (Figs 2b, 12, 23, 30b): Apical segment of each inferior appendage (Figs 2b, 12A, 23a) with basal and distal edges diverging, dorsal and ventral edges diverging, posterior edge of 2nd segment of each inferior appendage slightly concave dorsally and slightly convex ventrally, ventral edge slightly concave (Figs 12A, 23a). Apicodorsal vertex slightly angular, apicoventral angle rounded, projecting as thick lobe narrowing progressively to apex. Parameres in ventral view curved posteromesad in apical half (Figs 12 BV p, 23c). In lateral view (Fig 12 BL) each constricted at short distance beyond base, dilated at middle, with almost parallel dorsal and ventral margins in central area (S-shape), two files of long and thick spines on midventral margin, pointing outward; midlateral surface covered by sparse thin spicules or setae, from middle posteroventral to posterodorsal edge and covering most of apex, absents in middle anteroventral and dorsal edges. Aedeagus (phallicata) in lateral view (Fig 12 CL) with dorsal margin concave and posterior corner of concavity hooked anterad, posterior edge of aedeagus straight, projected posteroventrad, subapically rounded ventrally (Fig 12 CL); ventral lobe of aedeagus triangular (Fig 12 BV vl), lateral edges slightly rounded; lateroventral lobes of phallus straight, posterior edges strongly convex, apicolateral margins rounded (Fig 12 CD lvl). Apicodorsal lobe of segment IX slightly dilated subapicolaterally, almost round in shape (Figs 12 DD al, 23b), with small apicomesal excision in some specimens; preanal appendages (Fig 12 DD pa) round, shorter than apicodorsal lobe, almost covered by it; in ventral view, apical band V-shaped (Fig 12 DV ab) nearly as wide as long, non-sclerotized inside area with posteromesal excision, posterior edges rounded (Fig 12 DV va), anal sclerites triangular (Fig 12 DV as). Female genitalia (Figs 13, 25): In lateral view (Figs 13 La, 13Lb, 25L), posterodorsal margin of segment VIII valves on each side irregular posteriorly, convex on ventral edge, with dorsolateral projection, in some specimens slightly indented posteriorly, posterolateral margin irregular, with 1–2 posterior projections, ventral projection more conspicuous (Fig 13 Lb 1–3). In dorsal view (Figs 13 Da, 13Db, 25D), with indentation between segment VIII valves, with rounded apical and subapical corners, delimiting oval space, small projection in apical corner in some specimens (Fig 13 Db). In ventral view (Fig 13V, 25V) segment VIII valves forming two elongate sclerites, basal 1/4 of mesal edges parallel, distal 3/4 of mesal edges irregular, slightly concave, diverging; intersegmental membrane with pair of dark, ovoid or slightly elongate sclerites., Published as part of Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska & Stojanović, Katarina, 2021, The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.)., pp. 1-57 in Zootaxa 4975 (1) on pages 17-23, DOI: 10.11646/zootaxa.4975.1.1, http://zenodo.org/record/4804044, {"references":["Hagen, H. (1859) Die Phryganiden Pictet's. Entomologische Zeitung, 20 (4 - 6), 131 - 170.","Lepneva, S. G. (1964) Fauna of the USSR. Trichoptera. 1. Larvae and pupae of Annulipalpia. Zoological Institute of the Academy of Science of the USSR, New Series, 88, 1 - 638 [Jerusalem: Israel Program for Scientific Translations (1970)].","Nielsen, A. (1942) Uber die entwicklung und biologie der Trichoptera mit besonderer Berucksichtgung der queltrichopteren Himmerlands [About the development and biology of the Trichoptera with special consideration of spring Trichoptera from Himmerlands]. Archiv fur Hydrobiologie, Suppl. 17, (3 - 4), 337 - 358.","Ulmer, G. (1909) Die Susswasserfauna Deutschlands, Heft 5, 6: Trichoptera. Verlag, Gustav Fischer, Jena, 326 pp.","Silfvenius, A. J. (1905) Beitrage zur Metamorphose der Trichopteren. Acta Societatis pro Fauna et Flora Fennica, 27 (6), 1 - 168.","Pitsch, T. (1993) Zur Larvaltaxonomie, Faunistik und Okologie Mitteleuropaischer Fliessgewasser-Kocherfliegen (Insecta: Trichoptera) [Larval Taxonomy, Faunistics and Ecology of Central European River Caddisflies (Insecta: Trichoptera)]. Landschaftsentwicklung und Umweltforschung, Schriftenreihe des Fachbereichs Landschaftsentwicklung Sonderheft 8, TU Berlin, 322 pp. https: // depositonce. tu-berlin. de / handle / 11303 / 5106","Sedlak, E. (1985) Bestimmungsschlussel fur mitteleuropaische Kocherfliegenlarven (Insecta, Trichoptera). [Identification key for Central European caddis larvae (Insecta, Trichoptera)]. Wasser und Abwasser Vienna, 29, 1 - 146. (Translation from Czech and edition: J. Waringer). https: // www. zobodat. at / pdf / WasserAbwasser _ 1985 _ 0001 - 0146. pdf","Klapalek, F. (1893) Untersuchungen uber die Fauna der Gewasser Bohmens. I. Metamorphose der Trichopteren, II serie. Archiv fur die Naturwissenschaftliche Landesdurchforschung von Bohmen, 8 (6), 1 - 142.","Malicky, H. (2004) Atlas of European Trichoptera. Springer, Dordrecht, The Netherlands, 359 pp. https: // doi. org / 10.1007 / 978 - 1 - 4020 - 3026 - 0 _ 1","Holzenthal, R. W., Blahnik, R. J., Prather, A. L. & Kjer, K. M. (2007) Order Trichoptera Kirby, 1813 (Insecta), Caddisflies. Zootaxa, 1668 (1), 639 - 698. https: // doi. org / 10.11646 / zootaxa. 1668.1.29","McLachlan, R. (1865) Trichoptera Britannica: A monograph of the British species of caddis-flies. Transactions of the Entomological Society of London, 3 rd Series, 5, 1 - 183. https: // doi. org / 10.1111 / j. 1365 - 2311.1967. tb 01433. x"]}
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25. Rhyacophila ferruginea
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Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, and Stojanović, Katarina
- Subjects
Insecta ,Arthropoda ,Trichoptera ,Rhyacophila ferruginea ,Rhyacophila ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy - Abstract
Rhyacophila ferruginea (Scopoli), nomen dubium Phryganea ferruginea Scopoli, 1763: 266, fig. 691. Rhyacophila ferruginea (Scopoli): Hagen, 1859: 153. The original description of this species, as Phryganea ferruginea (Figs 1a, 1b) was: “ Phryganea ferruginea. Length of 6 1/3 lines [supposedly French lines, that gives approximately 14.287 mm of length. M.A. Alonso Zarazaga, personal communication]. Diagnosis. All rust colored; forewings reticulated dark; black eyes. In forests by the waters; month of May. Abdomen with lateral black dots, as many as segments of it. Antennae 6 lines long, rusty. The other sex with a round white common spot, and white spots (5–6) on the outer margin of the forewings.” Hagen (1854), in his study of the species of Phryganea included in Scopoli’s Entomologia Carniolica stated that the description of P. ferruginea does not match the drawing, even with other Phryganea. Following the “reticulate wings” and “white spots” of wings, he proposed three options that could be one of the following: Chaetopteryx villosa (Fabricius, 1798) (based on body contour and reticulation of wings), one of two Hydropsyche Pictet 1834, and one Rhyacophila (reticulation of wings); the color (all rust) only matched with the mentioned Rhyacophila (maybe R. nebulosa Stephen), and, as he had only the female, he couldn’t check if males also had the white spots on the wings. In 1859 Hagen cited this species and R. fasciata, together with R. vulgaris, R. dorsalis and R. paupera: “4. R. ferruginea Scop. Anal appendage rounded, almost completely covering the lateral appendages. The smallest species. Carniola, Austria. Maybe dark colored females of my collection from Zurich belong to it.” “5. R. fasciata Hag. The appendages are very similar to the previous species, but the size of the animal is much more significant and the upper wings have three dark cross-ties. A single male from Elberfeld”. McLachlan (1865), at the end of his description of Rhyacophila septentrionis wrote: “I have some doubt in announcing this as a new species, since the form of the appendices agrees very well with the figure of those of R. ferruginea, sent to me by Dr. Hagen. I submitted an example to that gentleman, and he says that it is larger and darker than his continental types of that species and may be distinct. R. ferruginea is described as ‘die kleinste Art’ of the group (the true genus Rhyacophila) to which it belongs”. In his publication of 1868, McLachlan said: “ R. ferruginea, (Scopoli) Hagen. I have not seen this insect, which, according to Hagen (in litt.) is smaller than septentrionis, but with similar lobes and appendices. Scopoli’s name cannot be said to apply to this species with certainty.” Finally, in his publication of 1879, McLachlan concluded at the end of the paragraph about Rhyacophila septentrionis: “I do not feel justified in adopting Scopoli’s name ferruginea (as was done by Hagen for the example from Carniola). Even supposing that Scopoli had a Rhyacophila before him (which is just possible), the particular species must remain uncertain.” We agree with this statement, due to the difficulty of identification from the original species described, so we propose to change the status of Rhyacophila ferruginea (Scopoli 1763) to nomen dubium., Published as part of Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska & Stojanović, Katarina, 2021, The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.)., pp. 1-57 in Zootaxa 4975 (1) on pages 13-14, DOI: 10.11646/zootaxa.4975.1.1, http://zenodo.org/record/4804044, {"references":["Scopoli, I. A. (1763) Entomologia Carniolica Exhibens Insecta Carnioliae Indigena et Distributa in Ordines, Genera, Species, Varietates. Methodo Linnaeana. I. T. Trattner, Vindobonae [Vienna], xxxvi + 420 pp. https: // doi. org / 10.5962 / bhl. title. 119976","Hagen, H. (1859) Die Phryganiden Pictet's. Entomologische Zeitung, 20 (4 - 6), 131 - 170.","Hagen, H. (1854) Die Kupfer zu Scopoli's Entomologia Carniolica. Entomologische Zeitung, 15 (3), 81 - 91.","Fabricius, J. C. (1798) Entomologia systematica emandata et aucta. Secundum classes, ordines, genera, species adjectis synonimis, locis, observationibus descriptionibus. Supplementum Entomologiae Systematicae. Hafniae [Copenhagen], apud Proft et Storch.","Pictet, F. J. (1834) Recherches pour Servir a l'Histoire et a l'Anatomie des Phryganides. A. Cherbuliez, Geneve [Geneva]. J. - B. Bailliere, Paris, iii + 235 pp., 20 coloured plates. https: // doi. org / 10.5962 / bhl. title. 66017","McLachlan, R. (1865) Trichoptera Britannica: A monograph of the British species of caddis-flies. Transactions of the Entomological Society of London, 3 rd Series, 5, 1 - 183. https: // doi. org / 10.1111 / j. 1365 - 2311.1967. tb 01433. x"]}
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26. The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.)
- Author
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Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, and Stojanović, Katarina
- Subjects
Insecta ,Arthropoda ,Trichoptera ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy - Abstract
Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, Stojanović, Katarina (2021): The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.). Zootaxa 4975 (1): 1-57, DOI: https://doi.org/10.11646/zootaxa.4975.1.1
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- 2021
27. Rhyacophila fasciata Hagen
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Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, and Stojanović, Katarina
- Subjects
Insecta ,Arthropoda ,Trichoptera ,Rhyacophila ,Rhyacophila fasciata ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy - Abstract
Rhyacophila fasciata Hagen Rhyacophila fasciata Hagen, 1859: 153. Lectotype: 1 male. Entomology 11067, Entomology Collection of the Museum of Comparative Zoology, Harvard University. Type locality: Elberfeld (Germany). Other information: (in label) 57; E.-illegible; Hagen; 107; ML; type 11067; (vial); Lectotype Rhyacophila fasciata Hagen. (MCZBase, 2020). (Figs 2a, 2b, 30a, 30b) Ross (1952) included the species in his publication about the lectotypes of Hagen in the collection of the Museum of Comparative Zoology at Harvard University, Cambridge, Massachusetts. Description. This species has been described by several authors over many years. The first publication where this species is cited is that of Hagen (1859), where he provided a very short description: “A. Lower appendages undivided at the top. 1. The tongue-like extention of the last abdominal segment with an enlarged end. 5. R. fasciata Hag. The app. are very similar to the previous species (R. ferruginea Scop.), but the size of the animal is much more significant, and the upper wings have three dark cross bands. A single male from Elberfeld” (Fig 30a).” McLachlan (1868) described it as follows: “ R. fasciata Hagen, may be distinguished almost with certainty by the dark fasciae on the anterior wings. The form of the dorsal lobe is very distinct from the preceding (R. paupera), being broad and rounded, and nearly concealing the app. sup. The second joint of the app. inf. is obliquely truncate (Pl.XIV. fig. 16). I have three ♂ from Carinthia from Zeller.” In 1879, McLachan described R. fasciata and R. septentrionis. In the description of R. fasciata he included the original specimen from Elberfeld, his specimens from Carinthia, saying that they should be referred to septentrionis, and 7 ♂ and 1 ♀ from the Pyrenees (France), writing “it may be that these should form a distinct species”. These specimens from the Pyrenees were described in 1916 by Navás as Rhyacophila sociata (Valladolid et al. 2018). On the other hand, in the description of R. septentrionis McLachlan included his specimens from Scotland, as well as others from different countries of North and Central Europe. Based on results of our studies of morphology and genetics, we can say that most of the specimens cited belong to R. fasciata, keeping only those from Scotland as R. septentrionis. Klapálek (1893) described the larva and the pupa of R. septentrionis in Bohem, but the area matches with those of R. fasciata, so it should be this species. The same situation pertains to Silfvenius (1905), who described larvae and pupae from South Finland as R. septentrionis that should be R. fasciata. Ulmer (1909), based on previous authors, described the imagos and larvae of R. fasciata and R. septentrionis, first one from Elberfeld and the second one from different places in Germany. We consider that these specimens all belong to R. fasciata. There are more recent authors that have described R. fasciata and R. septentrionis specimens: Nielsen (1942) as R. septentrionis from Denmark; Nóvak (1963) as R. fasciata from Czechoslovakia; Hickin (1954) and Mackereth (1954) as R. septentrionis from United Kingdom; Fotius-Jaboulet (1964) as R. septentrionis from France; Lepneva (1964) as R. septentrionis from northwest, west and southwest Russia; Eidel (1974) as R. fasciata from Austria; Buholzer (1978) as R. fasciata from Switzerland; Sedlak (1985) as R. fasciata from Central Europe; Pitsch (1993) as R. fasciata from Central Europe. Of all these descriptions, only those from the United Kingdom could belong to R. septentrionis; the rest, from continental Europe, should be R. fasciata or some related species. Finally, Malicky & Sipahiler (1993) illustrated the differences among male specimens of R. fasciata from Europe, Turkey, and Lebanon that they considered as subspecies of the R. fasciata Group. Some of them have been promoted to species (R. denticulata McLachlan 1879, by Valladolid et al. 2018; R. kykladica Malicky & Sipahiler 1993, by Valladolid et al. 2019), one species has been resurrected (R. sociata Navás 1916, previously a synonym of R. denticulata, by Valladolid et al. 2018), and others could be considered also valid species (Valladolid, unpublished data)., Published as part of Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanisław, Dorda, Beatriz A., Hinić, Jelena, Ibrahimi, Halil, Karaouzas, Ioannis, Krpač, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska & Stojanović, Katarina, 2021, The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.)., pp. 1-57 in Zootaxa 4975 (1) on pages 14-15, DOI: 10.11646/zootaxa.4975.1.1, http://zenodo.org/record/4804044, {"references":["Hagen, H. (1859) Die Phryganiden Pictet's. Entomologische Zeitung, 20 (4 - 6), 131 - 170.","Ross, H. H. (1952) Lectotypes of Hagen species belonging to certain families of Trichoptera. Psyche: A Journal of Entomology, 59, 31 - 36. https: // doi. org / 10.1155 / 1952 / 52847","McLachlan, R. (1868) Contributions to a knowledge of European Trichoptera. Transactions of the Entomological Society of London, 4 th Series, 1, 289 - 308.","Valladolid, M., Arauzo, M., Basaguren, A., Dorda, B. A. & Rey, I. (2018) The Rhyacophila fasciata Group in Western Europe: Confirmation of Rhyacophila denticulata McLachlan 1879 (stat. prom.) and Rhyacophila sociata Navas 1916 (stat. res.), based on morphological and molecular genetic evidence (Trichoptera: Rhyacophilidae). Zootaxa, 4418 (6), 526 - 544. https: // doi. org / 10.11646 / zootaxa. 4418.6.2","Klapalek, F. (1893) Untersuchungen uber die Fauna der Gewasser Bohmens. I. Metamorphose der Trichopteren, II serie. Archiv fur die Naturwissenschaftliche Landesdurchforschung von Bohmen, 8 (6), 1 - 142.","Silfvenius, A. J. (1905) Beitrage zur Metamorphose der Trichopteren. Acta Societatis pro Fauna et Flora Fennica, 27 (6), 1 - 168.","Ulmer, G. (1909) Die Susswasserfauna Deutschlands, Heft 5, 6: Trichoptera. Verlag, Gustav Fischer, Jena, 326 pp.","Nielsen, A. (1942) Uber die entwicklung und biologie der Trichoptera mit besonderer Berucksichtgung der queltrichopteren Himmerlands [About the development and biology of the Trichoptera with special consideration of spring Trichoptera from Himmerlands]. Archiv fur Hydrobiologie, Suppl. 17, (3 - 4), 337 - 358.","Novak, K. (1963) Beschreibung und bestimmungstabelle der weibchen bohmischer arten der gattung Rhyacophila. Acta Societatis Entomologicae Cechosloveniae, 60 (4), 304 - 311.","Hickin, N. E. (1954) Larvae of the British Trichoptera. 42. Rhyacophila septentrionis McLachlan (Rhyacophilidae). Proceedings of the Royal Entomologica Society of London, Series A, General Entomology, 29 (4 - 6), 59 - 61. https: // doi. org / 10.1111 / j. 1365 - 3032.1954. tb 01199. x","Mackereth, J. C. (1954) Taxonomy of the larvae of the British species of the genus Rhyacophila (Trichoptera). Proceedings of the Royal Entomologica Society of London, Series A, General Entomology, 29 (10 - 12), 147 - 152. https: // doi. org / 10.1111 / j. 1365 - 3032.1954. tb 01189. x","Fotius-Jaboulet, M. C. (1964) Description de la larve de Rhyacophila praemorsa Mcl. et comparaison de cette larve a celle de Rhyacophila septentrionis Mcl. Travaux du Laboratoire de Zoologie et de la Station Aquicole Grimaldi de la Faculte des Sciences de Dijon, 62, 1 - 13.","Lepneva, S. G. (1964) Fauna of the USSR. Trichoptera. 1. Larvae and pupae of Annulipalpia. Zoological Institute of the Academy of Science of the USSR, New Series, 88, 1 - 638 [Jerusalem: Israel Program for Scientific Translations (1970)].","Eidel, K. (1974) Die Kocherfliegen (Trichoptera) des Wutachgebietes. Mitteilungen des Badischen Landesvereins fur Naturkunde und Naturschutz, 11 (2), 181 - 195. https: // www. zobodat. at / pdf / Mitt-Bad-Landesver-Natkde-Natschutz-Freiburg _ NF _ 11 _ 0181 - 0195. pdf","Buholzer, H. (1978) Larvenmorphologie und Verbreitung der Schweizerishen Rhyacophila Arten (Trichoptera, Rhyacophilidae). Ph. D. Dissertation, ETH Nr. 6177, Zurich, 151 pp. https: // www. research-collection. ethz. ch / handle / 20.500.11850 / 135968","Sedlak, E. (1985) Bestimmungsschlussel fur mitteleuropaische Kocherfliegenlarven (Insecta, Trichoptera). [Identification key for Central European caddis larvae (Insecta, Trichoptera)]. Wasser und Abwasser Vienna, 29, 1 - 146. (Translation from Czech and edition: J. Waringer). https: // www. zobodat. at / pdf / WasserAbwasser _ 1985 _ 0001 - 0146. pdf","Pitsch, T. (1993) Zur Larvaltaxonomie, Faunistik und Okologie Mitteleuropaischer Fliessgewasser-Kocherfliegen (Insecta: Trichoptera) [Larval Taxonomy, Faunistics and Ecology of Central European River Caddisflies (Insecta: Trichoptera)]. Landschaftsentwicklung und Umweltforschung, Schriftenreihe des Fachbereichs Landschaftsentwicklung Sonderheft 8, TU Berlin, 322 pp. https: // depositonce. tu-berlin. de / handle / 11303 / 5106","Malicky, H. & Sipahiler, F. (1993) Kocherfliegen (Trichoptera) aus der Turkei, mit Bemerkungen zu weiteren mediterranean Kocherfliegen. Bulletin de la Societe Entomologique Suisse, 66, 457 - 468.","McLachlan, R. (1879) A Monographic Revision and Synopsis of the Trichoptera of the European Fauna, Part VIII. John Van Voorst, London, 1874 - 1880, pp. 429 - 500, plates 45 - 51. https: // doi. org / 10.5962 / bhl. title. 28556","Valladolid, M., Karaouzas, I., Arauzo, M., Dorda, B. A. & Rey, I. (2019) The Rhyacophila fasciata Group in Greece: Rhyacophila kykladica Malicky & Sipahiler 1993 (stat. prom.) (Trichoptera: Rhyacophilidae). Morphological description, genetic and ecological features. Zootaxa, 4657 (3), 503 - 522. http: // dx. doi. org / 10.11646 / zootaxa. 4657.3.5","Navas, L. (1916) Tricopteros nuevos de Espana. 1 ª Serie. Broteria, Serie Zoologica, 14, 5 - 11."]}
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28. Invertebrados y calidad del agua
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Valladolid, María
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Los ríos pueden presentar una biodiversidad alta, en función de su estado de conservación general y de la variabilidad de hábitats que posean. Desde la cabecera, donde nacen, hasta su desembocadura en otro río o en el mar, el cauce de cada río posee numerosos sustratos (grandes rocas, gravas de diversos tamaños, arenas, limos), vegetación (bosques de ribera, plantas semisumergidas y sumergidas, algas filamentosas y microscópicas) y velocidades de la corriente del agua (zonas de corriente rápida y media, remansos, zonas estancadas) que permiten la existencia de todo tipo de animales vertebrados e invertebrados en sus aguas. Por otra parte, la presencia de ciertos factores como la contaminación de las aguas por residuos de todo tipo (químicos, biológicos, físicos) procedentes de agricultura, ganadería, industria o entornos urbanos, así como la modificación del paisaje (por ejemplo, en la extracción de arenas y gravas) hace que esta biodiversidad baje en la zona afectada, llegando incluso a desaparecer los organismos vivos en los casos más extremos.
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29. Additions to the article The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.) (Valladolid et al., 2021)
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Valladolid, María
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In our previous paper (Valladolid et al. 2021) we have detected two errors: in the title, Rhyacophila septentrionis McLachlan 1865 (stat. prom.), the correct reference is Rhyacophila septentrionis McLachlan 1865 (stat. res.). And the correct e-mail address of Pavel Chvojka is: pavel.chvojka@nm.cz. After the publication, some specimens of Rhyacophila fasciata Hagen 1859 from Poland (cited as belonging to the M. Valladolid Collection) were deposited in the Collection of Entomology of the Museo Nacional de Ciencias Naturales (MNCN – CSIC), Madrid, with the following numbers: [Adults]. R. fasciata: 4 ♂, river Pasłęka (NE Poland), 53.618N, 20.326E, 180 m a.s.l., 11/v/85 [MNCN_Ent 296070, MNCN_Ent 296071, MNCN_Ent 296073, MNCN_Ent 296074 (MNCN)]. 1 ♀, river Łyna (NE Poland), 53.441N, 20.413E, 190 m a.s.l., 11/v/91 [MNCN_Ent 296072 (MNCN)]. Leg. S. Czachorowski. [Pupae]. R. fasciata: 2 immature pupae (IP) + 1 ♂P + 1 ♀P, Rurka, river Rurzyca (W Poland), 52.999N, 14.481E, 130 m a.s.l., 07/xii/96 [2 IP, MNCN_Ent 296077, MNCN_Ent 296078; 1 ♂P, MNCN_Ent 296075; 1 ♀P, MNCN_Ent 296076 (MNCN)]. 1 ♂P + 1 ♀P, river Wałsza (NE Poland), 54.236N, 20.128E, 70 m a.s.l., 19/iv/99 [1 ♂P, MNCN_Ent 296062; 1 ♀P, MNCN_Ent 296063 (MNCN)]. 1 ♂P + 1 ♀P, Gaznoty, river Gizela (NE Poland), 53.534N, 19.901E, 190 m a.s.l., 9/vi/99 [1 ♂P, MNCN_Ent 296064; 1 ♀P, MNCN_Ent 296065 (MNCN)]. 1 ♂P + 1 ♀P, Zajączki, river Gizela (NE Poland), 53.560N, 19.882E, 170 m a.s.l., 9/vi/99 [1 ♂P, MNCN_Ent 296066; 1 ♀P, MNCN_Ent 296067 (MNCN)]. 1 ♂P + 1 ♀P, river Mała Wkra (NE Poland), 53.552N, 19.964E, 140 m a.s.l., 17/iv/00 [1 ♂P, MNCN_Ent 296060; 1 ♀P, MNCN_Ent 296061 (MNCN)]. 1 ♂P + 1 ♀P, Elbląg, river Kumiela (N Poland), 54.158N, 19.414E, 15 m a.s.l., 10/vii/03 [1 ♂P, MNCN_Ent 296058; 1 ♀P, MNCN_Ent 296059 (MNCN)]. 1 ♂P + 1 ♀P, brook Srebrny Potok (NE Poland), 54.162N, 19.491E, 135 m a.s.l., 11/vii/03 [1 ♂P, MNCN_Ent 296068; 1 ♀P, MNCN_Ent 296069 (MNCN)]. Leg. S. Czachorowski. [Larvae]. R. fasciata: 1 L, Góry Stołowe, brook Kudowski Potok (SW Poland), 50.482N, 16.337E, 840 m a.s.l., 19/ix/94 [MNCN_Ent 296079 (MNCN)]. Leg. S. Czachorowski.
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30. The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.).
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VALLADOLID, MARÍA, primary, ARAUZO, MERCEDES, additional, CHERTOPRUD, MIKHAIL V., additional, CHVOJKA, PAVEL, additional, CZACHOROWSKI, STANISŁAW, additional, DORDA, BEATRIZ A., additional, HINIĆ, JELENA, additional, IBRAHIMI, HALIL, additional, KARAOUZAS, IOANNIS, additional, KRPAČ, VLADIMIR, additional, KUČINIĆ, MLADEN, additional, LODOVICI, OMAR, additional, SALOKANNEL, JUHA, additional, STAMENKOVIĆ, VALENTINA SLAVEVSKA, additional, STOJANOVIĆ, KATARINA, additional, WALLACE, IAN, additional, and REY, ISABEL, additional
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31. Rhyacophila fasciata subsp. viteceki Valladolid & Kucinic 2020
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Valladolid, María, Kučinić, Mladen, Arauzo, Mercedes, Cerjanec, Darko, Ćuk, Renata, Dorda, Beatriz A., Lodovici, Omar, Stanić-Koštroman, Svjetlana, Vučković, Ivan, and Rey, Isabel
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Insecta ,Arthropoda ,Trichoptera ,Rhyacophila ,Rhyacophila fasciata ,Animalia ,Rhyacophilidae ,Biodiversity ,Rhyacophila fasciata viteceki valladolid & kučinić ,Taxonomy - Abstract
Rhyacophila fasciata viteceki Valladolid & Kučinić (ssp. nov.) This subspecies has been found in Bosnia and Herzegovina. Etymology. The specific name is the genitive of Vitecek, given in honour of Dr. Simon Vitecek, biologist and trichopterologist of Wasser Cluster Lunz, Lunz am See, Austria. Type material. Holotype ♂: BOSNIA AND HERZEGOVINA, river Neretva, Bačevići (43.254154º N 17.824627º E, 35 m a.s.l.), 30/vi/17 (Stanić-Koštroman & M. Kučinić) [N1, MNCN _ Ent 269367 (MNCN)]. Paratypes: 2 ♂, same locality as holotype, 30/vi/17 (Stanić-Koštroman & M. Kučinić) [N2, no. 4455, (MCK) and N3, no. 1111 (UMBH)]. 2 ♂ and 1 ♀, river Sturba, 30/viii/18 (M. Kučinić) [1 ♂, S1, MNCN _ Ent 269368 (MNCN); 1 ♀, S3, MNCN _ Ent 269369 (MNCN); 1 ♂ S2, no. 4456 (MKC)]. 1 ♂, river Bunica, 04/vi/17 (StanićKoštroman & M. Kučinić) [B1, no. 1112 (UMBH)]. Description of the imago. Holotype (N1): Length from front of head to distal edge of segment IX 8.91 mm, each forewing 12.55 mm, each hind wing 10.54 mm. Males: Length 8.29–9.21 mm (x = 8.72, n = 6), each forewing 9.83–12.55 (x = 11.34, n = 6), each hind wing 8.85–10.54 mm (x = 9.79, n = 6). Female: Length from front of head to distal edge of segment VIII 11.26 mm (n =1), forewing 14.52 mm (n = 1), hind wing 12.15 mm (n = 1). In ethanol-preserved specimens colour generally pale brown, yellowish, with golden brown setae. Head, thorax, and abdomen dorsally pale brown, with small dark brown spots in dorsal area, some specimens in lateral view with long black spots marking borders between dorsal and ventral areas, abdomen ventrally yellowish; female darker than male, anterior 2/3 of abdominal segments pale brown or brown in darker specimens. Legs light, with spurs reddish brown. Forewings brown, spotted; hind wings pale. Male genitalia (Figs 3, 6 a–6e): Apical segment of each inferior appendage (Figs 3A, 6a) with basal and distal edges diverging, posterior edge oblique and slightly convex, ventral edge straight to slightly concave, at least two times longer that dorsal edge. Apicodorsal vertex angular, apicoventral angle projecting as thick lobe narrowing progressively to round apex (Fig 6a). Parameres (Figs 3 BV–3BL, 6c–6d) in ventral view curved posteromesad in apical 2/3 (Figs. 3 BV p, 6c). In lateral view (Figs. 3 BL, 6d) each slender at base, slightly dilated in middle, with rounded dorsal margin before midlength and almost straight ventral margin at midlength, pointed at apex; row of few thick spines on midventral margin (Figs 6 c–6d); midlateral surface covered by very fine spicules or setae, reaching from anteroventral to posterodorsal edges of paramere, absent from dorsal edge. Aedeagus (phallicata) in lateral view (Figs 3 CL, 6e) with dorsal margin deeply concave and posterior corner of concavity hooked anterad; upper posterior edge concave to obliquely truncate apex, ventral edge sinous. Lateroventral lobes of phallus (Fig. 3 CD lvl) convex, narrowing progressively towards apex, apicolateral margins round, posteromesal edge of each lobe concave. Ventral lobe of aedeagus nearly round, tapering and acute caudally (Fig 3 BV vl). Apicodorsal lobe of segment IX (Figs 3 DD, 6b) slightly dilated subapicolaterally, posterior edge semicircular, lateral edges converging anterad; preanal appendages (fig 3DD pa) shorter than apicodorsal lobe (Fig 3 DD al), obliquely subtruncate apicolaterally, with slightly concave posteromesal edges (Figs. 3 DD, 6b). In ventral view, apical band V-shaped, inner and outer edges converging in posterior third, pointed apically, longer than wide (Fig 3 DV ab); posterior edge of non-sclerotized ventral area slightly concave, with small mesal incision (Fig 3 DV va), anal sclerites subtriangular, concave apically (Fig 3 DV as)., Published as part of Valladolid, María, Kučinić, Mladen, Arauzo, Mercedes, Cerjanec, Darko, Ćuk, Renata, Dorda, Beatriz A., Lodovici, Omar, Stanić-Koštroman, Svjetlana, Vučković, Ivan & Rey, Isabel, 2020, The Rhyacophila fasciata Group in Croatia and Bosnia and Herzegovina: Rhyacophila f. fasciata Hagen 1859 and the description of two new subspecies, Rhyacophila fasciata delici Kučinić & Valladolid (ssp. nov.) from Croatia and Bosnia and Herzegovina and Rhyacophila fasciata viteceki Valladolid & Kučinić, pp. 51-75 in Zootaxa 4885 (1) on pages 65-66, DOI: 10.11646/zootaxa.4885.1.3, http://zenodo.org/record/4296372
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32. The Rhyacophila fasciata Group in Europe: Rhyacophila fasciata Hagen 1859 and formerly synonymized species (Trichoptera: Rhyacophilidae), with new description of Rhyacophila fasciata and Rhyacophila septentrionis McLachlan 1865 (stat. prom.).
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Croatian Science Foundation, Ministry of Culture (Czech Republic), Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanislaw, Dorda, Beatriz A., Ibrahimi, Halil, Karaouzas, Ioannis, Krpac, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, Stojanović, Katarina, Wallace, Ian, Rey Fraile, Isabel, Croatian Science Foundation, Ministry of Culture (Czech Republic), Valladolid, María, Arauzo, Mercedes, Chertoprud, Mikhail V., Chvojka, Pavel, Czachorowski, Stanislaw, Dorda, Beatriz A., Ibrahimi, Halil, Karaouzas, Ioannis, Krpac, Vladimir, Kučinić, Mladen, Lodovici, Omar, Salokannel, Juha, Stamenković, Valentina Slavevska, Stojanović, Katarina, Wallace, Ian, and Rey Fraile, Isabel
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[EN] The presence and distribution of Rhyacophila fasciata Hagen 1859 in Europe were revised, based on bibliographic study, collection specimens, and new material collected in different countries. The status of formerly synonymized species, Rhyacophila ferruginea (Scopoli 1763) and Rhyacophila septentrionis McLachlan 1865 was also assessed. The type of R. ferruginea is missing, the taxon is still unidentified, and thus we propose Rhyacophila ferruginea as a nomen dubium. Morphological features and genetic evidence revealed that R. septentrionis differs from R. fasciata, so we propose to change its status to status resurrectus. We therefore include new descriptions of the different stages (larva, pupa, male, and female) of R. fasciata and of R. septentrionis, together with a molecular analysis based on mitochondrial cytochrome oxidase I (mtCOI) and ecological notes. The species R. coppai Oláh 2020 NEW SYNONYM and R. soreda Coppa & Oláh 2020 NEW SYNONYM are synonyms of R. sociata Navás 1916; the species R. kopasa Oláh & Coppa 2020 NEW SYNONYM and R. rova Oláh & Coppa 2020 NEW SYNONYM are synonyms of R. denticulata McLachlan 1879; the species R. matrensis Oláh & Szcz¿sny 2020 is probably a synonym of R. fasciata, so more study of this species is needed in order to confirm or deny that it is a valid species., [ES] Se ha revisado la presencia y distribución de Rhyacophila fasciata Hagen 1859 en Europa, basada en el estudio de la bibliografía, especímenes de colecciones y en nuevo material recolectado en diferentes países. Se evaluó asimismo el estado de las especies anteriormente sinonimizadas Rhyacophila ferruginea (Scopoli 1763) y Rhyacophila septentrionis McLachlan, 1865. El ejemplar tipo de R. ferruginea se ha perdido y el taxón permanece todavía sin identificar, por lo que proponemos Rhyacophila ferruginea como un nomen dubium. Las características morfológicas y las evidencias genéticas indican que R. septentrionis difiere de R. fasciata, por lo que proponemos un cambio de estatus a status resurrectus. Se incluyen nuevas descripciones de las distintas etapas (larva, pupa, machos y hembras) de R. fasciata y de R. septentrionis, junto con el análisis molecular del gen mitocondrial Citocromo Oxidasa subunidad I (COImt), y notas ecológicas. Las especies R. coppai Oláh 2020 NUEVO SINÓNIMO y R. soreda Coppa & Oláh 2020 NUEVO SINÓNIMO son sinónimos de R. sociata Navás 1916; las especies R. kopasa Oláh & Coppa 2020 NUEVO SINÓNIMO y R. rova Oláh & Coppa 2020 NUEVO SINÓNIMO son sinónimos de R. denticulata McLachlan 1879; la especie R. matrensis Oláh & Szcz¿sny 2020 es probablemente un sinónimo de R. fasciata, por lo que se necesita un estudio más detallado para confirmarla o rechazarla como especie válida.
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33. Estudio del estado ecológico del río Bellós (P.N. Ordesa y Monte Perdido, verano de 2015 y 2019) mediante indicadores de macroinvertebrados
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Valladolid, María, Baz Ramos, Arturo, Aranda Peco, Darío, Valladolid, María, Baz Ramos, Arturo, and Aranda Peco, Darío
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[EN] A study has been carried out with the aim of knowing how the water quality of a pyrenean river varies from the study of its aquatic macroinvertebrate fauna. For this purpose, samples collected on 2 different dates (2015 and 2019) and in 3 sampling points of the Bellós river, belonging to the National Park of Ordesa and Monte Perdido, located in the province of Huesca, Spain, have been examined. For this purpose, the different families of aquatic macroinvertebrates have been separated and identified and different indices have been calculated (IBMWP: Iberian Biological Monitoring Working Party; IASPT: Iberian Average Score per Taxon; NFAM: Total Number of Families; EPT: Number of Ephemoptera, Plecoptera and Trichoptera families; NNFPLE: Number of Plecoptera Families), as well as the Ecological Status Ratio (EQR). In general, 60% of the measurements for the IBMWP index show a Very Good quality, while 30% belong to a Good quality status and only 10% show a Moderate quality status. Despite these results, there is a clear negative trend in the water quality of this river, as occurs, for example, at point OR-BE-3, where the IBMWP value falls to 74 points over the course of 4 years, being the most significant of the study., [ES] Se ha realizado un estudio con el objetivo de conocer cómo varía la calidad del agua de un río pirenaico a partir del estudio de su fauna de macroinvertebrados acuáticos. Para este cometido, se han examinado unas muestras recolectadas en 2 fechas diferentes (2015 y 2019) y en 3 puntos de muestreo del río Bellós, perteneciente al Parque Nacional de Ordesa y Monte Perdido, localizado en la provincia de Huesca, España. Para ello, se han separado e identificado las diferentes familias de macroinvertebrados acuáticos y se han calculado diferentes índices (IBMWP: Iberian Biological Monitoring Working Party; IASPT: Iberian Average Score per Taxon; NFAM: Número total de Familias; EPT: Número de familias de Efemópteros, Plecópteros y Tricópteros; NFPLE: Número de Familias de Plecópteros), así como también el ratio de estado ecológico (EQR). En general, en el 60% de las medidas para el índice IBMWP se obtiene una calidad Muy Buena, mientras que el 30% pertenece a un estado de calidad Bueno y tan sólo en un 10% se aprecia un estado de calidad Moderado. A pesar de estos resultados, se aprecia una clara tendencia negativa en la calidad del agua de este río, como ocurre, por ejemplo, en el punto OR-BE-3, en dónde el valor del IBMWP cae hasta 74 puntos en el transcurso de 4 años siendo el más significativo del estudio.
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34. Estudio del estado ecológico del río Arazas (Parque Nacional de Ordesa y Monte Perdido, verano de 2015) mediante índices de macroinvertebrados
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Valladolid, María, Roque Escalera, Reyda, Valladolid, María, and Roque Escalera, Reyda
- Abstract
[EN] The ecological status of the Arazas river (Ordesa y Monte Perdido National Park) has been evaluated, based on the benthic macroinvertebrate communities collected in the summer of 2015. Three sampling points were selected, belonging to type 27, high mountain rivers. For each of them, different indexes were calculated (IBMWP, IASPT, NFAM, FPLE and EPT) as well as their ecological quality ratios (EQR). The temporal variability of the state was also evaluated, comparing with the values obtained from the summer of 2013. The results indicate that the communities were dominated by pollution-sensitive organisms. The values for the different indexes increase from higher to lower altitudes, while at the sampling points hardly any significant changes are observed, except for AR-3 in 2013, which presents the opposite pattern. Variability is null from one year to the next, indicating the water quality of the river as Good for both years., [ES] Se ha evaluado el estado ecológico del río Arazas (Parque Nacional de Ordesa y Monte Perdido), en función de las comunidades de macroinvertebrados bentónicos recolectadas en verano de 2015. Se seleccionaron tres puntos de muestreo, pertenecientes al tipo 27, ríos de alta montaña. Para cada uno de ellos, se calculó distintos índices (IBMWP, IASPT, NFAM, FPLE y EPT) así como sus ratios de estado ecológico (EQR). También se evaluó la variabilidad temporal del estado, comparando con los valores obtenidos del verano de 2013. Los resultados indican que las comunidades estuvieron dominadas por organismos sensibles a la contaminación. Los valores para los distintos índices aumentan de menor a mayor altitud, mientras que en los puntos de muestreo apenas se observan cambios importantes, excepto para AR- 3 en 2013 que presenta la tendencia contraria. La variabilidad es nula de un año y otro, marcando la calidad del agua del río como Bueno para ambos años.
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- 2021
35. Vulnerabilidad de las aguas subterráneas a la contaminación por nitrato en la cuenca del río Ebro (España) mediante el procedimiento LU-IV
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Arauzo, Mercedes, Valladolid, María, García, Gema, Arauzo, Mercedes, Valladolid, María, and García, Gema
- Abstract
[EN] Nitrate pollution from diffuse sources is one of the principal causes of groundwater quality deterioration on a global scale. Recent research suggests the need to minimize uncertainty in assessing groundwater vulnerability based on a robust methodology, based on a source–pathway–receptor approach, at the basin scale. The LU–IV procedure (Arauzo, 2017) was devised for mapping intrinsic groundwater vulnerability (risk associated with the physical environment) and specific vulnerability to nitrate pollution (risk associated with land use in areas intrinsically vulnerable), with the final goal of improving the nitrate vulnerable zones (NVZ) delineation. This methodology uses simple and readily available parameters combined in a GIS environment that allows assessing groundwater vulnerability in the entire catchment area that potentially can drain water with nitrate in excess into a receiving aquifer. The LU–IV procedure applied to the river Ebro basin (Spain) revealed a surface area of 18,757 km2 under high to extreme vulnerability to nitrate pollution (susceptible to affect groundwater quality). These results differ from the 9.796 km2 of NVZ designated by the Spanish regional administrations with competencies in the Ebro river basin. Although the officially designated NVZ are consistent with the results of this research, the application of the new procedure allowed us to identify 50% more surface area that could be classified as NVZ., [ES] La contaminación por nitrato de fuentes difusas es una de las principales causas del deterioro de la calidad de los recursos hídricos subterráneos a escala global. Recientes investigaciones señalan la necesidad de minimizar la incertidumbre en la evaluación de la vulnerabilidad de las aguas subterráneas, mediante el desarrollo de metodologías robustas que permitan evaluar la vulnerabilidad, bajo un enfoque fuente–vía–receptor, en el contexto de la cuenca hidrológica. El procedimiento LU–IV (Arauzo, 2017) fue ideado para cartografiar la vulnerabilidad intrínseca de las aguas subterráneas (riesgos asociados al medio físico) y la vulnerabilidad específica a la contaminación por nitrato (riesgos asociados a los usos del suelo en territorios intrínsecamente vulnerables) con el objetivo de mejorar la delimitación de las zonas vulnerables a la contaminación por nitrato (ZVN). Esta metodología utiliza parámetros sencillos y fácilmente disponibles que, combinados en un entorno de SIG, permiten evaluar con precisión la vulnerabilidad (intrínseca y específica) en la totalidad de la cuenca hidrológica susceptible de drenar agua con nitrato en exceso hacia un acuífero receptor. La aplicación del procedimiento LU–IV a la cuenca del río Ebro (España) ha permitido determinar que un territorio de 18.757 km2 presenta un nivel de alto a extremo de vulnerabilidad a la contaminación por nitrato (susceptible de afectar a la calidad de sus aguas subterráneas), por lo que las zonas identificadas podrían ser potencialmente designables como ZVN. Esta superficie difiere de los 9.796 km2 designados oficialmente como ZVN por las administraciones autonómicas con competencias en la cuenca del Ebro. Si bien las zonas oficialmente designadas coinciden en gran medida con los resultados de esta investigación, la aplicación del nuevo procedimiento LU–IV ha permitido identificar un 50% más de territorios clasificables como ZVN.
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- 2021
36. The Rhyacophila fasciata Group in Croatia and Bosnia and Herzegovina: Rhyacophila f. fasciata Hagen 1859 and the description of two new subspecies, Rhyacophila fasciata delici Kučinić & Valladolid (ssp. nov.) from Croatia and Bosnia and Herzegovina and Rhyacophila fasciata viteceki Valladolid & Kučinić (ssp. nov.) from Bosnia and Herzegovina (Trichoptera: Rhyacophilidae)
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VALLADOLID, MARÍA, primary, KUČINIĆ, MLADEN, additional, ARAUZO, MERCEDES, additional, CERJANEC, DARKO, additional, ĆUK, RENATA, additional, DORDA, BEATRIZ A., additional, LODOVICI, OMAR, additional, STANIĆ-KOŠTROMAN, SVJETLANA, additional, VUČKOVIĆ, IVAN, additional, and REY, ISABEL, additional
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- 2020
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37. Cartografía de la vulnerabilidad de las aguas subterráneas a la contaminación por nitratos de fuentes difusas en la cuenca del río Ebro (N.E. de España)
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Arauzo, Mercedes, primary, Valladolid, María, additional, and García, Gema, additional
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- 2020
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38. The Rhyacophila fasciata Group in Croatia and Bosnia and Herzegovina: Rhyacophila f. fasciata Hagen 1859 and the description of two new subspecies, Rhyacophila fasciata delici Kučinić & Valladolid (ssp. nov.) from Croatia and Bosnia and Herzegovina and Rhyacophila fasciata viteceki Valladolid & Kučinić (ssp. nov.) from Bosnia and Herzegovina (Trichoptera: Rhyacophilidae)
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Croatian Science Foundation, Valladolid, María, Kučinić, Mladen, Arauzo, Mercedes, Cerjanec, Darko, Cuk, Renata, Dorda, Beatriz A., Lodovici, Omar, Stanić-Koštroman, Svjetlana, Vučković, Ivan, Rey Fraile, Isabel, Croatian Science Foundation, Valladolid, María, Kučinić, Mladen, Arauzo, Mercedes, Cerjanec, Darko, Cuk, Renata, Dorda, Beatriz A., Lodovici, Omar, Stanić-Koštroman, Svjetlana, Vučković, Ivan, and Rey Fraile, Isabel
- Abstract
[EN] We present the description of two new subspecies of the Rhyacophila fasciata Group: Rhyacophila fasciata delici Ku¿ini¿ & Valladolid (ssp. nov.), broadly distributed in Croatia and present also in Bosnia and Herzegovina, and R. fasciata viteceki Valladolid & Ku¿ini¿ (ssp. nov.), found in Bosnia and Herzegovina. Our study of the morphology of adults, as well as our analysis of the barcode region of the mitochondrial cytochrome oxidase I (mtCOI) gene and geographical distribution confirm the differences of the two new subspecies with the nominal species R. f. fasciata, also found in both countries., [ES] Se presenta la descripción de dos nuevas subespecies del Grupo Rhyacophila fasciata: Rhyacophila fasciata delici Kučinić& Valladolid (ssp. nov.), ampliamente distribuida en Croacia y presente también en Bosnia y Herzegovina y R. fasciata vitecekiValladolid & Kučinić (ssp. nov.), encontrada en Bosnia y Herzegovina. El estudio de la morfología de los adultos, así como el análisis de la citocromo oxidasa I mitocondrial (COImit) y la distribución geográfica confirma las diferencias de las dos nuevas subespecies con la especie nominal R. f. fasciata, también presente en ambos países.
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- 2020
39. Cartografía de la vulnerabilidad de las aguas subterráneas a la contaminación por nitratos de fuentes difusas en la cuenca del río Ebro (N.E. de España)
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Agencia Estatal de Investigación (España), Arauzo, Mercedes, Valladolid, María, García, Gema, Agencia Estatal de Investigación (España), Arauzo, Mercedes, Valladolid, María, and García, Gema
- Abstract
La contaminación por nitratos de fuentes difusas es una de las principales causas del deterioro de la calidad de los recursos hídricos subterráneos a escala global. Recientes investigaciones señalan la necesidad de minimizar la incertidumbre en la evaluación de la vulnerabilidad de las aguas subterráneas, mediante el desarrollo de metodologías robustas que permitan evaluar la vulnerabilidad bajo un enfoque fuente–vía–receptor en el contexto de la cuenca hidrológica. El procedimiento LU–IV (Arauzo, 2107) fue ideado para cartografiar la vulnerabilidad intrínseca de las aguas subterráneas (riesgos asociados al medio físico) y la vulnerabilidad específica a la contaminación por nitrato (riesgos asociados a los usos del suelo en territorios intrínsecamente vulnerables), con el objetivo final de mejorar la delimitación de las zonas vulnerables a la contaminación por nitrato (ZVN). Esta metodología utiliza parámetros sencillos y fácilmente disponibles que, combinados en un entorno de SIG, permite evaluar con precisión la vulnerabilidad (intrínseca y específica) en la totalidad de la cuenca hidrológica susceptible de drenar agua (potencialmente portadora de nitrato) hacia un acuífero receptor. La aplicación del procedimiento LU–IV a la cuenca hidrológica del río Ebro (N.E. de España) ha permitido determinar que una superficie de 18.757 km2 presenta un grado de vulnerabilidad específica a la contaminación por nitrato de alto a extremo, por lo que los territorios afectados podrían ser potencialmente designables como ZVN. Esta superficie difiere de los 9.796 km2 designados oficialmente como ZVN por las administraciones autonómicas con competencias en la designación de ZVN en la cuenca del Ebro. Si bien los territorios oficialmente designados coinciden en gran medida con los resultados de esta investigación, la aplicación del nuevo procedimiento ha permitido identificar un 50% más de territorios clasificables como zonas vulnerables. Las áreas aluviales presentaron el mayor grad
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- 2020
40. Rhyacophila sociata Navas 1916, status resurrectus
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Valladolid, María, Arauzo, Mercedes, Basaguren, Ana, Dorda, Beatriz A., and Rey, Isabel
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Insecta ,Arthropoda ,Trichoptera ,Rhyacophila ,Animalia ,Rhyacophilidae ,Biodiversity ,Taxonomy ,Rhyacophila sociata - Abstract
Rhyacophila sociata Nav��s 1916 (status resurrectus) . In his publication, Nav��s (1916) described one male collected in Solares (Cantabria), and as stated previously, Schmid (1949) did not included it in his study of Nav��s��� collection. A staff person of the University of Zaragoza, where the insect collection of Nav��s was housed years ago, suggested that the holotypes, including that of R. sociata, possibly were sent to the Museo de Ciencias Naturales of Barcelona. The curator of the arthropod collection of this museum informed us that this specimen is not in the Barcelona collection, nor is the specimen described as R. gemella (Nav��s 1923). Consequently, we decided to designate a neotype for this species. In a second step, we tried to collect new specimens from Solares, without success, and researchers working in this area confirmed that they never collected the species there. We decided to designate also a new type locality, where the neotype specimen was captured. Neotype: 1 male (08/06/09). Collection number: MNCN _ Ent 160675. Tissues and DNA Collection Number: MNCN / ADN 57444. Other specimens: 3♂, 30/06/08; 1♂ + 6♀, 06/08/08; 1♂ + 1♀, 08/06/09; 1♂, 3/07/09. Collection numbers, see Table 1. Type locality: Casalarreina, La Rioja (Spain). River Oja. Latitudinal and longitudinal geographic coordinates: 42.546105 N, 2.915515 W. Altitude: 490 m a.s.l. Description of the larva. Biometrics last instar larva and prepupa: Length: 9.43���15.34 mm (x��= 2.28, n = 26). Maximum width of larva at metathorax. Maximum width of abdominal segments II���III: 2.32���4.13 mm (x��= 2.96, n = 26). Color: Thorax and abdomen greenish, dorsum with dark areas delimited by narrow, pale, dorsolateral marks. Sclerotized areas of head and thorax dark brown with pale spots and stripes. Specimens preserved in alcohol generally pale yellow, with sclerotized areas reddish brown to black in some places. Head (Fig. 1). Length: 1.37���2.23 mm (x��= 1.58, n = 26). Width: 1.00���1.84 mm (x��= 1.22, n = 26). Maximum width in posterior third of head, approximately in line with sensory pits #9. Cephalic capsule (Figs 1a, 1b), in dorsal view with yellow background anterior of setae #6 and light brown posterior of them, across full width of dorsal view (Figs. 1a, 1b) and halfway down sides (Fig. 1c), except sometimes lighter posterior occiput and beside frontoclypeal and coronal sutures. Ventral view uniformly yellow, without dark spots. Frontoclypeal apotome (Fig. 1d) with brown pattern in posterior third, posterior of setae #6, this pattern U���shaped in 59% of specimens studied (modified U��� shape in 41% of specimens), and with 3���4 pale muscle attachment spots with dark borders inside pattern. Posterior dorsal area of head with pair of brown patches, marked with darker muscle attachment spots (in 78% of specimens). Three light spots around setae #15, #16 and #19���21, forming pair of light longitudinal stripes along head in 53% of specimens. Light triangular spot on juncture of frontal and coronal sutures in 85% of specimens, sometimes replaced by pair of light spots around sensory pits #9. On posterior occipital zone, pair of light areas connecting with dorsal light stripes of setae #15, #16 and #19���21 in 61% of specimens. Most specimens (73%) with light areas bordering frontal and coronal sutures (n = 100). Mandibles (Fig. 2) asymmetrical, as in other rhyacophilids, left one bigger than right one. Inner blade of left mandible smooth, convex, right mandible with small tooth in middle. Maxillolabium and labrum (Fig. 3) as in other Rhyacophila species. Mentum rectangular (Fig. 3a), its anterior half slightly sclerotized. Labrum (Fig. 3b) with small transparent area in middle of anterior edge. Thorax (Fig. 4): Anterior half of pronotum pale or very light coloured in 88% of specimens studied. Sinuous posterior margin bordered by dark band, black in middle and posterolaterally, light brown submesally. Posterior half of pronotum (Fig. 4a) with three dark triangular areas separated by light zones, central dark region tapered posteriorly and reaching posterior edge of sclerite, its anterior reaching sensory pit #P2. Lateral dark triangular areas separated from posterior margins by light stripes, each delimited by line of small darker points parallel to back edge. Each pronotal plate with curved row of dark dots from anterior edge of lateral dark triangular area toward anterolateral corner, curving around circular spot on anterior half of most pigmented specimens (Fig. 4a). Circle of dark dots also around setae #5. Anterolateral margin of each pronotal sclerite black only in anterolateral angle and extending posterad laterally without contacting posterolateral margin (Fig. 4b). Anterior margin not coloured, sometimes with small, brown spot near anterior angle. Central area of posterior marginal band of each sclerite light brown, not black (Fig. 4b). Abdomen (Figs. 5���7): Similar to other species of Rhyacophila. Colour as for meso- and metathoracic segments, greenish with dark dorsal areas delimited by light bars in living larvae and light reddish brown dorsally and pale yellow ventrally in fixed larvae. Widths of anterior abdominal segments similar, narrower in posterior segments. Lateral abdominal gills in tufts of 21���25 filaments. Dorsal sclerite of the segment IX (Fig. 5) light coloured, with two narrow discontinuous black bands on anterior and posterior edges. Anal prolegs (Figs. 6D, 6V, 7a) typical of group, with long sword process (Figs. 7a, 7c). In this aspect, R. denticulata differing from R. sociata in that, instead of this long sword process, basilateral plate with short and angular process (Despax 1928a, fig. 6). Anal claws each with two ��� three teeth on ventral edge (Figs. 7a, 7b), basoventral hook black basally and reddish brown apically (Figs. 6V, 7c). Legs (Fig. 8): Similar to those of other Rhyacophila species. With light reddish brown colour, dorsoproximal coxa black, with small black areas also in dorsoproximal femur and proximal trochanter (dorsal and ventral). Light- coloured zone in distal dorsolateral area of tibia of each of three pairs of legs. Forelegs each with spicules, extending ventrally from distal part of trochanter to end of tarsus, with different disposition on each segment: On trochanter forming isolated tufts, on femur forming double rows, on tibia tufts ventrally and in rows laterally and on tarsus, similar to trochanter but with tufts more densely distributed. Setae reddish, some thicker and darker: On each foreleg, setae 1,3,4 of coxa and 1,4 of trochanter and 1,2,4,6 of femur; on each midleg, setae 1,4 of coxa and trochanter and 1,2,4,6 of femur; on each hindleg, setae 1,4,5 of coxa and 1,4 of trochanter and 1,2,3,4,6 of femur. Description of the pupa. Biometrics of pupa and cocoon. Pupal length (total): 8.24���14.08 mm (x��= 10.83, n = 39); male pupa: 8.24���11.45 mm (x=�� 9.72, n = 19); female pupa: 8.36���14.08 mm (x��= 11.08, n = 20). Maximum width of young pupa in abdominal segments II and III. Cocoon length (total): 11.00��� 15.50 mm (x=�� 13.32, n = 32); width: 3.00��� 4.64 mm (x��= 3.67 mm, n = 32); male cocoon length: 11.00��� 14.28 mm (x��= 12.68, n = 15), width: 3.18���4.05 mm (x��= 3.55 mm, n = 15); female cocoon length: 11.58���15.30 mm (x��= 13.89, n = 13), width: 3.00���4.37 mm (x��= 3.77, n = 13). Head: Distribution of setae on dorsal head similar to that of R. denticulata (Despax 1928a). Mandibles similar in R. denticulata and R. sociata, left one with two large teeth and right one with three, with numerous fine teeth on inner blade. Labrum similar in shape to that of R. denticulata. Antennae in R. sociata of variable length, reaching from middle of abdominal segment V to anterior part of segment VII. Thorax: Tubercules of prothorax each with 5���6 setae in R. sociata but only 4 in R. denticulata. Wing pads reaching posterior edge of abdominal segment IV in R. sociata, and posterior edge of segment III in R. denticulata (Despax 1928a). Abdomen: Paired hook plates of anterior margins pedunculated and present from abdominal segments IV to VII; anterior hook plates on abdominal segment III not visible in R. sociata (Fig. 9), small and with 3���4 spines developed and 3���4 very small in R. denticulata (Despax 1928a). Paired posterior hook plates sessile and on segments III���V in the two species. Number of hooks per plates varying among these species, being least numerous in R. denticulata (see Despax 1928a), and of intermediate abundance in R. sociata (Fig. 9). Description of the imago. Males length: 9.50���10.80 mm (x��= 10.07, n = 7), each forewing: 10.8���11.8 (x��= 11.29, n = 7), each hind wing: 9.30���10.40 mm (x=�� 9.83, n = 7); females, length: 10.70���12.60 mm (x=�� 11.54, n = 7), each forewing: 11.80���12.80 mm (x��= 12.36, n = 7), each hind wing: 10.70���11.10 mm (x��= 10.96, n = 7). Colour generally pale, yellowish with setae reddish brown. Head and thorax reddish brown, abdomen yellowish, with small black spots in dorsal and lateral areas, sometimes also with dark bands on each side of abdominal segments IV���V to VII. Legs light, with spurs reddish brown. Wings pale, darker in females. Dark area on leading edge, between subcostal (Sc) and radial 1 (R1) veins in forewing and between Sc and radial 2 (R2) in hind wing; in R. fasciata this area present between Sc and R1 in both wings, but in R. denticulata only in forewing, between Sc and R2 together with dark spots in edge of wing, at R1���R5 and medial 1 (M1) veins. Male genitalia (Figs. 10, 11): 2nd segment of each inferior appendage quadrangular, with basal and distal edges nearly parallel, posterior and ventral edges slightly concave. Apicodorsal and especially apicoventral angles rounded, apicoventral angle projecting as lobe narrowing progressively to apex. In R. denticulata and R. fasciata males, 2nd segment of each inferior appendage wider basally than in R. sociata, with basal and distal edges diverging, apicodorsal vertex more angular and ventral lobe thicker; also posterior edge sinuous in these two species, in R. denticulata concave in the upper and lower halves, concavities less conspicuous in R. fasciata (Fig. 10A). Parameres (Figs. 10B, 11) each in lateral view slender at base, dilated in middle, with rounded dorsal and ventral margin, and pointed at apex, with few thick spines on midventral margin and small spicules or chaetae on posterior half of external surface. In dorsal and ventral views parameres curved posteromesad in apical 1/3. In R. denticulata parameres more dilated than in R. sociata, each with midventral and lower half of midlateral areas covered with spines long and thick on ventral margin and decreasing in size dorsally, middorsal half with small spines or chaetae; parameres more strongly curved posteromesad in apical 1/3, apex often sinuous and/ or overlapping. In R. fasciata, parameres in lateral view each with base slightly thicker than for other two species and less dilated in middle, midlateral surface almost covered with spines, thicker spines on ventral margin, decreasing in size dorsally, spines of ventral margin less numerous than in R. denticulata; slightly curved posteromesad in apical 1/3 and often overlapping apically (Figs. 10B, 11). Aedeagus (phallicata) in lateral view (Fig. 10 CL) slender and clearly curved in middle, with mid-dorsal margin concave and midventral margin convex, apically with margins almost parallel. Ventral lobe of phallus with parallel margins basally in dorsal view, abruptly narrower apically, apicolateral margins rounded, aedeagus apically blunt (Fig. 10 CV). Aedeagus of R. denticulata in lateral view with mid-dosal margin concave for short distance but midventral margin not convex, ventral lobe in dorsal view with margins convex and narrowing progressively toward apex, apicolateral margins slightly projecting caudad, and aedeagus slightly pointed (Fig. 10 CV). Aedeagus of R. fasciata in lateral view with mid-dorsal margin concave and posterior corner of concavity hooked anterad, midventral margin with small notch, in dorsal view margins of ventral lobe similar and aedeagus similar to R. sociata (Fig. 10 CV). Apicodorsal lobe of segment IX dilated subapicolaterally, with small apicomesal excision; preanal appendages shorter than that lobe, with round edges and small invagination near contact area between segment IX and preanal appendages (Fig. 10 DD). In ventral view, apical band V-shaped, anal sclerites triangular (Fig. 10 DV). In R. denticulata apicodorsal lobe of segment IX dilated subapicolaterally about as much as for R. sociata, but with apex rounded and without excision, preanal appendages shorter than that lobe, more nearly squared than in R. sociata, in ventral view, apical band U-shaped, anal sclerites triangular. In R. fasciata, apicodorsal lobe more dilated than in R. sociata and R. denticulata, almost from its base, and with broad apicomesal excision, similar to R. sociata. In ventral view, apical band V-shaped, with apices close together, anal sclerites triangular (Fig. 10 DV). Female genitalia (Fig. 12): In lateral view, segment VIII valves of R. sociata with posterior margin shallowly concave apically, with each dorsolateral apex extending farther posterad than ventrolateral apex. In R. denticulata, posterior margin with two small projections on each side, one dorsal and one ventral separated by modest indentation and ventrolateral apex longer than dorsolateral apex. In R. fasciata posterolateal margin on each side triangular and longer than small dorsolateral projection, excision between them corresponding to shallow posterior concavity of R. sociata and dorsolateral indentation of R. denticulata. In dorsal view, R. sociata with indentation between broad segment VIII valves, apicodorsal ends of valves with rounded apical and subapical corners and delimiting subcircular space. Rhyacophila denticulata also with apicodorsal ends of valves broad but with apical and subapical corners more nearly rectilinear than in R. sociata and delimiting transversely oval space. In R. fasciata apicodorsal ends of segment VIII valves small, blunt, with delimited space more nearly triangular, wider anteriorly. In ventral view, R. sociata with segment VIII valves forming two elongated sclerites, fused basally, intersegmental membrane with pair of dark sclerites united anteriorly to form heart-shape structure. In R. denticulata, segment VIII valves not united basally, two intersegmental membrane sclerites coma-shaped, not fused, thicker in anterior 1/3 and more widely separated posteriorly. In R. fasciata, segment VIII valves widely separated and not fused basally, intersegmental membrane sclerites longitudinally oval and more widely separated than in R. denticulata. Genetic analysis. The first approximations at the genetic level for the European samples of R. fasciata, R. denticulata, and R. sociata showed that R. fasciata samples could be separated into at least two different groups: One group of specimens from Austria and a second one from central-northern Europe. The difference was sufficient to considerer these groups to represent at least two species. A study of these two species will be conducted in the future. Since the original description of R. fasciata was based in specimens from Carinthia (Austria), we used the sequences from Austria for the comparison with R. denticulata and R. sociata. The mitochondrial sequences analyzed show clear differences between the R. fasciata specimens from Austria and those of R. denticulata and R. sociata. Based on the divergence of sequences, there are two differentiated branches, one corresponding to R. fasciata and another that includes R. sociata and R. denticulata species (Fig. 13). The specific clades are supported by very high bootstrap values in the three cases (98 for R. fasciata, and 99 for the R. sociata ��� R. denticulata node and for each of the R. sociata and R. denticulata branches). The genetic distances (maximum composite likelihood model) between the species, including an outgroup species (R. relicta McLachlan 1879), were 0.041 (R. sociata ��� R. denticulata), 0.052 (R. sociata ��� R. fasciata) and 0.056 (R. denticulata ��� R. fasciata). The pairwise distances between each of these species and the outgroup were 0.076 (R. relicta ��� R. fasciata), 0.095 (R. relicta-R. sociata), and 0.103 (R. relicta ��� R. denticulata). The maximum intraspecific distances obtained were 0.0062 for R. sociata, 0.0053 for R. denticulata, and 0.0040 for R. fasciata., Published as part of Valladolid, Mar��a, Arauzo, Mercedes, Basaguren, Ana, Dorda, Beatriz A. & Rey, Isabel, 2018, The Rhyacophila fasciata Group in Western Europe: Confirmation of Rhyacophila denticulata McLachlan 1879 (stat. prom.) and Rhyacophila sociata Nav��s 1916 (stat. res.), based on morphological and molecular genetic evidence (Trichoptera: Rhyacophilidae), pp. 526-544 in Zootaxa 4418 (6) on pages 530-534, DOI: 10.11646/zootaxa.4418.6.2, http://zenodo.org/record/1245456
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- 2018
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41. Assessment of the risks of N-loss to groundwater from data on N-balance surplus in Spanish crops: An empirical basis to identify Nitrate Vulnerable Zones
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Ministerio de Ciencia, Innovación y Universidades (España), Arauzo, Mercedes, Valladolid, María, García, Gema, Ministerio de Ciencia, Innovación y Universidades (España), Arauzo, Mercedes, Valladolid, María, and García, Gema
- Abstract
The aim of this research was to conduct an empirical assessment of the risks of N-loss to groundwater associated with land use (LU), based on annual data on the net N-balance surplus in Spanish crops. These data were used to generate a detailed risk rating system reflecting the potential risks of N-loss from agriculture. The new LU ratings were used to assess the specific vulnerability of groundwater to nitrate pollution, by using the LU-IV procedure (Arauzo, 2017). The study area included the catchment areas of 12 alluvial aquifers associated to tributaries of the Ebro River (Spain). Most of the alluvial aquifers were chronically polluted by nitrate, with only a few remaining unaffected by pollution. The LU maps from two different base maps (MCAE 2000-09; SIOSE 2011) were used to generate the respective versions of the map of vulnerability to nitrate pollution using the LU-IV procedure. Potential nitrate vulnerable zones (NVZ) were extracted from different models of vulnerability for comparison with the map of groundwater nitrate content. The models compared were the following: model A (LU-IV procedure, based on MCAE 2000-09 and using LU ratings from N-surpluses in Spanish crops), model B (LU-IV procedure, based on SIOSE 2011 and using LU ratings from N-surpluses in Spanish crops), model C (LU-IV procedure, based on MCAE 2000-09 and using LU ratings from bibliographical references; Arauzo, 2107), model D (IV index), model E (DRASTIC), and model F (GOD). Results confirmed, as expected, that models A and B proved to be the best risk predictors, both for polluted groundwater areas and for areas at risk of being polluted. These results support the high level of reliability of the LU-IV procedure, when applying the LU ratings obtained empirically from the N-surpluses. Keywords: alluvial aquifer, catchment area, groundwater vulnerability, LU-IV procedure, Mediterranean area.
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- 2019
42. The Rhyacophila fasciata Group in Greece: Rhyacophila kykladica Malicky & Sipahiler 1993 (stat. prom.) (Trichoptera: Rhyacophilidae). Morphological description, genetic and ecological features
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Valladolid, María, Arauzo, Mercedes, Dorda, Beatriz A., Rey Fraile, Isabel, Valladolid, María, Arauzo, Mercedes, Dorda, Beatriz A., and Rey Fraile, Isabel
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[EN] The morphology of the different stages (larva, pupa, male, and female) of Rhyacophila fasciata kykladica Malicky & Sipahiler 1993 was examined as a basis for the description of the taxon. Morphological data were supplemented by molecular analysis of mitochondrial cytochrome C oxidase subunit I (mtCOI), which were compared with samples of the nominate subspecies Rhyacophila fasciata fasciata Hagen 1859, as well as with other new species in this group, Rhyacophila denticulata McLachlan 1879 and Rhyacophila sociata Navás 1916. Our results revealed genetic differences between all the taxa; therefore, a change of taxonomic status of R. fasciata kykladica to R. kykladica (stat. prom.) is proposed., [ES] Se ha estudiado la morfología de los diferentes estadíos (larva, pupa, macho y hembra) de Rhyacophila fasciata kykladica Malicky & Sipahiler 1993, con el fin de completar la descripción del taxón. Los datos morfológicos se complementaron con el análisis del gen de la citocromo C oxidasa mitocondrial, subunidad I (mtCOI), que se comparó con muestras de la subespecie nominal Rhyacophila fasciata fasciata Hagen 1859, así como con otras especies nuevas en este grupo, Rhyacophila denticulata McLachlan 1879 y Rhyacophila sociata Navás 1916. Nuestros resultados revelaron diferencias genéticas entre todos los taxones, por lo que se propone un cambio de estatus taxonómico de R. fasciata kykladica a R. kykladica (stat. prom.).
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- 2019
43. The Rhyacophila fasciata Group in Western Europe: Confirmation of Rhyacophila denticulata McLachlan 1879 (stat. prom.) and Rhyacophila sociata Navás 1916 (stat. res.), based on morphological and molecular genetic evidence (Trichoptera: Rhyacophilidae)
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VALLADOLID, MARÍA, primary, ARAUZO, MERCEDES, additional, BASAGUREN, ANA, additional, DORDA, BEATRIZ A., additional, and REY, ISABEL, additional
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- 2018
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44. The Rhyacophila fasciata Group in Western Europe: Confirmation of Rhyacophila denticulata McLachlan 1879 (stat. prom.) and Rhyacophila sociata Navás 1916 (stat. res.), based on morphological and molecular genetic evidence (Trichoptera: Rhyacophilidae)
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Ministerio de Ciencia e Innovación (España), Valladolid, María, Arauzo, Mercedes, Basaguren, Ana, Dorda, Beatriz A., Rey Fraile, Isabel, Ministerio de Ciencia e Innovación (España), Valladolid, María, Arauzo, Mercedes, Basaguren, Ana, Dorda, Beatriz A., and Rey Fraile, Isabel
- Abstract
In order to check the presence and distribution of Rhyacophila fasciata fasciata Hagen 1859 (species described from Austria) and R. fasciata denticulata McLachlan 1879 in the Iberian Peninsula, we studied the morphology of Spanish, French, and Austrian specimens, together with their mitochondrial cytochrome c oxidase (mtCOI). We observed that the individuals considered to date as R. fasciata denticulata are in fact two different species: R. denticulata, presently known from France and possibly in some rivers of the Basque Country (Spain), and R. sociata Navás 1916 distributed in Spain and France. These two species are also different from the reference species (R. fasciata) from Austria, so we propose a change in the taxonomic status of R. fasciata denticulata to R. denticulata (stat. prom.) and the restoration of R. sociata (stat. res.), with the designation of a neotype, due to the loss of the holotype.
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- 2018
45. Discophrya Lachmann 1859
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Fernández-Leborans, Gregorio, Valladolid, María, Arauzo, Mercedes, Millán, Andrés, Gabilondo, Regina, Gallardo, Manuela, Jiménez, Luis, and Ramírez-Ballesteros, Mireya
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Astomatida ,Oligohymenophorea ,Discophrya ,Discophryidae ,Biodiversity ,Protozoa ,Ciliophora ,Taxonomy - Abstract
Genus Discophrya Lachmann, 1859 Freshwater suctorians. Evaginative swarmer is dorsoventrally flattened and ciliated on the ventral side. Cup-shaped species without lorica, and when they have lorica, it is a extension of the stalk. Cellular body flattenned. Stalk is strong especially in symphoriont species, with a proximal widening. Contractile vacuole easily distinguishable. (Matthes 1988; Lynn & Small 2000)., Published as part of Fern��ndez-Leborans, Gregorio, Valladolid, Mar��a, Arauzo, Mercedes, Mill��n, Andr��s, Gabilondo, Regina, Gallardo, Manuela, Jim��nez, Luis & Ram��rez-Ballesteros, Mireya, 2017, Epibionts on Hydraena species (Coleoptera: Hydraenidae) from high mountain rivers of Pyrenees (Ordesa and Monte Perdido National Park), with the description of a new species, pp. 79-94 in Zootaxa 4317 (1) on page 85, DOI: 10.11646/zootaxa.4317.1.3, http://zenodo.org/record/880068, {"references":["Matthes, D. (1988) Suctoria. In: Matthes, D., Guhl, W. & Haider, G. (Eds.), Suctoria und Urceolariidae (Peritricha). Gustav Fischer Verlag, Stuttgart, pp. 1 - 226.","Lynn, D. H. & Small, E. B. (2000) Phylum Ciliophora. In: Lee, J. J., Leedale, G. F. & Bradbury, P. (Eds.), An Illustrated Guide to Protozoa. Allen Press, Kansas, pp. 371 - 656."]}
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- 2017
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46. Discophrya ordesae Ramírez-Ballesteros 2017, sp. n
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Fernández-Leborans, Gregorio, Valladolid, María, Arauzo, Mercedes, Millán, Andrés, Gabilondo, Regina, Gallardo, Manuela, Jiménez, Luis, and Ramírez-Ballesteros, Mireya
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Biodiversity ,Taxonomy - Abstract
Description of Discophrya ordesae Fernández-Leborans & Valladolid, sp. n. Derivatio nominis: from Ordesa valley (Pyrenees, Comunity of Aragón, Spain). Ciliate suctorians located mainly in ventral areas of abdomen and thorax (in this case between legs), in number of 1–2, rarely 3 individuals per basibiont (Figure 5). Fanlike body (222–238 µm long, and 255–277 µm wide) with distal end uniformly rounded and proximal end strait and connected to the stalk (Figures 6–7). Body very flattened. Distal edge of the lorica double with capitate tentacles inserted (135–148), of variable length (Figures 8–9) as they are retracted or not (5.3–15.5 µm retracted; 27.2–102.2 extended). Stalk short (86.3–97.2 µm) and thick. Distal end of stalk joining to the basibiont by a slightly expanded region. Proximal part of the stalk continued by a lorica (stylotheca) with thick edge and strong surrounding the cellular body. Macronucleus located in the middle of body (Figure 10–11), oval or rounded (100.4–125 µm long, 109.3– 127 µm wide). In several specimens, larval kineties may be observed in the centre of the body (Figure 12), with the cilia protruding laterally, probably constituting the development of the swarmer on brood pouch (Table 4). Evaginative budding. Registration numbers: MNCN 39.04/5-39.04/7. Distribution. It was found attached to ventral area, mainly in abdomen, of Hydraena delia and H. truncata (Coleoptera: Hydraenidae). From Yaga river (Table 2).
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- 2017
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47. Tokophrya stenostyla Hamilton & Jahn
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Fernández-Leborans, Gregorio, Valladolid, María, Arauzo, Mercedes, Millán, Andrés, Gabilondo, Regina, Gallardo, Manuela, Jiménez, Luis, and Ramírez-Ballesteros, Mireya
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Biodiversity ,Taxonomy - Abstract
Description of Tokophrya cf. stenostyla Hamilton & Jahn The suctorians analyzed (Figures 2–3) had an oval elongated body (51–53 µm long, 20–42 µm wide). In several individuals there was a cap-shaped region protruding from the front end of the body. The posterior end of the body was truncated just above the junction of the stalk. Tentacles spread at the distal end, not grouped in actinophores. There were 20–25 tentacles, directly attached to the surface of the ciliate. The stalk was long (105–121 µm), and its posterior end was widen slightly in attachment with substrate. The anterior end showed a widening near the body, composed by an unequal double ring. The macronucleus was spherical or oval (19–29 µm long, 17–27 µm wide), located in the middle or slightly towards the anterior half of the body (Table 3). Registration numbers: MNCN 39.04/2-39.04/4 Distribution. They were found attached principally to the dorsal area (Figure 4) of elytra of several species of Hydraena: H. delia, H. subimpressa and H. truncata (Coleoptera: Hydraenidae). Found in rivers Bellós and Yaga. (Table 2)., Published as part of Fernández-Leborans, Gregorio, Valladolid, María, Arauzo, Mercedes, Millán, Andrés, Gabilondo, Regina, Gallardo, Manuela, Jiménez, Luis & Ramírez-Ballesteros, Mireya, 2017, Epibionts on Hydraena species (Coleoptera: Hydraenidae) from high mountain rivers of Pyrenees (Ordesa and Monte Perdido National Park), with the description of a new species, pp. 79-94 in Zootaxa 4317 (1) on page 83, DOI: 10.11646/zootaxa.4317.1.3, http://zenodo.org/record/880068
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- 2017
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48. Procedimiento LU-IV para cartografiar la vulnerabilidad de las aguas subterráneas a la contaminación por nitrato de origen difuso: aplicación al territorio de la Comunidad de La Rioja (España)
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Arauzo, Mercedes, Valladolid, María, García, Gema, Molina, David, and Ministerio de Economía y Competitividad (España)
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Usos del suelo ,Geographic information systems (GIS) ,Nitrate Vulnerable Zones (NVZ) ,Zonas Vulnerables a la Contaminación por Nitrato (ZVN) ,Land use ,Factores hidrogeológicos ,Hydrogeological factors ,Sistemas de información geográfica (SIG) - Abstract
[EN]: Nitrate pollution from diffuse sources is the main cause of groundwater quality degradation. The Nitrates Directive of the European Union (EU; 91/676/EEC) establishes that water resources should be considered affected by nitrate pollution when their nitrate contents exceed 50 mg L-1. The Directive defines Nitrate Vulnerable Zones (NVZ) as the areas of land draining into waters affected by nitrate pollution. In these areas farmers are required to comply with the measures laid out in Action Programmes designed to improve water quality. However, one major obstacle to a more efficient implementation of EU environmental policies for nitrate pollution control is the lack of consensus on the criteria to be used for designating NVZ. In this regard, the use of inappropriate criteria for the designations can seriously reduce the effectiveness of the Action Programmes implemented in the NVZ. Bearing all this in mind, the new LU-IV procedure (Arauzo, 2017), for assessing and mapping groundwater vulnerability to nitrate pollution from diffuse sources, was applied to the territory of the Community of La Rioja (northern Spain; Fig. 1) in which, several aquifers (Table I) are chronically affected by nitrate pollution. More specifically, the study had the following objectives: (1) to analyse the distribution of nitrate contents in the 14 aquifers that, totally or partly, belong to the Community of La Rioja (Table I; Fig. 1), (2) to generate the thematic maps of the intrinsic groundwater vulnerability and the specific groundwater vulnerability to nitrate pollution, using the LU-IV procedure, and (3) to define the NVZ in the study area. The LU-IV procedure combines a map of intrinsic vulnerability (based on the IV index) with a map of the risks associated with different land uses (using the Over tool from logical toolset of Spatial Analyst Tools in ArcGIS 10.3). The most basic formulation of the IV index uses four environmental parameters that are commonly related to intrinsic groundwater vulnerability: lithology of the vadose zone, depth to groundwater table, topography slope and annual precipitation (Table II). This method stands out as it meets the following requirements: (1) it uses readily available parameters that provide enough data to feed the model, (2) it excludes redundant parameters, (3) it avoids the need to assign insufficiently contrasted weights to parameters, (4) it assesses the entire catchment area that potentially drains N-polluted waters into the receptor aquifer, (5) it is implementable within a GIS, and (6) it provides a multi-scale representation (Arauzo, 2017). The spatial modelling of nitrate contents in the 14 aquifers under study (Fig. 2) showed large nitrate polluted areas in all of the alluvial aquifers, which exhibited the worst conditions. It was observed that the alluvial aquifers located in first- and second-order basins (aquifers no 044, 045 and 047) showed significant negative correlations between nitrate concentration and water table elevation (Table I). This result was consistent with the existence of stagnant groundwater zones in the lower sections of these aquifers (Fig. 2), where nitrates tend to accumulate. The map of the intrinsic groundwater vulnerability (based the IV index; Fig. 3) showed high to extreme levels of intrinsic vulnerability across 12.3% of the territory of La Rioja (617 km2) and moderate levels in 21.6 % (1.084 km2). All the alluvial areas were within the range of high to extreme intrinsic vulnerability. The map of the specific groundwater vulnerability to nitrate pollution (according the LU-IV procedure; Fig. 4) showed high to extreme levels of specific vulnerability across 483 km2 and moderate levels in 527 km2. To date, the Community of La Rioja has officially designated a total of three NVZ within the study area, jointly covering a surface of 124 km2 (Fig. 1). It was estimated that 53.3% of the alluvial areas in La Rioja exhibited high to extreme vulnerability to nitrate pollution, while 23.8% was subject to moderate risk (Fig. 4). This high vulnerability can be attributed to the combined effect of some typically alluvial characteristics, including: the shallow water table in the alluvial areas, the interconnections between rivers and alluvial aquifers, the permeability of the alluvial deposits and the typically high concentration of irrigated agriculture on the lower terraces and floodplains along river banks. These results highlight the need to redefine what have been the officially designed NVZ in the study area until now. First of all, it seems necessary to ensure the effective protection of the alluvial aquifers, by extending the designations of the NVZ to all the alluvial areas (this high level of protection should be generalized for all the alluvial areas in Europe). On the other hand, territories with moderate vulnerability to nitrate pollution (beyond the alluvial areas) should also be monitored and controlled, given their wide extension. In other words, if we want to effectively implement Action Programmes designed to restore and protect water quality, in line with Directive 91/676/EEC, it is first necessary to review and redefine the current criteria for the designation of NVZ., [ES]: El procedimiento LU-IV es una nueva herramienta que permite cartografiar la vulnerabilidad específica de las aguas subterráneas a la contaminación por nitrato y delimitar las Zonas Vulnerables a la Contaminación por Nitrato (ZVN; Directiva 91/676/CEE). Combina un mapa de vulnerabilidad intrínseca (a partir del índice IV, que estima los riesgos asociados a parámetros del medio físico) y un mapa de riesgos asociados a los usos del suelo (LU). El procedimiento ha sido aplicado al territorio de la Comunidad de La Rioja (España). El mapa de vulnerabilidad específica reveló que una superficie de 483 km2 presentaba niveles de vulnerabilidad de alto a extremo, mientras que otros 527 km2 mostraban niveles medios. Centrándonos en los territorios aluviales (los más vulnerables, atendiendo a factores del medio físico), el 53,3% presentó una vulnerabilidad específica de alta a extrema, el 23,8% niveles medios y el 22,9% niveles bajos o inapreciables. De estos resultados se desprende la necesidad de una protección integral de la totalidad de los territorios aluviales de La Rioja mediante la ampliación de las designaciones de ZVN. Las zonas que presentaron niveles medios de vulnerabilidad en territorios no aluviales también deberían ser susceptibles de seguimiento, dada su amplia extensión., Este trabajo ha sido financiado mediante los proyectos AGL2011-29861/AGR y CGL2016-81110-R (AEI/EU). La Confederación Hidrográfica del Ebro aportó gran parte de los datos hidroquímicos y de profundidades del nivel freático.
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- 2017
49. Sobre la presencia del complejo híbrido Squalius alburnoides (Steindachner, 1866) (Cyprinidae, Actinopterygii) en un sistema de cuevas situado en el sur de España
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Doadrio, Ignacio, Valladolid, María, Carmona, José Ambrosio, Corona-Santiago, Diushi Keri, Perea, Silvia, Cunha, Carina, and Boto, Luis
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Evolución ,Peces de Cueva ,Evolution ,Polyploid Fishes ,Cyprinidae ,Peces poliploides ,Cave Fishes - Abstract
Ponencia Invitada Inaugural del Congreso de Espeleología "EspeleoMeeting Ciudad de Villacarrillo" (Villacarrillo (Jaén), 13, 14 y 15 de agosto de 2016)., [ES] En este trabajo se describe a través de la citología, histología y secuenciación del gen de la rodopsina, la única población de peces encontrada en una cueva de la Península Ibérica. Esta población pertenece a la especie Squalius alburnoides (Steindachner, 1866) (Cyprinidae) y tiene la particularidad de tener un origen híbrido con individuos y poblaciones de diferentes ploidias (2n=50; 3n=75 y 4n=100) y distintos mecanismos de reproducción. Los peces de la cueva de Peal del Becerro I presentaron una degeneración incipiente de la retina, con menor cantidad de fotorreceptores y pigmentación que los peces de la misma especie situados en el exterior de la cueva (Embalse de La Bolera). Todos resultaron ser tetraploides simétricos AAPP lo que sugiere que este biotipo favorece de algún modo la viabilidad de poblaciones de esta especie permitiendo recuperar la bisexualidad y un genoma balanceado. Sin embargo, es necesario realizar estudios en profundidad desde la genómica y transcriptómica y tener un mejor conocimiento de la biología y ecología de esta población cavernícola., [EN] In this study we described through a multidisciplinary approach (cytology, histology and rhodopsin gene sequencing) the only cave population of freshwater fish found in the Iberian Peninsula. This population belong to the species Squalius alburnoides (Steindachner, 1866) (Cyprinidae), which has the singularity of being a species of hybridogenetic origin with individuals and populations of different ploidies (2n=50; 3n=75 y 4n=100) and diverse mechanisms of reproduction. The individuals of S. alburnoides found in the Peal del Becerro I cave showed an incipient degeneration of the retina, with lower amount of photoreceptor cells and pigmentation relative to individuals outside the cave (de la Bolera reservoir). All individuals from the cave were symmetric tetraploids AAPP, which suggests that this biotope is favouring the viability of this population through the recovery of bisexuality and a balanced genome. Nonetheless, further deeper studies using genomics and transcriptomics approaches are required to achieve a better understanding of the biology and ecology of this cave-dweller population.
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- 2016
50. Epibionts on Hydraena species (Coleoptera: Hydraenidae) from high mountain rivers of Pyrenees (Ordesa and Monte Perdido National Park), with the description of a new species
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FERNÁNDEZ-LEBORANS, GREGORIO, primary, VALLADOLID, MARÍA, additional, ARAUZO, MERCEDES, additional, MILLÁN, ANDRÉS, additional, GABILONDO, REGINA, additional, GALLARDO, MANUELA, additional, JIMÉNEZ, LUIS, additional, and RAMÍREZ-BALLESTEROS, MIREYA, additional
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- 2017
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