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Sökning: WFRF:(Asplund Anders)

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1.
  • Bignert, Anders, et al. (författare)
  • Comments Concerning the National Swedish Contaminant Monitoring Programme in Marine Biota, 2004
  • 2004
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • This report gives a summary of the monitoring activities within the national Swedishcontaminant programme in marine biota. It is the result from the joint efforts of: theInstitute of Applied Environmental Research at Stockholm University (analyses oforganochlorines), the Centre for Environmental Monitoring at the University of Agriculture(analyses of heavy metals) and the Contaminant Research Group at the Swedish Museumof Natural History (co-ordination, sample collection administration, sample preparation,recording of biological variables, minor additional analyses of organochlorines, storage offrozen biological tissues in the Environmental Specimen Bank for retrospective studies,data preparation and statistical evaluation). The monitoring programme is financiated bythe Environmental Protection Agency in Sweden.The data of concern in this report represent the bioavailable part of the investigatedcontaminants i.e. the part that has virtually passed through the biological membranes andmay cause biological effects. The objectives of the monitoring program in marine biotacould be summarised as follows:• to estimate the levels and the normal variation of various contaminants in marine biotafrom several representative sites, uninfluenced by local sources, along the Swedish coasts.The goal is to describe the general contaminant status and to serve as reference values forregional and local monitoring programmes• to monitor long term time trends and to estimate the rate of found changes.quantified objective: to detect an annual change of 10% within a time period of 10 years with a power of 80%at a significance level of 5%.• to estimate the response in marine biota of measures taken to reduce the discharges ofvarious contaminantsquantified objective: to detect a 50% decrease within a time period of 10 years with a power of 80% at asignificance level of 5%.• to detect incidents of regional influence or widespread incidents of ‘Chernobyl’-character and to act as watchdog monitoring to detect renewed usage of bannedcontaminants.quantified objective: to detect an increase of 200% a single year with a power of 80% at a significance levelof 5%.• to indicate large scale spatial differencesquantified objective: to detect differences of a factor 2 between sites with a power of 80% at a significancelevel of 5%.• to explore the development and regional differences of the composition and pattern ofe.g. PCB’s, HCH’s and DDT’s as well as the ratios between various contaminants.• the time series are also relevant for human consumption since important commercial fishspecies like herring and cod are sampled. A co-operation with the Swedish FoodAdministration is established. Sampling is also co-ordinated with SSI (Swedish RadiationProtection Authority) for analysing radionuclides in fish and blue mussels (HELCOM,1992).• all analysed, and a large number of additional specimens, of the annually systematicallycollected material are stored frozen in the Environmental Specimen Bank.. This invaluable4material enables future retrospective studies of contaminants impossible to analyse today aswell as control analyses of suspected analytical errors.• although the programme is focused on contaminant concentration in biota, also thedevelopment of biological variables like e.g. condition factor, liver somatic index (LSI) andfat content are monitored at all sites. At some few sites, integrated monitoring with fishphysiology and population are running in co-operation with the Swedish Fishery Board.• experiences from the national program with several time series of over 20 years can beused in the design of regional and local monitoring programmes.• the perfectly unique material of high quality, long time series is further used to explorerelationships among biological variables and contaminants concentrations in varioustissues; the effects of changes in sampling strategy, the estimates of variance componentsand the influence on the concept of power etc.• the accessibility of high quality data collected and analysed in a consistent manner is anindispensable prerequisite to evaluate the validity of hypothesis and models concerning thefate and distribution of various contaminants. It could furthermore be used as input of ‘real’data in the ongoing model building activities concerning marine ecosystems in general andin the Baltic and North Sea environment in particular.• the contaminant programme in marine biota constitute an integrated part of the nationalmonitoring activities in the marine environment as well as of the international programmeswithin ICES, OSPARCOM and HELCOM.The present report displays the timeseries of analysed contaminants in biota andsummarises the results from the statistical treatment. It does not in general give thebackground or explanations to significant changes found in the timeseries. Increasingconcentrations thus, urge for intensified studies.Short comments are given for temporal trends as well as for spatial variation and, for somecontaminants, differences in geometric mean concentration between various species caughtat the same site. Sometimes notes of seasonal variation and differences in concentrationbetween tissues in the same species are given. This information could say something aboutthe relative appropriateness of the sampled matrix and be of help in designing monitoringprogrammes. In the temporal trend part, an extract of the relevant findings is summarised inthe 'conclusion'-paragraph. It should be stressed though, that geographical differences maynot reflect antropogenic influence but may be due to factors like productivity, temperature,salinity etc.The report is continuously updated. The date of the latest update is reported at thebeginning of each chapter. The creation date of each figure is written in the lower leftcorner.
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2.
  • Bignert, Anders, et al. (författare)
  • Comments Concerning the National Swedish Contaminant Monitoring Programme in Marine Biota, 2006
  • 2006
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • This report gives a summary of the monitoring activities within the national Swedishcontaminant programme in marine biota. It is the result from the joint efforts of: theInstitute of Applied Environmental Research at Stockholm University (analyses oforganochlorines), the Centre for Environmental Monitoring at the University of Agriculture(analyses of heavy metals) and the Contaminant Research Group at the Swedish Museumof Natural History (co-ordination, sample collection administration, sample preparation,recording of biological variables, minor additional analyses of organochlorines, storage offrozen biological tissues in the Environmental Specimen Bank for retrospective studies,data preparation and statistical evaluation). The monitoring programme is financiated by theEnvironmental Protection Agency (EPA) in Sweden.The data of concern in this report represent the bioavailable part of the investigatedcontaminants i.e. the part that has virtually passed through the biological membranes andmay cause biological effects. The objectives of the monitoring program in marine biotacould be summarised as follows:• to estimate the levels and the normal variation of various contaminants in marine biotafrom several representative sites, uninfluenced by local sources, along the Swedish coasts.The goal is to describe the general contaminant status and to supply reference values forregional and local monitoring programmes• to monitor long term time trends and to estimate the rate of found changes.quantified objective: to detect an annual change of 10% within a time period of 10 years with a power of 80%at a significance level of 5%.• to estimate the response in marine biota of measures taken to reduce the discharges ofvarious contaminantsquantified objective: to detect a 50% decrease within a time period of 10 years with a power of 80% at asignificance level of 5%.• to detect incidents of regional influence or widespread incidents of ‘Chernobyl’-character and to act as watchdog monitoring to detect renewed usage of bannedcontaminants.quantified objective: to detect an increase of 200% a single year with a power of 80% at a significance level of5%.• to indicate large scale spatial differencesquantified objective: to detect differences of a factor 2 between sites with a power of 80% at a significancelevel of 5%.• to explore the development and regional differences of the composition and pattern ofe.g. PCB’s, HCH’s and DDT’s as well as the ratios between various contaminants.• the time series are also relevant for human consumption since important commercial fishspecies like herring and cod are sampled. A co-operation with the Swedish FoodAdministration is established. Sampling is also co-ordinated with SSI (Swedish RadiationProtection Authority) for analysing radionuclides in fish and blue mussels (HELCOM,1992).• all analysed, and a large number of additional specimens, of the annually systematicallycollected material are stored frozen in the Environmental Specimen Bank.. This invaluable5material enables future retrospective studies of contaminants impossible to analyse today aswell as control analyses of suspected analytical errors.• although the programme is focused on contaminant concentration in biota, also thedevelopment of biological variables like e.g. condition factor (CF), liver somatic index(LSI) and fat content are monitored at all sites. At a few sites, integrated monitoring withfish physiology and population are running in co-operation with the University ofGothenburg and the Swedish Fishery Board.• experiences from the national program with several time series of over 25 years can beused in the design of regional and local monitoring programmes.• the perfectly unique material of high qualityand long time series is further used to explorerelationships among biological variables and contaminants concentrations in varioustissues; the effects of changes in sampling strategy, the estimates of variance componentsand the influence on the concept of power etc.• the accessibility of high quality data collected and analysed in a consistent manner is anindispensable prerequisite to evaluate the validity of hypothesis and models concerning thefate and distribution of various contaminants. It could furthermore be used as input of ‘real’data in the ongoing model building activities concerning marine ecosystems in general andin the Baltic and North Sea environment in particular.• the contaminant programme in marine biota constitute an integrated part of the nationalmonitoring activities in the marine environment as well as of the international programmeswithin ICES, OSPARCOM and HELCOM.The present report displays the timeseries of analysed contaminants in biota andsummarises the results from the statistical treatment. It does not in general give thebackground or explanations to significant changes found in the timeseries. Increasingconcentrations thus, urge for intensified studies.Short comments are given for temporal trends as well as for spatial variation and, for somecontaminants, differences in geometric mean concentration between various species caughtat the same site. Sometimes notes of seasonal variation and differences in concentrationbetween tissues in the same species are given. This information could say something aboutthe relative appropriateness of the sampled matrix and be of help in designing monitoringprogrammes. In the temporal trend part, an extract of the relevant findings is summarised inthe 'conclusion'-paragraph. It should be stressed though, that geographical differences maynot reflect antropogenic influence but may be due to factors like productivity, temperature,salinity etc.The report is continuously updated. The date of the latest update is reported at the beginningof each chapter. The creation date of each figure is written in the lower left corner.
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3.
  • Bignert, Anders, et al. (författare)
  • Comments Concerning the National Swedish Contaminant Monitoring Programme in Marine Biota, 2008
  • 2008
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • This report gives a summary of the monitoring activities within the national Swedish contaminant programme in marine biota. It is the result from the joint efforts of: the Department of Applied Environmental Science at Stockholm University (analyses of organochlorines), the Department of Environmental Assessment at Swedish University of Agricultural Sciences (analyses of heavy metals), Department of Chemistry at Umeå University (analyses of PCDD/PCDF) and the Department of Contaminant Research at the Swedish Museum of Natural History (co-ordination, sample collection administration, sample preparation, recording of biological variables, storage of frozen biological tissues in the Environmental Specimen Bank for retrospective studies, data preparation and statistical evaluation). The monitoring programme is financiated by the Environmental Protection Agency (EPA) in Sweden.The data of concern in this report represent the bioavailable part of the investigated contaminants i.e. the part that has virtually passed through the biological membranes and may cause toxic effects. The objectives of the monitoring program in marine biota could be summarised as follows:• to estimate the levels and the normal variation of various contaminants in marine biota from several representative sites, uninfluenced by local sources, along the Swedish coasts. The goal is to describe the general contaminant load and to supply reference values for regional and local monitoring programmes• to monitor long term time trends and to estimate the rate of found changes.quantified objective: to detect an annual change of 10% within a time period of 10 years with a power of 80% at a significance level of 5%.• to estimate the response in marine biota of measures taken to reduce the discharges of various contaminantsquantified objective: to detect a 50% decrease within a time period of 10 years with a power of 80% at a significance level of 5%.• to detect incidents of regional influence or widespread incidents of ‘Chernobyl’- character and to act as watchdog monitoring to detect renewed usage of banned contaminants.quantified objective: to detect an increase of 200% a single year with a power of 80% at a significance level of 5%.• to indicate large scale spatial differencesquantified objective: to detect differences of a factor 2 between sites with a power of 80% at a significance level of 5%.• to explore the development and regional differences of the composition and pattern of e.g. PCB’s, HCH’s and DDT’s as well as the ratios between various contaminants.• the time series are also relevant for human consumption since important commercial fish species like herring and cod are sampled. A co-operation with the Swedish Food Administration is established. Sampling is also co-ordinated with SSI (Swedish Radiation Protection Authority) for analysing radionuclides in fish and blue mussels (HELCOM, 1992).• all analysed, and a large number of additional specimens, of the annually systematically collected material are stored frozen in the Environmental Specimen Bank.. This invaluable4material enables future retrospective studies of contaminants impossible to analyse today as well as control analyses of suspected analytical errors.• although the programme is focused on contaminant concentration in biota, also the development of biological variables like e.g. condition factor (CF), liver somatic index (LSI) and fat content are monitored at all sites. At a few sites, integrated monitoring with fish physiology and population are running in co-operation with the University of Gothenburg and the Swedish Board of Fisheries.• experiences from the national programme with several time series of over 25 years can be used in the design of regional and local monitoring programmes.• the perfectly unique material of high quality and long time series is further used to explore relationships among biological variables and contaminant concentrations in various tissues; the effects of changes in sampling strategy, the estimates of variance components and the influence on the concept of power etc.• the accessibility of high quality data collected and analysed in a consistent manner is an indispensable prerequisite to evaluate the validity of hypothesis and models concerning the fate and distribution of various contaminants. It could furthermore be used as input of ‘real’ data in the ongoing model building activities concerning marine ecosystems in general and in the Baltic and North Sea environment in particular.• the contaminant programme in marine biota constitute an integrated part of the national monitoring activities in the marine environment as well as of the international programmes within ICES, OSPARCOM and HELCOM.The present report displays the timeseries of analysed contaminants in biota and summarises the results from the statistical treatment. It does not in general give the background or explanations to significant changes found in the timeseries. Increasing concentrations thus, urge for intensified studies.Short comments are given for temporal trends as well as for spatial variation and, for some contaminants, differences in geometric mean concentration between various species caught at the same site. Sometimes notes of seasonal variation and differences in concentration between tissues in the same species are given. This information could say something about the relative appropriateness of the sampled matrix and be of help in designing monitoring programmes. In the temporal trend part, an extract of the relevant findings is summarised in the 'conclusion'-paragraph. It should be stressed though, that geographical differences may not reflect antropogenic influence but may be due to factors like productivity, temperature, salinity etc.The report is continuously updated. The date of the latest update is reported at the beginning of each chapter. The creation date of each figure is written in the lower left corner.
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4.
  • Bignert, Anders, et al. (författare)
  • Miljögifter och metaller i biologiskt material från marin miljö
  • 2004
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • A short summary of the results up to year 2002/03 is given below. Graphical presentations,tables and details are given in the following chapters. A summary of the estimatedconcentrations up to 2002/03 is given in table 23.3.•The condition of herring in the Baltic is decreasing in almost all autumn time series. Atthe same time fat content is decreasing in herring from Harufjärden, Landsort andUtlängan (autumn and spring).•Lead concentrations in herring, cod and perch livers are decreasing in almost all timeseries from both the Swedish west coast and the Baltic.•The increasing trends of cadmium concentrations in herring liver from the Baltic Properand from the Bothnian Sea reported for the period 1980 to 1997 seems to havestopped.In herring from Ängskärsklubb a significant decrease can be seen for the last ten years,and in the time series from Landsort there is also indications of this decrease.•Cadmium concentrations in blue mussels from the Baltic Proper are about 5 timeshigherthan the suggested background levels for the North Sea and 3 times higher thanthe mussel samples from Fladen and Väderöarna.•HCH’s are decreasing at almost all sites with a time serie long enough to permit astatistical trend analysis.•HCB is decreasing in herring, cod and guillemot from the Baltic Proper and also inherring and cod at the Swedish westcoast. However, some relativelyhighconcentrationshave been detected in the last years, and it looks like the decrease islevelling out.•TCDD-equivalents have not decreased in herring at Harufjärden, Karlskrona andFladen during the investigated timeperiod 1990-1999. There is a significant decrease ofthese substances in guillemot eggs from St Karlsö between 1970 and the middle of the80-ies after that, the decrease has levelled out. 
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5.
  • Helander, Björn, 1946-, et al. (författare)
  • The Role of DDE, PCB, Coplanar PCB and Eggshell Parameters for Reproduction in the White-tailed Sea Eagle (Haliaeetus albicilla) in Sweden.
  • 2002
  • Ingår i: Ambio. - 0044-7447 .- 1654-7209. ; 31:5, s. 386-403
  • Tidskriftsartikel (refereegranskat)abstract
    • The reproduction of white-tailed sea eagles was monitoredin1964–1999 in 3 differently contaminated sub-populations: BalticSea coast (Bp), inland central Sweden (Ip) and Lapland (Lp). 249dead eggs from 205 clutches were obtained for analyses of DDEand PCBs and for eggshell measurements. A desiccation index(Di) value was calculated for each egg as a measure of waterloss through the shell. In the highly contaminated Bp, p,p´-DDEconcentrations in the eggs decreased continuously and 5-foldduring the study period and PCB concentrations decreased 3-fold from the mid 1980s. The PCB pattern changed slightly overtime towards more high-chlorinated congeners but the relativetoxicity of the PCB mixture, expressed as 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents (TEQ), remained constant and TEQcan be assumed to have decreased in a similar way as PCB overtime. Productivity (P), shell thickness (St), shell index (Si) and Diincreased over time in the Bp but no change in Di or productivityoccurred in the Lp, where residue concentrations were 5–8 timeslower. P of the Bp was not correlated to St or Si but was negatively correlated to Di, DDE and PCB. An S-shaped doseresponse relationship was indicated between P and DDE. After1988, when the PCB/DDE ratio was considerably higher thanpreviously, PCB but not DDE concentrations were significantlyhigher in eggs with dead embryos as compared to undevelopedeggs, implying lethal concentrations of PCB, and a LOEL of 320pg g–1 TEQ is suggested for embryo mortality. In a subset of 21eggs, representing productive and unproductive females, analyzed for a selection of coplanar PCB congeners, tris(4-chlorophenyl) methanol and bis(4-chlorophenyl) sulphone, there wasno evidence for a correlation between P and any of these compounds. A reduction in residue concentrations in old females didnot lead to increased P or improved Di-values, indicating aremaining effect from a previous, higher exposure to contaminants. The inability to reproduce included a high rate ofundeveloped eggs, indicating effects at a prezygotic stage. Pshowed the strongest correlation with Di, and Di was moststrongly correlated to DDE. Thus, the remaining effect of previousexposure resulted in a stronger correlation to the symptom (Di)rather than to the suggested causative agent (DDE). LOEL valuesfor depressed P were estimated at 120 µg g–1 DDE and 500 µgg–1 PCB (lipid basis). It is concluded that the major reason fordepressed P during the study period was DDE, but that effectsalso from PCB were largely concealed by the effects from DDE.
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6.
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7.
  • Asplund, Anders, 1974- (författare)
  • How a continuously changing B2B environment influences the selection of suppliers : introducing a model and process approach
  • 2004
  • Licentiatavhandling (övrigt vetenskapligt/konstnärligt)abstract
    • Creation of a supply base is perhaps the most important task of the purchasing function. In this creation process, potential suppliers must be identified, analysed and decisions made. Decisions that, in most cases, have direct effects on the company's "bottom line". The tools to support and aid this process are often one-dimensional and assume to a high degree that, in all cases, there is a valid description of the best possible supplier. This research suggests that this is not the case. Which is the best possible supplier is situation specific. This is a fact acknowledged in the literature and by the empirical material. What is missing is a tool to support the supplier selection process from a starting point that each sourcing situation is unique. This research proposes such a process approach and, at the same time, a model for supplier selection.The purpose of this study is to analyse and develop the process of, and the criteria for, supplier selection in a sub-tier, business to business context. The research has been initiated by, and had its starting point in, one company (Volvo Aero Corporation) acting in the specific and very demanding environment of the aero-engine industry. The main aim of this research is to give managerial implications for purchasing professionals.To be able to ensure that the best possible supplier for a specific situation is selected, the situation has to be analysed. This research proposes a model and process that starts by defining the minimum requirement which a supplier has to fulfil for a purchaser to be convinced that the intended relationship will be successful for the intended period of time. This minimum requirement is called the supplier profile. The business environment, network and market conditions, the.purchasing company 's strategies and the characteristics of the product, service or function to be sourced are identified as influential factors when creating the supplier profile. The results also highlight the need to work cross-functionally when creating the supplier profile and the need to combine different theoretical bases to get a complete picture of the requirements to put on a potential supplier.
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8.
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9.
  • Asplund, Erik, et al. (författare)
  • Framsyn för Norrbotten och Västerbotten : en idéskrift om utvecklingsinsatser idag och imorgon
  • 2009
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • Rapport från DARE delprojekt regional framsyn. Etapp 1; scenarier och förslag på aktiviteter.Detta dokument är slutrapporten från den regionala framsynsprocessen som drevs 2008-2009 inom projektet DARE – Development Arena for Research and Entrepreneurship.Framsynen har verkat efter ett normativt och handlingsinriktat angreppssätt. Ledmotiv för processen har varit frågor som: Hur vill vi ha det? Varför är det inte så nu? Vad behöver vi göra nu och i framtiden? Regionen kan sägas kännetecknas av att den är rik på naturresurser och fattig på folk. Det är bakgrunden till de fokusområden som framsynen behandlat- Grönare näringsliv (hur kan nya och miljöeffektivare produkter och tjänsterutvecklas effektivare?)- Demografiutveckling (hur kan samhällsfunktionerna bestå med inverteradebefolkningspyramider och hur kan utvecklingen mot en åldrande befolkningvändas?)Lite tvärs över båda frågorna ovan hamnar ett annat fokus; regionens attraktivitet. Inom detta område har en ung framsyn genomförts med deltagare från olika delar av Norrbotten.Framsynen har gått steg för steg genom visioner, analys av framgångsfaktorer, scenarieskapande, förslag på åtgärder och prioritering av dessa. Under genomförandet har det uppstått ett antal avknoppningar i form av t ex nya samarbeten och projekt. Ett av de sistnämnda var den unga framsynen som genomfördes med finansiering av Norrbottens läns landsting.Bland de prioriterade förslagen som redovisas i denna rapport dominerar olika aktiviteter för att knyta samman olika aktörer och grupper inom regionen och på så sätt göra mer av mindre. Många av förslagen visar regionala aktörers förväntningar på universitetens roll i den regionala utvecklingen och markerar ett intresse av tätare samverkan meduniversiteten. Förslagen berör alla verksamheter inom universiteten, såväl utbildning, forskning och förvaltning. Bland de prioriterade förslagen finns:• Stimulera gröna affärs och teknikutvecklingsallianser för regionens småföretag• Stimulera ”den lille forskaren” – en modell för småföretagens forskarkollektiv• Utred grönare näringsliv som gemensamt profilområde för regionens universitet• Stärk företagsnyttig forskning & utvecklingsinsatser kring ”age management”• Etablera ett ”integrationsnätverk” för universitetens studenter & det regionalasamhället• Utveckla dialogen mellan universiteten & avnämargrupper i utvecklingen avutbildningar • Skapa regionalt utvecklingslab för bättre samverkan mellan universiteten ochomgivande samhälleInom DARE-projektet kommer nu det material som utvecklats inom framsynsprocessen att användas för utveckling av samverkan inom universiteten, mellan universiteten och med andra intressenter av den regionala utvecklingen, inte minst då de som deltagit i framsynen.
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10.
  • Asplund, Gunilla, et al. (författare)
  • Soil Peroxidase-Mediated Chlorination of Fulvic Acid
  • 1991
  • Ingår i: Humic substances in the aquatic and terrestrial environment : proceedings of an international symposium, Linköping, Sweden, August 21-23, 1989. - Berlin Heidelberg New York : Springer. - 3540537023 ; , s. 474-483
  • Bokkapitel (refereegranskat)abstract
    • Humic matter has recently been shown to contain considerable quantities of naturally produced organohalogens. The present study investigated the possibility of a non-specific, enzymatically mediated halogenation of organic matter in soil. The results showed that, in the presence of chloride and hydrogen peroxide, the enzyme chloroperox1dase (CPO) from the fungus Caldariomyces fumago catalyzes chlorination of fulvic acid. At pH 2.5 - 6.0, the chlorine to fulvic acid ratio in the tested sample was elevated from 12 mg/g to approximately 40-50 mg/g. It was also shown that this reaction can take place at chloride and hydrogen peroxide concentrations found in the environment. An extract from spruce forest soil was shown to have a measurable chlorinating capacity. The activity of an extract of 0.5 kg soil corresponded to approximately 0.3 enzyme units, measured as CPO activity. Enzymatically mediated halogenation of humic substances may be one of the mechanisms explaining the w1despread occurrence of adsorbable organic halogens (AOX) in soil and water.
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