Matches in SemOpenAlex for { <https://semopenalex.org/work/W1683802404> ?p ?o ?g. }
- W1683802404 abstract "The identification of factors that cause the patchy distribution of organisms in space and time within natural ecosystems is a central concern in ecology. In running waters, disturbance by bed-moving flows has been recognized to contribute to this patchiness, but the mechanisms behind this process are still poorly understood. Recent research has revealed that most bed-moving spates and floods cause a small-scale mosaic of stream bed patches of different substratum stabilities (sediment scour, sediment deposition, and stable patches). The aim of the present research was to investigate the separate and combined roles of this “local disturbance history” and microhabitat parameters in determining the small-scale distributions of benthic stream organisms (bacteria, algae and invertebrates).The first three chapters of my thesis investigate bacteria, algae and invertebrates after natural spates and floods in two gravel-bed streams, the Schmiedlaine in Bavaria, Germany, and the Kye Burn in the South Island of New Zealand. The final chapter describes a manipulative experiment in the Schmiedlaine in which the stream bed was disturbed manually to obtain a better understanding of how disturbance history affects stream organisms.Local bed movement patterns during several natural disturbances were determined using metal-link scour chains. The same chains were also used as reference points when selecting stream bed patches for manipulation during the experimental disturbance. Quantitative samples were collected several times from random sites before each disturbance and from scour, fill and stable patches after each disturbance. In addition to sampling bacteria, algae and invertebrates, we measured primary production under controlled conditions in both streams and bacterial production in the Kye Burn. For each sampling site, we determined several abiotic and biotic microhabitat parameters that are known to influence the distributions of stream biota, e.g. water depth, substratum composition, near-bed current velocity and standing stock of particulate organic matter (POM).The results of the correlative studies suggest that local disturbance history plays an important role in determining the small-scale distributions of stream bacteria, algae and invertebrates. Disturbance history was related to distributions of all three organism groups both directly and indirectly (via effects on habitat parameters) and significant habitat parameter effects revealed previously undetected history effects in several cases, indicating a strong interaction between disturbance history and the better explored habitat parameters.Bacterial microdistribution was related directly to disturbance history at least as often as to any of the other nine studied habitat parameters (except for the surface area of the sampled stones in the Schmiedlaine). The relationships of local disturbance history with algal distributions were not quite as strong. In the flood-prone Schmiedlaine, substratum characteristics and current velocity were related to algal distribution at least as often as disturbance history. In the relatively more stable Kye Burn, there were no direct influences of disturbance history on the algae. Substratum characteristics, water depth, current velocity and POM were the habitat parameters with the highest numbers of significant relationships. However, disturbance history also influenced algal distribution indirectly in both streams, and this indirect influence was particularly strong in the Kye Burn. Primary production was always similar across bed stability types in both streams. Averaged across both streams, invertebrate distribution was related only to near-bed current velocity more often than to disturbance history. In the Kye Burn, disturbance history and water depth were the habitat parameters that were related most often to invertebrate distributions. Further important parameters for invertebrates were substratum size and epilithic algal biomass.The observed relationships of benthic densities to the investigated habitat parameters were largely in accordance with previous microhabitat studies for benthic algae and invertebrates. These results also show that benthic bacteria in streams appear to be influenced by similar habitat parameters as benthic algae and invertebrates.The findings of the experimental disturbance in the Schmiedlaine generally supported those of the correlative research, lending more weight to the generality of the results. Local disturbance history influenced directly algal microdistribution in the stream bed most often, followed by near-bed current velocity, total invertebrate density and the surface area of the sampled stone. Primary production was also always similar between the three bed stability types. In contrast to the benthic algae and the correlative study on bacteria, bacterial microdistribution in the experiment was influenced directly solely by stone surface area. However, disturbance history had a strong indirect influence via habitat parameters on bacterial distribution. For invertebrate distribution, disturbance history was the parameter with the second-highest number of significant relationships after current velocity. Indirect effects of disturbance history on the stream organisms were similarly common as in the correlative studies and significant habitat parameter effects revealed previously undetected history effects in several cases, confirming the strong interaction between disturbance history and the better- explored habitat parameters.The combined findings of the present research provide substantial evidence that local disturbance history is an important, and previously unrecognised factor contributing to the patchy distribution of stream organisms in space and time." @default.
- W1683802404 created "2016-06-24" @default.
- W1683802404 creator A5042037698 @default.
- W1683802404 date "2005-10-28" @default.
- W1683802404 modified "2023-09-24" @default.
- W1683802404 title "The roles of local disturbance history and microhabitat parameters for stream biota" @default.
- W1683802404 cites W1273791837 @default.
- W1683802404 cites W1485232674 @default.
- W1683802404 cites W1489838709 @default.
- W1683802404 cites W1495276840 @default.
- W1683802404 cites W1505889214 @default.
- W1683802404 cites W1510412811 @default.
- W1683802404 cites W1515221271 @default.
- W1683802404 cites W1517515745 @default.
- W1683802404 cites W1561387878 @default.
- W1683802404 cites W1582066981 @default.
- W1683802404 cites W1594857605 @default.
- W1683802404 cites W1605950248 @default.
- W1683802404 cites W1758349511 @default.
- W1683802404 cites W1779993084 @default.
- W1683802404 cites W1874459609 @default.
- W1683802404 cites W1966985018 @default.
- W1683802404 cites W1967943117 @default.
- W1683802404 cites W1968076659 @default.
- W1683802404 cites W1968932909 @default.
- W1683802404 cites W1976137466 @default.
- W1683802404 cites W1977141508 @default.
- W1683802404 cites W1979067113 @default.
- W1683802404 cites W1984062300 @default.
- W1683802404 cites W1984499410 @default.
- W1683802404 cites W1985548933 @default.
- W1683802404 cites W1985845539 @default.
- W1683802404 cites W1994020089 @default.
- W1683802404 cites W1996922079 @default.
- W1683802404 cites W1998846889 @default.
- W1683802404 cites W1999739384 @default.
- W1683802404 cites W2001449898 @default.
- W1683802404 cites W2001594506 @default.
- W1683802404 cites W2004946302 @default.
- W1683802404 cites W2007131168 @default.
- W1683802404 cites W2010614703 @default.
- W1683802404 cites W2012548888 @default.
- W1683802404 cites W2014664302 @default.
- W1683802404 cites W2014724154 @default.
- W1683802404 cites W2016654357 @default.
- W1683802404 cites W2017142906 @default.
- W1683802404 cites W2019312920 @default.
- W1683802404 cites W2023830853 @default.
- W1683802404 cites W2025011477 @default.
- W1683802404 cites W2025142465 @default.
- W1683802404 cites W2027497105 @default.
- W1683802404 cites W2032838039 @default.
- W1683802404 cites W2033416936 @default.
- W1683802404 cites W2033431991 @default.
- W1683802404 cites W2035126508 @default.
- W1683802404 cites W2036300713 @default.
- W1683802404 cites W2036680106 @default.
- W1683802404 cites W2039883194 @default.
- W1683802404 cites W2041335173 @default.
- W1683802404 cites W2042184876 @default.
- W1683802404 cites W2043087610 @default.
- W1683802404 cites W2046147250 @default.
- W1683802404 cites W2047785769 @default.
- W1683802404 cites W2049403699 @default.
- W1683802404 cites W2050645339 @default.
- W1683802404 cites W2052142819 @default.
- W1683802404 cites W2053229370 @default.
- W1683802404 cites W2053380801 @default.
- W1683802404 cites W2053522635 @default.
- W1683802404 cites W2054637019 @default.
- W1683802404 cites W2054760115 @default.
- W1683802404 cites W2057221944 @default.
- W1683802404 cites W2057930778 @default.
- W1683802404 cites W2058745938 @default.
- W1683802404 cites W2059831730 @default.
- W1683802404 cites W2060793884 @default.
- W1683802404 cites W2063764235 @default.
- W1683802404 cites W2064673022 @default.
- W1683802404 cites W2065339591 @default.
- W1683802404 cites W2065634928 @default.
- W1683802404 cites W2067507596 @default.
- W1683802404 cites W2067659920 @default.
- W1683802404 cites W2071748824 @default.
- W1683802404 cites W2073835300 @default.
- W1683802404 cites W2075197853 @default.
- W1683802404 cites W2075670582 @default.
- W1683802404 cites W2079987422 @default.
- W1683802404 cites W2081632123 @default.
- W1683802404 cites W2082823622 @default.
- W1683802404 cites W2084148941 @default.
- W1683802404 cites W2085060412 @default.
- W1683802404 cites W2085643826 @default.
- W1683802404 cites W2092613863 @default.
- W1683802404 cites W2092813639 @default.
- W1683802404 cites W2094194527 @default.
- W1683802404 cites W2095826095 @default.
- W1683802404 cites W2096256585 @default.
- W1683802404 cites W2099530654 @default.
- W1683802404 cites W2102174826 @default.
- W1683802404 cites W2102250383 @default.