Identifying the processes and mechanisms that govern communities of organisms is the main goal of community ecology. Locally operating mechanisms such as environmental filtering, in which the environment determines what species are found in a given location, as well as regional processes such as dispersal have all been identified as potential drivers of community processes. However, the relative importance of these drivers may vary temporally and spatially. In dendritic stream networks, headwater streams are isolated when compared to more centrally located mainstem stream sections. I investigated the potential for stream networks to influence the relative influence of local and regional processes via a survey and field experiment based approaches. I found that headwater streams can influence mainstem stream communities, potentially as a result of the dispersal of organisms or abiotic materials. Additionally, I demonstrated that macroinvertebrate communities in headwater streams respond more strongly to manipulations of local environment than do mainstem streams, both in terms of community composition as determined taxonomically and as functional traits. These results indicate that headwater streams may be affected differently than mainstem streams by anthropogenic activity and as such, management strategies and restorations may need to be specifically tailored to address the relative influences of local and regional processes at varying points within a stream network. / Ph. D.

Made available in DSpace on 2016-06-02T19:31:50Z (GMT). No. of bitstreams: 1 2985.pdf: 1080161 bytes, checksum: 6f77b3c4bacbb6a36ca073cc541e5909 (MD5) Previous issue date: 2010-04-29 / Universidade Federal de Minas Gerais / To understand the effects of spatial heterogeneity on the processes that determine the distribution of organisms in low-order streams, in the present study we asked the following question: do the composition and spatial arrangement of leaf litter patches at the scale of streambed landscapes influence the structure and composition of aquatic macroinvertebrate communities? We evaluated substrate organization in two distinct phases: an initial description of the streambeds using landscape ecology techniques, and a second, experimental phase studying the response of aquatic macroinvertebrates to manipulated distributions of the substrate. The results of the descriptive phase showed the importance of leaf litter substrate influencing taxon richness, diversity, evenness, and abundance; further, the division of the habitat in patches was also important to structure the macroinvertebrate communities. The experimental manipulation showed that resource aggregation influences the colonization of the community, mainly in the early periods (8 days). In general, the influence of resource spatial distribution had different effects between the two approaches used, probably due to differences in patch size and quality. The results of the present study can contribute to a better comprehension of the mechanisms structuring the communities of aquatic macroinvertebrates, and to the improvement of sampling techniques and stream restoration projects. / Para tentar entender como a heterogeneidade espacial influencia os processos que determinam a distribuição de organismos em riachos de baixa ordem, o presente estudo teve como objetivo responder a pergunta: a composição e o arranjo espacial das manchas de folhas na escala de paisagens de fundos de riachos influenciam a estrutura e a composição das comunidades de macroinvertebrados aquáticos? Avaliamos a organização dos substratos em duas fases distintas: uma descrição inicial dos ambientes a serem estudados por meio de técnicas de ecologia de paisagem e uma segunda fase experimental, estudando a resposta dos macroinvertebrados aquáticos a distribuições manipuladas do substrato. Os resultados da fase descritiva nos deram indícios da importância da proporção do substrato detritos influenciando a riqueza, diversidade, equitabilidade e abundância; além disso, a divisão do habitat em manchas também parece ser importante para a estruturação da comunidade dos macroinvertebrados. A manipulação experimental permitiu inferir a influência da agregação dos recursos nos processos de colonização da comunidade, principalmente nos períodos iniciais (oito dias). De maneira geral, a influência da distribuição de recursos teve resultados diferentes para as duas abordagens utilizadas, provavelmente devido a diferenças no tamanho e na qualidade das manchas. Os resultados do presente estudo podem contribuir para uma maior compreensão sobre os mecanismos de estruturação de comunidades de macroinvertebrados aquáticos, subsidiando a melhoria das técnicas de amostragem e projetos futuros de restauração dos riachos.

En la presente tesis se muestrearon ríos sobre los 2000 msnm (ríos altoandinos tropicales) que se distribuyen en la amplia región de los Andes del Norte (Ecuador) y los Andes Centrales (Perú) en Sudamérica. El muestreo de las 123 localidades se realizó en época seca, las cuales se seleccionaron tomando en cuenta su grado de alteración, que van desde sin o poca alteración (referencia) hasta muy alterados. En una primera instancia se analizaron las carácteristicas fisicoquímicas e hidromorfológicas de los ríos, las cuales mostraron una alta influencia de la altitud. Se registraron reducciones en la temperatura y oxígeno a medida que la altitud se incrementaba, por otra parte las diferencias en la heterogeneidad de los hábitats, así como la calidad del bosque de ribera fueron dos factores con un alta importancia al momento de caracterizar los ríos altoandinos. Se econtraron diferencias en la mineralización en los diferentes dominios morfotectónicos, siendo más elevados los valores de conductividad en las zonas del sur, debido a la geomorfología propia de cada zona. La comunidad bentónica mostro estar altamente influenciada por la altitud y la latitud. La altitud mostró intervenir positiva o negativamente en la abundancia y frecuencia de algunos géneros como Hyalella, Podonomopsis, Claudioperla, Anomalopsyche, Paltostoma, Rheotanytarsus, Camelobaetidius, etc. Por su parte, la latitud reveló la tendencia de algunos taxa a disminuir o aumentar su abundancia y frecuencia, tal es el caso de Anacroneuria, Camelobaetidius, Anchytarsus, Hagenulopsis, Claudioperla, Austrelmis, Smicridea, etc. Por otra parte y como punto novedoso para el conicimiento de la zona de estudio, se analizó a la familia Chironomidae a nivel de género, hecho importante para el conocimiento taxónomico de la familia en ríos tropicales de los Andes sobre los 2000 msnm, ya que no hay trabajos a este nivel taxonómico en la zona altoandina. La familia Chironomidae mostro patrones similares a los de la comunidad bentónica en general, sindo los factores relacionados con la altitud (oxígeno y temperatura) lo que determinan en gran medida su distrbución, sin embargo, al igua que el resto de la comunidad la heterogenidad de hábitats mostraron ser de suma importancia para la familia de los quironómidos. Además, la litografía y la biogeografía fueron dos factores que determinan la composición de esta familia. Con esta visión general, se analizaron los patrones de biodiversidad de estos ríos, donde se determinó que la comunidad bentónica altoandina tiene una amplia variabilidad en la diversidad local mientras que si analizamos la diversidad Gamma hay una tendencia a disminuir tanto a medida que la altitud y la latitud aumentan. Por su parte se evidenció cambios en la composición de la comunidad, la cual fue evidente también en ambos gradientes, sin embargo debido a la amplia heterogeneidad ambiental fue necesario analizar la reposición de especies a diferentes escalas de agrupación ya que sin esta corrección los cambios ambientales locales no permiten visualizar los patrones existentes en la comunidad, indicandonos la importancia de los factores locales en la biodiversidad regional. Finalmente, y con la recopilación de la estructura, composición y distribución de la fauna béntica, así como de la variabilidad ambiental tanto natural como antropogénica, se desarrolló un índice multimétrico que nos permite evaluar la calidad ecológica de los ríos altoandinos aplicable a una zona geográfica amplia. Los análisis previos al desarrollo del índice multimétrico demostraron que la variabilidad de la zona alta (localidades de páramo y puna) y la zona baja (localidades de bosque montano) era diferente. Posteriormente usando a las comunidades de macroinvertebrados acuáticos de las localidades de referencia se determinaron a dichas zonas como tipologías diferentes, las cuales se usaron para desarrollar el IMEERA-B (Bosque) y el IMEERA-P (Páramos y Punas). En nuestro estudio en la zona baja el gradiente de presión está determinado por la contaminación orgánica y la degradación hidromorfológica, y en la zona alta el gradiente está influenciado por la contaminación orgánica y la heterogeneidad del hábitat. Finalmente, se determinaron 6 métricas para IMEERA-B que evalúan la riqueza, el hábito y la tolerancia/intolerancia, y para el IMEERA-P se determinaron 4 métricas que evalúan la riqueza y la tolerancia/intolerancia. / STRUCTURE AND COMPOSITION OF AQUATIC MACROINVERTEBRATES COMMUNITIES IN HIGHLAND ANDEAN RIVERS OF ECUADOR AND PERU. DESIGN OF A MEASURE OF WATER QUALITY WITH MULTIMETRIC INDEXES In this thesis we sampled Highland Andean Rivers above 2000 m a.s.l. (tropical andean highland rivers) which are distributed in a wide geographical region of the North Andes (Ecuador) and Central Andes (Peru) in South America. In total 123 sites were sampled in dry season, which were selected taking into account the anthropogenic influence gradient, ranging from no alteration, little alteration (i.e., reference) to highly altered. The physico-chemical caracteristics of rivers showed a high altitud influence. We recorded a decrease in both temperature and oxygen as altitude increases. Habitat heterogeneity and the riverine forest quality were identified as determinant enviromental characteristics regarding the andean higland rivers studied. The mineralization show differences between the morphotectonics groups, while were the conductivity was higher at the south, depending on the geomorphology of each zone. The sampled macroinvertebrate assemblages were influenced by both latitudinal and altitudinal gradients. In detail, assemblages showed different gradient responses (positive or negative), depending of the organism and its requirements. The patterns of abundance and richness are probably determined by the environmental variability observed, and described by the temperature, oxygen, habitat heterogeneity and the presence, and absence of riverine forest. The family Chironomidae, as we expected, showed different responses depending of the genus, while the composition of the family was determined mainly by temperature, oxygen, lithography. and biogeography. We also studied the biodiversity patterns of Highland Andean Rivers rivers. The benthic community assemblage showed a high variability at local diversity (alpha diversity), while the gamma diversity decreased in both latitude and altitude gradients. Moreover, the community presented some discontinuities in the beta diversity. Regarding latitudinal gradient, the composition of assemblage changed in each morphological group, while altitude changes were described by vegetation types (mountain forest or páramo-puna) or presence or absence of riverine forest. Finally, using the aquatic macroinvertebrate communities of the reference sites, two different zones were identified as distinct from each other: from 2000 to 3500 m a.s.l and those sites at altitudes higher than 3500 m a.sl.. For such reasons two versions of a multi-metric index - the IMEERA index - were developed. The IMEERA B index includes six metrics evaluating richness, habit and tolerance/intolerance. The IMEERA P index was calculated using four metrics evaluating richness and tolerance/intolerance. Results showed that in lower altitudes (Bosque river type, IMEERA-B index), the pressure gradient was driven by the organic pollution and the hydromorphological degradation, while in higher altitudes (Páramo and Puna river types; IMEERA-P river type), the gradient was driven by the organic pollution and the habitat heterogeneity.