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Sökning: WFRF:(Wilander Anders)

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1.
  • Persson, Gunnar, et al. (författare)
  • 1 b, urval och representativitet
  • 2009
  • Ingår i: Rapport / Naturvårdsverket. - 0282-7298. ; , s. 105-116
  • Annan publikation (övrigt vetenskapligt/konstnärligt)
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2.
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3.
  • 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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4.
  • 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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5.
  • 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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6.
  • 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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7.
  • Aneman, Anders, et al. (författare)
  • Vasopressor Responsiveness Beyond Arterial Pressure : A Conceptual Systematic Review Using Venous Return Physiology
  • 2021
  • Ingår i: Shock. - : Lippincott Williams & Wilkins. - 1073-2322 .- 1540-0514. ; 56:3, s. 352-359
  • Forskningsöversikt (refereegranskat)abstract
    • We performed a systematic review to investigate the effects of vasopressor-induced hemodynamic changes in adults with shock. We applied a physiological approach using the interacting domains of intravascular volume, heart pump performance, and vascular resistance to structure the interpretation of responses to vasopressors. We hypothesized that incorporating changes in determinants of cardiac output and vascular resistance better reflect the vasopressor responsiveness beyond mean arterial pressure alone. We identified 28 studies including 678 subjects in Pubmed, EMBASE, and CENTRAL databases. All studies demonstrated significant increases in mean arterial pressure (MAP) and systemic vascular resistance during vasopressor infusion. The calculated mean systemic filling pressure analogue increased (16 +/- 3.3 mmHg to 18 +/- 3.4 mmHg; P = 0.02) by vasopressors with variable effects on central venous pressure and the pump efficiency of the heart leading to heterogenous changes in cardiac output. Changes in the pressure gradient for venous return and cardiac output, scaled by the change in MAP, were positively correlated (r (2) = 0.88, P < 0.001). Changes in the mean systemic filling pressure analogue and heart pump efficiency were negatively correlated (r (2) = 0.57, P < 0.001) while no correlation was found between changes in MAP and heart pump efficiency. We conclude that hemodynamic changes induced by vasopressor therapy are inadequately represented by the change in MAP alone despite its common use as a clinical endpoint. The more comprehensive analysis applied in this review illustrates how vasopressor administration may be optimized.
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8.
  • Eriksson, Barbro, et al. (författare)
  • Neuroendocrine pancreatic tumours : clinical presentation, biochemical and histopathological findings in 84 patients
  • 1990
  • Ingår i: Journal of Internal Medicine. - : Wiley. - 0954-6820 .- 1365-2796. ; 228:2, s. 103-113
  • Tidskriftsartikel (refereegranskat)abstract
    • A prospective study has been performed on 84 patients with endocrine pancreatic tumours evaluated at the Medical Department in Uppsala. Available information concerning the patients' presenting symptoms, age at diagnosis, clinical syndrome, tumour location, location of metastases, diagnostic radiology, biochemical and histopathological findings has been analysed. Our results indicate that most patients initially show rather vague and non-specific symptoms, with dyspepsia and pain being the most frequent presenting features. The median delay between appearance of the first symptom and diagnosis was 2 years; the delay was 3 5 months in sporadic cases and 14.5 months in familial cases. In spite of improvements in diagnostic methods, the median age at diagnosis (53 years) has not been reduced, and most patients are encountered when the tumour has reached an advanced stage. There is a need for a method of screening patients with still uncharacteristic abdominalsymptoms for a neuroendocrine tumour. The presence of elevated levels of plasma chromogranin in all patients with a proven tumour suggests that such possibilities exist, and the use of this biochemical marker in the future might reduce the age at diagnosis and thus improve the likelihood of cure and survival of patients with endocrine pancreatic tumours.
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9.
  • Fölster, Jens, et al. (författare)
  • A Novel Environmental Quality Criterion for Acidification in Swedish Lakes - An Application of Studies on the Relationship Between Biota and Water Chemistry
  • 2007
  • Ingår i: Acid Rain - Deposition to Recovery. - Netherlands : Springer. - 9781402058844 ; , s. 331-338
  • Bokkapitel (övrigt vetenskapligt/konstnärligt)abstract
    • The recovery from acidification has led to the demand for more precise criteria for classification of acidification. The Swedish Environmental Protection Agency has revised Sweden's Ecological Quality Criteria for acidification to improve the correlation between the chemical acidification criteria and biological effects. This paper summarises the most relevant findings from several of the studies commissioned for this revision. The studies included data on water chemistry in 74 reference lakes in southern Sweden with data on fish in 61 of the lakes, as well as data on littoral fauna in 48 lakes. We found that the acidity variable most strongly correlated to the biota was the median pH from the current year. Our results probably do not reflect the mechanisms behind the negative effects of acidity on the biota, but are fully relevant for evaluation of monitoring data. The biogeochemical models used for predicting acidification reference conditions generate a pre-industrial buffering capacity. In order to get an ecologically more relevant criteria for acidification based on pH, we transferred the estimated change in buffering capacity into a corresponding change in pH. A change of 0.4 units was defined as the threshold for acidification. With this criterion a considerably lower number of Swedish lakes were classified as acidified when compared with the present Ecological Quality Criteria.
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10.
  • Fölster, Jens, et al. (författare)
  • A Novel Environmental Quality Criterion for Acidification in Swedish Lakes – An Application of Studies on the Relationship Between Biota and Water Chemistry
  • 2007
  • Ingår i: Water, Air, & Soil Pollution: Focus. - : Springer Science and Business Media LLC. - 1567-7230 .- 1573-2940. ; 7:1-3, s. 331-338
  • Tidskriftsartikel (refereegranskat)abstract
    • The recovery from acidification has led to the demand for more precise criteria for classification of acidification. The Swedish Environmental Protection Agency has revised Sweden’s Ecological Quality Criteria for acidification to improve the correlation between the chemical acidification criteria and biological effects. This paper summarises the most relevant findings from several of the studies commissioned for this revision. The studies included data on water chemistry in 74 reference lakes in southern Sweden with data on fish in 61 of the lakes, as well as data on littoral fauna in 48 lakes. We found that the acidity variable most strongly correlated to the biota was the median pH from the current year. Our results probably do not reflect the mechanisms behind the negative effects of acidity on the biota, but are fully relevant for evaluation of monitoring data. The biogeochemical models used for predicting acidification reference conditions generate a pre-industrial buffering capacity. In order to get an ecologically more relevant criteria for acidification based on pH, we transferred the estimated change in buffering capacity into a corresponding change in pH. A change of 0.4 units was defined as the threshold for acidification. With this criterion a considerably lower number of Swedish lakes were classified as acidified when compared with the present Ecological Quality Criteria.
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