Abstract In this thesis, I examine two important aspects surrounding salmonid reproductive ecology, namely: (i) the problems with passing obstructions during migratory spawning runs and (ii) how the early life stages in boreal streams are influenced by increased levels of fine-grained particulate matter from drained peatlands. These aspects are not only critical to salmonid reproductive success but have grave implications regarding environmental quality and species conservation. Spawning runs can be re-established by constructing fishways at obstructions but the efficiency of fishways depends on several factors. The passage of multi-sea-winter salmon was enhanced in the Isohaara fishway by increasing its water flow and by creating a small waterfall at the entrance. The fishway, which consists of vertical slot and Denil sections, proved to be unsuitable for most freshwater fish, whitefish and river lamprey, whereas salmonids, once they had entered, successfully negotiated the fishway. In fishway design, the migratory behaviour and the demands of the species of interest should be considered. For salmonids, priority should be given to the attractiveness of the fish entrance. When there is a migration corridor, the availability and the quality of spawning and rearing habitats has a major effect on the success of restoration projects. In the humic rivers studied, the survival of incubated brown trout eggs was lower in riffles susceptible to increased levels of fine-grained particulate matter from drained peatlands. Additionally, an increase in the Fe content of high molecular weight dissolved organic matter followed by its precipitation and sedimentation was proposed to be involved. Correspondingly, the recapture rates of stocked yearling salmon were lower in the affected riffles, individual salmon being smaller and thinner and having less food in their stomachs than reference salmon. Based on these results, it seems probable that peatland drainage, by influencing the incubation success of salmonid embryos and the foraging, growth and survival of juveniles, eventually affects the number and quality of smolts produced. In future, such water pollution control measures should be implemented that would enhance the success of natural spawning and help ensure environmental quality.

Abstract Peatland drainage changes catchment conditions and increases the transport of suspended solids (SS) and nutrients. New knowledge and management methods are needed to reduce SS loading from these areas. This thesis examines sediment delivery and erosion processes in a number of peatland drainage areas and catchments in order to determine the effects of drainage on sediment and erosion dynamics and mechanics. Results from studies performed in peat mining, peatland forestry and disturbed headwater catchments in Finland are presented and potential sediment load management methods are discussed for drainage areas and headwater brooks. Particular attention is devoted to erosion of organic peat, sediment transport and methods to reduce the impacts of peatland drainage in boreal headwaters. This thesis consists of six articles. The first and second papers focus on the erosion and sediment transport processes at peat harvesting and peatland forestry drainage networks. The results indicate that in-channel processes are important in drained peatland, since the drainage network often constitutes temporary inter-storm storage for eroding and transporting material. Sediment properties determine the bed sediment erosion sensitivity, as fluffy organic peat sediment consolidates over time. As flashiness and peak runoff control sediment entrainment and transport from drained peatland areas, water quality management should include peak runoff management. The third, fourth and fifth papers studies use and application of peak runoff control (PRC) method to the peat harvesting and peatland forestry conditions for water protection. Results indicate that effective water quality management in drained peatland areas can be achieved using this method. Installation of the PRC structures is a useful and cost-effective way of storing storm runoff waters temporarily in the ditch system and providing a retention time for eroded sediment to settle to the ditch bed and drainage network. The main effect of the PRC is on SS and SS-bound nutrients. The sixth paper is concentrated to test new restoration structure to be used in degraded headwater brooks. The results show that addition of woody restoration structures to the channel is effective and simple sediment management methods in headwater areas. New information provided in this thesis on sediment erosion and transport processes in drained peatland areas can help to improve water quality control in these areas. In-channel processes are important for both peatland uses, since the drainage network often constitutes temporary inter-storm storage for eroding and transporting material. Therefore, controlling these processes is a key to effective water quality management, which can be achieved using the PRC method in drainage areas or by utilisation of natural fluvial processes in natural channels downstream.

Abstract As human activities are increasingly affecting natural communities, many communities are impacted by multiple stressors and their interactions. Understanding how natural and anthropogenic stressors act individually and in concert is essential for managing and conserving natural ecosystems efficiently. In this thesis I studied how geology-related natural acidity, land drainage and their interaction affect biological communities and leaf decomposition in boreal headwater streams. I further assessed the concordance of communities along natural and anthropogenic stressor gradients. As model organisms, I used benthic diatoms, bryophytes, invertebrates and leaf-decomposing fungi. I showed that geology-related natural acidity constitutes a strong environmental filter for stream communities, reducing species richness and changing community composition. Community concordance was also generally strongest along the natural acidity gradient. However, natural acidity mostly did not homogenize communities nor did it affect leaf decomposition by fungi. Effects of peatland drainage differed between the two stream types, being mainly sedimentation in the circumneutral streams and increasing metal concentrations in the acid streams. Overall, changes in community composition were better able than pure species richness to track single stressor impacts. Furthermore, fungal assemblages were more homogeneous and decomposition rates slower in drained acidic sites than in any other stream type. Thus the drainage-induced shift in water chemistry in the acidic streams seems to constitute an even stronger environmental filter than sedimentation. Conservation planning needs to give special attention to these vulnerable, naturally stressful ecosystems. / Tiivistelmä Ihmistoiminnan vaikuttaessa yhä enemmän luonnon elinympäristöihin eliöyhteisöihin kohdistuu usein samanaikaisesti monenlaisia paineita. Ekosysteemien tehokas hoitaminen ja suojelu edellyttävät tarkkaa tietoa siitä, miten luonnollinen stressi ja ihmistoiminta yhdessä ja erikseen vaikuttavat ekosysteemeihin. Väitöskirjassani tutkin, kuinka geologiasta johtuva luonnollinen happamuus ja metsäojitus vaikuttavat boreaalisten purojen eliöyhteisöihin ja lehtikarikkeen hajotukseen. Tarkastelin myös eliöryhmien yhdenmukaisuutta ihmistoimintagradientilla ja luonnollisella stressigradientilla. Malliorganismeinani olivat piilevät, vesisammalet, pohjaeläimet ja hajottajasienet. Väitöskirjassani osoitan, että geologiasta johtuva puroveden happamuus toimii merkittävänä ympäristösuodattimena purojen eliöyhteisöille vähentäen lajirunsautta ja muokaten lajistoa. Myös eliöryhmien lajistovaihtelu oli yhdenmukaisinta luonnollisella happamuusgradientilla. Toisaalta luonnollinen happamuus ei vaikuttanut merkittävästi lehtikarikkeen hajotukseen tai purojen väliseen sieniyhteisöjen monimuotoisuuteen. Metsäojituksen fysikaalis-kemiallinen vaikutus erosi purotyypeittäin: pH-neutraaleissa puroissa ojitus pääosin lisäsi pohjan hiekoittumista, kun taas happamissa puroissa veden metallipitoisuudet kasvoivat entisestään. Yleisesti ottaen sekä luonnollisen happamuuden että metsäojituksen vaikutukset näkyivät parhaiten muutoksina eliöyhteisöjen lajikoostumuksessa. Lisäksi ojitetuissa happamissa puroissa hajottajasieniyhteisöjen lajistot olivat keskenään samankaltaisempia ja lehtikarikkeen hajotus hitaampaa kuin muissa purotyypeissä. Metsäojituksen aikaansaama muutos luonnollisesti happamien purojen vesikemiassa näyttää siis olevan jopa merkittävämpi ympäristösuodatin kuin pohjan hiekoittuminen. Luonnollisesti stressattujen elinympäristöjen herkkyys maankäytön muutoksille tulisikin huomioida ympäristön hoidon suunnittelussa nykyistä paremmin.