RESUMO
Local changes caused by dams can have drastic consequences for ecosystems, not only because they change the water regime but also the modification on lakeshore areas. Thus, this work aimed to determine the changes in soil moisture after damming, to understand the consequences of this modification on the arboreal community of dry forests, some of the most endangered systems on the planet. We studied these changes in soil moisture and the arboreal community in three dry forests in the Araguari River Basin, after two dams construction in 2005 and 2006, and the potential effects on these forests. For this, plots of 20 m x 10 m were distributed close to the impoundment margin and perpendicular to the dam margin in two deciduous dry forests and one semi-deciduous dry forest located in Southeastern Brazil, totaling 3.6 ha sampled. Besides, soil analysis were undertaken before and after impoundment at three different depths (0-10, 20-30 and 40-50 cm). A tree (minimum DBH of 4.77 cm) community inventory was made before (TO) and at two (T2) and four (T4) years after damming. Annual dynamic rates of all communities were calculated, and statistical tests were used to determine changes in soil moisture and tree communities. The analyses confirmed soil moisture increases in all forests, especially during the dry season and at sites closer to the reservoir; besides, an increase in basal area due to the fast growth of many trees was observed. The highest turnover occurred in the first two years after impoundment, mainly due to the higher tree mortality especially of those closer to the dam margin. All forests showed reductions in dynamic rates for subsequent years (T2-T4), indicating that these forests tended to stabilize after a strong initial impact. The modifications were more extensive in the deciduous forests, probably because the dry period resulted more rigorous in these forests when compared to semideciduous forest. The new shorelines created by damming increased soil moisture in the dry season, making plant growth easier. We concluded that several changes occurred in the T0-T2 period and at 0-30 m to the impoundment, mainly for the deciduous forests, where this community turned into a "riparian-deciduous forest" with large basal area in these patches. However, unlike other transitory disturbances, damming is a permanent alteration and transforms the landscape to a different scenario, probably with major long-term consequences for the environment.
Assuntos
Umidade , Solo , Árvores/crescimento & desenvolvimento , Brasil , Monitoramento Ambiental , Estações do AnoRESUMO
Local changes caused by dams can have drastic consequences for ecosystems, not only because they change the water regime but also the modification on lakeshore areas. Thus, this work aimed to determine the changes in soil moisture after damming, to understand the consequences of this modification on the arboreal community of dry forests, some of the most endangered systems on the planet. We studied these changes in soil moisture and the arboreal community in three dry forests in the Araguari River Basin, after two dams construction in 2005 and 2006, and the potential effects on these forests. For this, plots of 20m x10m were distributed close to the impoundment margin and perpendicular to the dam margin in two deciduous dry forests and one semi-deciduous dry forest located in Southeastern Brazil, totaling 3.6ha sampled. Besides, soil analysis were undertaken before and after impoundment at three different depths 0-10, 20-30 and 40-50cm. A tree minimum DBH of 4.77cm community inventory was made before T0 and at two T2 and four T4 years after damming. Annual dynamic rates of all communities were calculated, and statistical tests were used to determine changes in soil moisture and tree communities. The analyses confirmed soil moisture increases in all forests, especially during the dry season and at sites closer to the reservoir; besides, an increase in basal area due to the fast growth of many trees was observed. The highest turnover occurred in the first two years after impoundment, mainly due to the higher tree mortality especially of those closer to the dam margin. All forests showed reductions in dynamic rates for subsequent years T2-T4, indicating that these forests tended to stabilize after a strong initial impact. The modifications were more extensive in the deciduous forests, probably because the dry period resulted more rigorous in these forests when compared to semideciduous forest. The new shorelines created by damming increased soil moisture in the dry season, making plant growth easier. We concluded that several changes occurred in the T0-T2 period and at 0-30m to the impoundment, mainly for the deciduous forests, where this community turned into a riparian-deciduous forest with large basal area in these patches. However, unlike other transitory disturbances, damming is a permanent alteration and transforms the landscape to a different scenario, probably with major long-term consequences for the environment.
Los cambios locales provocados por las represas pueden tener consecuencias para un ecosistema, ya que no solo cambian el régimen de las aguas, sino que también modifican las áreas a la orilla de los lagos. Por lo tanto, este trabajo tuvo como objetivo observar los cambios en la humedad del suelo después de la construcción de represas, para entender las consecuencias de esta modificación a la comunidad arbórea de los bosques secos, que son uno de los sistemas más amenazados del planeta. Después de la construcción de tres represas, se estudiaron los cambios en la humedad del suelo y la comunidad arbórea en 3 bosques secos de la cuenca del río Araguari, en donde se construyeron dos represas en 2005 y 2006. Se demarcaron parcelas de 20x10m que se distribuyeron cerca y perpendicular al margen de la represa en dos bosques secos caducifolios y un bosque seco semideciduo ubicado en el sureste de Brasil, en total se muestrearon 3.6 hectáreas. Se realizó un análisis de la humedad del suelo antes y después de la construcción del embalse en tres profundidades 0-10, 20-30, 40-50cm. El inventario de la comunidad arbórea DAP de 4.77cm se realizó antes T0, dos T2 y cuatro T4 años a partir de la retención del agua. Además se calcularon las tasas anuales dinámicas de todas las comunidades, y se utilizaron pruebas estadísticas para confirmar los cambios en la humedad del suelo y las comunidades de árboles. Los análisis confirmaron aumento de humedad del suelo en todos los bosques, especialmente durante la estación seca y en los lugares más cercanos al embalse, con un aumento del área basal debido al rápido crecimiento de muchos árboles. El mayor volumen de modificaciones se produjo en los primeros dos años después de La construcción del embalse, principalmente debido a la mayor mortalidad de los árboles más cerca del margen de la represa. Sin embargo, todos los bosques mostraron reducción de las tasas dinámicas en los años siguientes T2-T4, lo que indica que estos bosques tienden a estabilizarse después de un fuerte primer impacto. Las modificaciones fueron más severas en los bosques caducifolios, probablemente debido a una estación seca más severa en estos bosques en comparación con el semideciduo. Las nuevas márgenes creadas por el embalse aumentaron la humedad del suelo en la época seca facilitando el crecimiento de muchas plantas. Se concluye que los cambios que se produjeron en el período de T0-T2 y de 0-30m del embalse, principalmente en los bosques caducifolios estan transformando estas comunidades en bosque de ribera-caducifolia con gran área basal en estos parches. Sin embargo, este impacto es diferente a otras alteraciones transitorias, así la construcción del embalse es un cambio permanente y transforma el paisaje en otro escenario, probablemente con importantes consecuencias a largo plazo para el ambiente.
Assuntos
Umidade , Solo , Árvores/crescimento & desenvolvimento , Brasil , Monitoramento Ambiental , Estações do AnoRESUMO
A combinação de algumas características ecológicas das espécies para a formação dos chamados grupos ecológicos tem ajudado a identificar alguns padrões para as diferentes formações vegetais. A partir da análise fitossociológica e da estrutura diamétrica das espécies arbóreas de um fragmento de floresta estacional semidecidual, este estudo pretendeu classificar as espécies em grupos ecológicos e aferir o estado de conservação deste remanescente. Foram amostrados todos os indivíduos arbóreos com CAP > 15 cm, presentes em 25 parcelas (20x20 m) e as espécies foram classificadas por grupos sucessionais e síndrome de dispersão. Foram registrados 976 indivíduos distribuídos em 86 espécies, pertencentes a 38 famílias. As espécies secundárias iniciais apresentaram maiores valores na riqueza de espécies, densidade de indivíduos e valor de importância, seguido das espécies secundárias tardias e das pioneiras que tiveram pouca representatividade. Em relação à síndrome de dispersão pôde-se observar composição de 60 espécies zoocóricas, 21 anemocóricas e cinco autocóricas. A análise da distribuição de diâmetros para os grupos sucessionais sugeriu bom recrutamento para as secundárias iniciais e tardias e problemas na regeneração para o grupo das pioneiras. Estes resultados quando comprados com outros estudos similares realizados nas FES da região permitiram inferir que a floresta estudada se encontrou num estádio intermediário de desenvolvimento sucessional.
The combination of some species ecological characteristics for the creation of ecological groups has helped to identify the broader significance and validity of the patterns currently known for different vegetation types. From the analysis of phytosociological and diameter structure of tree species in a semideciduous forest fragment, this study aimed to classify the species in ecological groups and assess the conservation status of this remnant and possible disruptions in the structure of some populations. We sampled all trees with CBH > 15 cm, present in 25 plots (20x20 m). Species were classified by successional groups and dispersal syndrome. We recorded 976 individuals in 86 species belonging to 38 families. The sample had a composition of 42 early secondary species (48.8%), 27 late secondary (31.4%), 16 pioneer (18.6%) and one unclassified (1.2%). The group formed by early secondary showed higher density and relative frequency, while the group formed by the late secondary species stands out with higher values of relative dominance. Regarding the dispersal syndrome, 60 species presented zoochoric dispersal, 21 anemochoric and five autochorich. Diametric distribution analysis for the successional groups suggested problems in regeneration for the pioneer group. These results suggest that the studied forest is in an intermediate stage of successional development, moving toward a late stage, mainly due to the presence and dominance of some late successional species as to the low density of pioneer species
Assuntos
Biota , Florestas , Dispersão Vegetal , ÁrvoresRESUMO
Foi realizado o levantamento fitossociológico de um fragmento de floresta estacional semideciduallocalizada na reserva legal da Fazenda Irara, Uberlândia - MG. O estudo analisou um hectare do fragmento utilizando 25 parcelas contíguas e sistemáticas de 20 x 20 m, onde todos os indivíduos vivos arbóreos com circunferência a altura do peito maior que 15 cm foram amostrados e identificados. As espécies foram classificadas quanto aos grupos sucessionais e síndromes de dispersão. Foram amostrados 945 indivíduos distribuídos em 73 espécies, 65 gêneros e 36 famílias. O valor de equabilidade e do índice de diversidade de Shannon foram 0,81 e 3,47, respectivamente. Neste fragmento 17% são espécies pioneiras, 49% secundárias iniciais e 34% secundárias tardias, demonstrando um estágio intermediário de sucessão. Ocorre alta porcentagem de espécies zoocóricas (77%), podendo indicar alta atividade da fauna dispersora.
The phytosociological survey was realized in a semideciduous forest fragment located in the legal reserve of Irara Farm, Uberlândia - MG. This study analyzed one hectare of the fragment using 25 adjacent andsystematic plots of 20 x 20 m, where all the alive tree individuals with perimeter at breast height higher than 15 cm wereincluded and identified. The species were classified as successional groups and dispersal syndromes. Were sampled 945 individuals in 73 species, 65 genres and 36 families. The value of equability and Shannons diversity were 0,81 and 3,47, respectively. In this fragment 17% were pioneer species, 49% early secondary species and 34% late secondary species, demonstrating an intermediary succession stage. Occur high percentage of zoochoric species (77%), that can indicate high activity of disperser fauna.