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Sökning: WFRF:(Bignert Anders) > (2005-2009)

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1.
  • 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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2.
  • 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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3.
  • Glynn, Anders, et al. (författare)
  • Declining levels of PCB, HCB and p,p'-DDE in adipose tissue from food producing bovines and swine in Sweden 1991-2004
  • 2009
  • Ingår i: Chemosphere. - : Elsevier BV. - 0045-6535 .- 1879-1298. ; 74:11, s. 1457-1462
  • Tidskriftsartikel (refereegranskat)abstract
    • The official control programme for organochlorine (OC) contaminants in food producing animals in Sweden was used to study temporal and spatial trends of the polychlorinated biphenyl CB 153, hexachlorobenzene (HCB) and p,p'-DDE in adipose tissue from bovines and swine 1991-2004. Our results show that efforts to decrease OC contamination of animal feed and the environment have had a positive impact on the contamination of the animal production. OC concentrations declined significantly in almost all studied regions of Sweden. OC temporal trends were slower in bovines (6-8% per year) than in swine (10-12%). Power analyses showed that data from more than 10 years of sampling were needed for a detection of an annual OC level change of 5% in both species in the control programme, due to large within- and between-year variation in OC levels. CB 153 and p,p'-DDE levels were higher in southern than in northern Sweden. Levels decreased with age in milk cows, but not in young nulliparous cows (heifers) and bulls. Moreover, milk cows and bulls had significantly lower OC levels than heifers. Levels were not age-dependent among swine, but castrated male swine (barrows) had significantly lower OC levels than young female swine (gilts). Levels of the studied OCs are now in many cases below the LOQ of the analytical method used. Future time trend studies of these OCs thus depend on lowered LOQs in the control programme.
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6.
  • Bignert, Anders, et al. (författare)
  • Metals and Organic Contaminants in Starling (Sturnus vulgaris) from central and southern Sweden
  • 2008
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • The present study has been carried out on mandate of and in cooperation with the Swedish Environmental Protection Agency (SEPA) according to Agreement 222 0744. By use of liver and muscle of starling as a matrix representing parts of the terrestrial environment, the study will focus on accumulation, profiles and concentrations of some pesticides used in semi-agricultural areas of Sweden as well as the accumulated levels of some metals and ground elements. Flame retardants are materials added or applied to a product to increase its fire resistance. This study focuses on accumulated levels of PBDEs and HBCD. Five phenolic substances were analysed in muscle of starling; 4-tert-octylphenol (OP), nonylphenol, triclosan, bisphenol A and pentachlorphenol (PCP). Finally we screened the great group of perfluorinated compounds (PFCs).
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7.
  • Bignert, Anders (författare)
  • Some consequences using pooled samples versus individual samples and pooled samples with various relation between sampling error and uncertainty due to chemical analysis
  • 2008
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • Choosing an appropriate sampling strategy for environmental monitoring or storingsamples in Environmental Specimen Banks for future analyses includes the importantdecision of using individual or pooled samples. A number of advantages usingindividual samples for temporal trend studies can be identified e.g. that informationabout sample variance is important in it self and changes in variance is often the firstsign of a change in contaminant burden, freedom of choosing an appropriate centralmeasure (for right skewed distributions i.e. geometric mean values or medians)whereas pooled samples will represent arithmetic means. Furthermore, individualsampling enables adjustments for confounding factors (e.g. fat content, age, size) anddetection of extreme values. However, resources may be saved by using pooledsamples, if the sample variance is dominated by small-scale differences in time orspace or by genetic and/or physiological differences among individual biologicalsamples rather than of instrumental errors at the chemical analyses. The statisticalpower at temporal or spatial studies is determined by the random/unexplained samplevariation. The relation between the instrumental error and other sources of variation aswell as the relation between the cost for chemical analysis and collection andpreparation of samples will determine the number of individual samples in each pooland the number of pools that should be analysed to achieve high cost efficiency.Various scenarios of different number of individual samples, different number ofpooled samples containing various number of individual specimens, different relationbetween instrumental error and other sources of sample variance have been comparedby simulating random sampling from computer generated populations using realisticmeasures of variation from ongoing monitoring activities. The results may giveguidance to the selection of a cost efficient sampling strategy
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8.
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9.
  • Bignert, Anders, et al. (författare)
  • Spatial variation in concentrations and patterns of the PCDD/F and dioxin-like-PCB content in herring from the northern Baltic Sea
  • 2007
  • Ingår i: Journal of Environmental Monitoring. - Cambridge : Royal Society of Chemistry. - 1464-0325 .- 1464-0333. ; 9:6, s. 550-556
  • Tidskriftsartikel (refereegranskat)abstract
    • The purpose of the current study was to investigate spatial and seasonal variation of dioxin and dioxin-like PCB (dl-PCB) content in herring sampled along the northern Baltic Sea coast and map out risk zones for dioxins and dl-PCBs. We further aimed to investigate relationships between congener distribution (pattern) and sampling location and season. The results showed that there were distinct geographical differences in concentrations of dioxins, dibenzofurans and dl-PCBs along the Swedish coast, from the Bothnian Bay to north Baltic Proper, with the highest levels detected in the southern Bothnian Sea. The majority of the locations showed concentrations above the prescribed maximum for dioxin residues (4 TEQ pg g–1 wet weight [w.w.]). If all the edible parts of the fish (muscle, subcutaneous fat and skin) are considered, the estimated concentrations exceeded the prescribed maximum level in the whole study area for herring collected during spring–summer. Concentrations in herring caught during spring–summer compared to concentrations in herring sampled in the autumn indicated seasonal variation. The pattern analysis showed a variation in relative congener concentration at the different sampling locations (spring–summer). Pattern differences were also noticed between seasons.
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10.
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