Thesis (doctoral)--Swedish University of Agricultural Sciences, 2003. / Appendix includes four manuscripts and papers co-authored with others. Includes bibliographical references. Also issued electronically via World Wide Web in PDF format; online version lacks appendix of papers.

Diss. (sammanfattning) Uppsala : Uppsala universitet, 2006. / Härtill 5 uppsatser.

A breeding of seven European perch (Perca fluviatilis) groups of various origin was carried out under experimental conditions at 20°C temperature since the hatching of larval fish up till the age of 278 days, with intensive feeding using BioMar Inicio plus 0,55mm fodder with 15% fat content and BioMar Inicio plus 0,1mm fodder with 18% of fat content in later initial feeding. The average final weight of fish in the individual groups ranged between 79,4g and 27,63g. Mass yield statement (mass fraction of skinless filets, on the total mass), basic chemical analysis of filets (dry matter, crude protein, lipids and ash content) and organoleptic evaluation of musculature quality were carried out in the final stage of the growth test. No influence of the fish origin on the mass yield was detected. The average values ranged between 35,41% and 32,21%, but an influence of origin on crude protein content was discovered. The lowest values were determined in the population from the north of Germany 77,5% and the highest values on the contrary were determined in the population from the Štrbské Pleso lake 80,35%. The lowest lipids content was determined again in the population from the north of Germany 7,14%, while the highest fat content was detected in the population from Slovakia 8,66%. The results of organoleptic analysis didn't show substantial differences. Overall it can be stated that the monitoring didn't prove any substantial influences of fish origin on the parameters observed, which is confirmed by results of similar observations carried out by other authors e.g. with trout and carp.

The growth in perch (Perca fluviatilis) is generally slow but varies depending on living conditions. For instance, growth is more rapid in warmer water temperature and when there is reduced intra- and interspecific competition for food. The cormorant (Phalacrocorax carbo) was established in Lake Tåkern in 1994 and could possibly have an effect on the growth of perch due to predation of small perch and competition for food with larger perch. The aim of this study was to examine whether the growth of perch had changed from year 1978, when a previous study on perch was preformed, to a recent fish survey in 2019 in lake Tåkern. The aim of the study was to assess if any changes in growth could be explained by predation and competition from cormorants. The aim of the study was also to examine whether there was a difference in growth between females and males. The age was determined by using the opercular bone and an age analysis was done to compare the growth between year 1978 and 2019. The results showed that the growth of 1-3-year-old perch was higher in year 1978 than in 2019. This was contrary to the expected outcome, that the predation from cormorants should had decreased competition for young perch in 2019. Previous studies on perch have shown a difference between males and females with an age over 2 years old. However, by the results there is no support that differences between males and females have affected the difference in growth at ages 1-3 years old between 1978 and 2019. As there was no difference between the sexes, any difference in growth between 1978 and 2019 could not be explained by an altered sex ratio. Since there were only a few older individuals 2019 comparison of growth for individuals over 4 years old were not possible to do. The conclusion is that there was no support that cormorants reduced the competition for smaller perch. Cormorants could possibly have contributed to low number of older individuals in 2019.

Detta examensarbete syftade till att ta fram ett underlag för en regional åtgärdsplan avseende dibenso-p-dioxiner och dibensofuraner, gemensamt benämnda som PCDD/F eller dioxiner, i Gävleborgs län. Länet har historiskt varit ett av de mest utsatta områdena i Sverige beträffande dessa föroreningar och höga koncentrationer i bland annat strömming har medfört att denna inte får saluföras i övriga EU.   I arbetet har resultaten från den rådande forskningen på området studerats för att få kunskap om nuvarande källor och möjliga förklaringar till de fortsatt förhöjda koncentrationerna av dioxiner. Därefter har data från tidigare undersökningar av dioxinkoncentrationer i Gävleborgs län samlats in, sammanställts och använts för att studera hur koncentrationerna varierar geografiskt inom länet. Principalkomponentanalys (PCA) av specifika dioxinkongeners koncentrationer har sedan använts för att försöka identifiera verksamhetstyper som potentiellt kan ha bidragit till föroreningarna på olika platser - en analys som dock är behäftad med stora osäkerheter. De insamlade provresultaten har även använts för att genom massbalansmodellering undersöka återhämtningen i två känt förorenade fjärdar i länet; Norrsundet och Gårdsfjärden. Utifrån resultaten av ovanstående analyser diskuterades även nyttan av att genomföra eventuella åtgärder för att reducera halterna i kraftigt förorenade områden.   Proverna som sammanställts visade klara geografiska skillnader i sedimentkoncentration, och till viss del även i koncentration i muskel från abborre, vilket visar på en stark betydelse av lokala källor i vissa områden. Bland strömmingsproverna kunde inget liknande samband ses. Detta kan förklaras av att det migrerande beteendet hos strömming gör att fisken under sin livstid exponeras för varierande föroreningsnivåer i olika områden, medan abborren är mer stationär även som vuxen. Principalkomponentanalysen gav, för vissa prover, indikationer kring vilken typ av verksamhet som bidragit till de uppmätta koncentrationerna. Dessa resultat är dock mycket osäkra och bör inte på egen hand användas som underlag för att fastställa föroreningskällor. Massbalansmodelleringen visade att PCDD/F-koncentrationen i sediment inte har någon betydelse för koncentrationen i vattenmassan utan att inflödet från omgivande hav dominerar även i avgränsade fjärdar. De modellerade jämviktskoncentrationerna mellan sediment och vattenmassa indikerade även att koncentrationerna i sediment kommer fortsätta överskrida somliga gränsvärden tills koncentrationen i vattenmassan reducerats, vilket även stöds av att dessa gränsvärden överskreds i majoriteten av de sammanställda proverna.   Baserat på samtliga ovannämnda resultat drogs slutsatsen att lokala saneringsåtgärder sannolikt inte ger någon effekt på PCDD/F-koncentrationerna i strömming, samt att de inte är tillräckliga för att erhålla sedimentkoncentrationer under samtliga gränsvärden. De kan däremot effektivt minska den exponering som mer stationära organismer som abborre utsätts för i områden med kraftigt förorenade sediment, och kan även ha positiva effekter på förekomsten av andra miljöfarliga ämnen i området. För- och nackdelar måste således övervägas i varje enskilt fall. / The aim of this Master’s Thesis was to provide a basis for a regional plan of action regarding dibenzo-p-dioxins and dibenzofurans, commonly referred to as PCDD/F or dioxins, in Gävle-borg County. This region has historically been one of the Swedish areas most affected by these pollutants, and high concentrations in for example Atlantic herring (Clupea harengus) have resulted in restrictions where some fish species cannot be sold in other EU countries.   In this work, results of current research on the subject were studied in order to gain knowledge about current sources and possible explanations to the continued high concentrations of dioxins. Thereafter, data from earlier investigations of dioxin levels in Gävleborg County have been gathered, compiled and used to study the regional geographic variation of the concentrations. Principal component analysis (PCA) was then used on the concentrations of specific congeners in an attempt to identify source types that might have contributed to the contamination in various sites; this analysis is however marred by uncertainties. The gathered data have also been used to investigate the recovery in two bays with known contaminations, Norrsundet and Gårdsfjärden, using mass balance modelling. The benefits of implementing measures to reduce the PCDD/F-concentrations in highly polluted areas were then discussed based on the results of the above-mentioned analyses.   The measured sediment concentrations, and partly also the concentrations in European perch (Perca fluviatilis), of the compiled samples showed distinct geographic differences, which indicates a strong influence from local sources in some areas. Among the herring samples, no such connection could be seen. This could be explained by the migrating behaviour of adult herring, resulting in an exposure to various levels of contamination in different areas as they migrate, while adult perch has a more stationary behaviour. For some samples, the principal component analysis gave indications on source types that might have contributed to the local contamination levels. These results are however very uncertain and they should not be used as the sole basis when determining emission sources. The mass balance modelling showed that the PCDD/F-concentrations in sediments have no influence on the concentrations in the water body; the inflow from the surrounding sea is predominant also in enclosed bays. The modelled equilibrium concentrations between sediments and water body also indicated that the sediment concentrations will continue to exceed the guideline values until the water concentrations have decreased. This is also supported by the fact that the majority of the samples showed concentrations exceeding these guideline values.   Based on all of the abovementioned results it was concluded that local remediation measures would most likely not affect the PCDD/F-concentrations in herring. It was also concluded that such measures would not suffice to obtain sediment concentrations that fall below all guideline values. They can however be used to lessen the exposure that stationary organisms are subjected to in areas with highly contaminated sediments, and can also have positive effects on the levels of other hazardous substances in the area. Thus, the benefits and disadvantages need to be considered in each specific case.

Dams play an important role in our society, but their negative impacts on aquatic ecosystems have led to a need for conservation efforts to mitigate the negative effects. In some instances, dam removal has been suggested to be the most economically and ecologically beneficial restoration method to improve longitudinal connectivity. This, however, has increased the need of more research about the effects dam removal have on aquatic ecosystems, since the outcomes of this restoration method can be unpredictable. In this study, I investigated ecological impacts of dam removals in Swedish inland waters. I collected field data from five different lakes in Värmland and Dalarna, two lakes with dam removal in 2017/2018 and three without. I studied how dam removal affected different trophic levels of the aquatic ecosystem, where I predicted that a top-down effect would increase abundances of piscivorous European perch (Perca fluviatilis) and zooplankton, but decrease phytoplankton, whereas a bottom-up effect would lead to increases in biomass at all trophic levels (with most pronounced effects on nutrient concentration). If both top-down and bottom-up effects would operate in parallel, all the above mentioned effects could occur. I also predicted that if dam removal affected the fish community, there would be a change in species diversity and fish biomass. Moreover, if perch demography was affected, there would be a change in perch length and abundance of different age classes. To investigate this, I collected data on fish, plankton, nutrients (P, N), DOC, pH and conductivity in the five lakes and compared this with already existing historical data using a BACI design. Two-way ANOVAs were used to study the effects of dam removals on these variables. There were not enough historical data on P concentration or zoo-and phytoplankton to be analyzed statistically. I did, however, conduct correlation analyses with zoo- and phytoplankton. Contradictory to my prediction, the results showed no effect of dam removal on fish biomass or diversity, water chemistry or perch demography in the studied lakes. There was, however, a statistically significant effect of time on Tot-N, with lower values after the years of 2017/2018 (regardless of dam removal). There were also some differences between the lakes in species diversity, concentration of Tot-N, potentially piscivorous perch and perch length. The outcomes of dam removal are unpredictable, as are the expected time-lapse of the effects, which means that changes may yet occur in the studied lakes. Knowledge about ecosystem responses to dam removal enables managers to better predict the effects of dam removal, and thereby facilitate decision makings related to this restoration method. / Dammar spelar en viktig roll i vårt samhälle, men deras negativa påverkan på akvatiska ekosystem har ökat behovet av bevarandeinsatser för att minska de negativa effekterna. I somliga fall har dammutrivning föreslagits vara den mest ekonomiskt och ekologiskt gynnsamma bevarandemetoden för att förbättra longitudinell konnektivitet. Detta har dock ökat behovet av mer forskning gällande dammutrivningars effekter på akvatiska ekosystem, eftersom utfallen av denna bevarandemetod kan vara oförutsägbara. I denna studie undersökte jag dammutrivningars ekologiska effekter i svenska inlandsvatten. Jag samlade data i fält från fem olika sjöar i Värmland och Dalarna, två sjöar med dammutrivningar under 2017/2018 och tre utan. Jag undersökte hur dammutrivning påverkade olika trofiska nivåer i det akvatiska ekosystemet, med förväntningarna att en top-down-effekt skulle öka abundansen av fiskätande abborre (Perca fluviatilis) samt djurplankton, men minska växtplankton, medan en bottom-up-effekt skulle leda till ökad biomassa inom samtliga trofiska nivåer (men med mest effekter på näringskoncentration). Om både top-down- och bottom-up-effekter skulle verka parallellt kunde samtliga ovanstående nämnda effekter förekomma. Jag förväntade även att om dammutrivning påverkade fisksamhället skulle det ske en förändring i artdiversitet och fiskbiomassa. Därtill bör en effekt på demografi hos abborre leda till förändringar i abborrlängd- och abundans i olika åldersklasser. För att undersöka detta samlade jag in data över fisk, plankton, näringsämnen (P, N), DOC, pH och konduktivitet i de fem sjöarna och jämförde detta med redan existerande historiska data med en BACI design. Tvåvägs-ANOVAs användes för att studera effekterna av dammutrivningar på dessa variabler. Det fanns inte tillräckligt med historiska data över P-koncentration eller djur- och växtplankton för att analyseras statistiskt. Jag utförde dock korrelationsanalyser med djur- och växtplankton. I kontrast till min förväntan visade resultaten ingen effekt av dammutrivning på fiskbiomassa- eller diversitet, vattenkemi eller demografi hos abborre i de studerade sjöarna. Det var däremot en statistiskt signifikant effekt av tid på Tot-N, med lägre värden efter 2017/2018 (oberoende av dammutrivning). Det var även en del skillnader mellan sjöarna i artdiversitet, koncentration av Tot-N, potentiellt fiskätande abborre samt abborrlängder. Utfallen av damutrivningar är oförutsägbara, och detsamma gäller tidsintervallet för effekterna, vilket innebär att det fortfarande kan ske förändringar i de studerade sjöarna. Kunskap om ekosystemrespons till dammutrivning möjliggör för förvaltare att lättare bedöma effekter av dammutrivningar, och underlättar därav beslutsfattning relaterat till denna bevarandemetod.