Short-term carbon input increases microbial nitrogen demand, but not microbial nitrogen mining, in a set of boreal forest soils

Wild B.; Alaei S.; Bengtson P.; Bodé S.; Boeckx P.; Schnecker J.; Mayerhofer W.; Rütting T.
2017 | Biogeochemistry | 136 (261-278)

Mass transfer of an organophosphate flame retardant between product source and dust in direct contact

Liagkouridis, I.; Lazarov, B., Giovanoulis, G.; Cousins, I.T.
2017 | Emerging Contaminants | 3 (3) (115-120)

Transferring mixtures of chemicals from sediment to a toxicity test using silicone-based passive sampling and dosing

Mustajärvi, L.; Eriksson-Wiklund, A-K.; Gorokhova, E.; Jahnke, A.; Sobek, A.
2017 | Environ. Sci.: Processes Impacts | 19 (1404-1413)

In situ benthic flow-through chambers to determine sediment-to-water fluxes of legacy hydrophobic organic contaminants

Mustajärvi, L.; Eek, E.; Cornelissen, G.; Eriksson-Wiklund, A-K.; Undeman, E.; Sobek, A.
2017 | Environ. Pollut. | 231 (854-862)

Speciation and hydrological transport of metals in non-acidic river systems of the Lake Baikal basin: Field data and model predictions

Thorslund, Josefin; Jarsjö, Jerker; Wällstedt, Teresia; Mörth, Carl Magnus; Lychagin, Mikhail Yu.; Chalov, Sergey R.
2017 | Reg Environ Change | 17 (7) (2007-2021)

The speciation of metals in aqueous systems is central to understanding their mobility, bioavailability, toxicity and fate. Although several geochemical speciation models exist for metals, the equilibrium conditions assumed by many of them may not prevail in field-scale hydrological systems with flowing water. Furthermore, the dominant processes and/or process rates in non-acidic systems might differ from well-studied acidic systems. We here aim to increase knowledge on geochemical processes controlling speciation and transport of metals under non-acidic river conditions. Specifically, we evaluate the predictive capacity of a speciation model to novel measurements of multiple metals and their partitioning, under high-pH conditions in mining zones within the Lake Baikal basin. The mining zones are potential hotspots for increasing metal loads to downstream river systems. Metals released from such upstream regions may be transported all the way to Lake Baikal, where increasing metal contamination of sediments and biota has been reported. Our results show clear agreement between speciation predictions and field measurements of Fe, V, Pb and Zn, suggesting that the partitioning of these metals mainly was governed by equilibrium geochemistry under the studied conditions. Systematic over-predictions of dissolved Cr, Cu and Mo by the model were observed, which might be corrected by improving the adsorption database for hydroxyapatite because that mineral likely controls the solubility of these metals. Additionally, metal complexation by dissolved organic matter is a key parameter that needs continued monitoring in the Lake Baikal basin because dependable predictions could not be made without considering its variability. Finally, our investigation indicates that further model development is needed for accurate As speciation predictions under non-acidic conditions, which is crucial for improved health risk assessments on this contaminant.

Chlorinated Paraffins Leaking from Hand Blenders can lead to Significant Human Exposures.

Yuan, B.; Strid, A.; Darnerud, P.O.; de Wit, C.A.; Nyström, J.; Bergman, Å.
2017 | Environ Int | 109 (73-80)

Measurement of micronuclei and internal dose in mice demonstrates that 3-monochloropropane-1,2-diol (3-MCPD) has no genotoxic potency in vivo

J. Aasa; M. Törnqvist; L. Abramsson-Zetterberg
2017 | Food Chem. Toxicol. | 109 (414-420)

In this study 3-monochloropropane-1,2-diol (3-MCPD), a compound that appears as contaminant in refined cooking oils, has been studied with regard to genotoxicity in vivo (mice) with simultaneous measurement of internal dose using state-of-the-art methodologies. Genotoxicity (chromosomal aberrations) was measured by flow cytometry with dual lasers as the frequency of micronuclei in erythrocytes in peripheral blood from BalbC mice intraperitoneally exposed to 3-MCPD (0, 50, 75, 100, 125 mg/kg). The internal doses of 3-MCPD in the mice were calculated from N-(2,3-dihydroxypropyl)-valine adducts to hemoglobin (Hb), quantified at very low levels by high-resolution mass
spectrometry. Convincing evidence for absence of genotoxic potency in correlation to measured internal doses in the mice was demonstrated, despite relatively high administered doses of 3-MCPD. The results are discussed in relation to another food contaminant that is formed as ester in parallel to 3-MCPD esters in oil processing,
i.e. glycidol, which has been studied previously by us in a similar experimental setup. Glycidol has been shown to be genotoxic, and in addition to have ca. 1000 times higher rate of adduct formation compared to that observed for 3-MCPD. The conclusion is that at simultaneous exposure to 3-MCPD and glycidol the concern about genotoxicity would be glycidol.

Spatial Distributions of DDTs in the Water Masses of the Arctic Ocean

Carrizo, D.; Sobek, A.; Salvado, J.A.; Gustafsson, Ö.
2017 | Environ. Sci. Technol. | 51 (7913-7919)

Trends in black carbon and size-resolved particle number concentrations and vehicle emission factors under real-world conditions

Krecl, P.; Johansson, C.; Targino, A.C.; Ström, J.; Burman, L.
2017 | Atmos Environ | 165 (155-168)

Kerbside concentrations of NOx, black carbon (BC), total number of particles (diameter > 4 nm) and number size distribution (28–410 nm) were measured at a busy street canyon in Stockholm in 2006 and 2013. Over this period, there was an important change in the vehicle fleet due to a strong dieselisation process of light-duty vehicles and technological improvement of vehicle engines. This study assesses the impact of these changes on ambient concentrations and particle emission factors (EF). EF were calculated by using a novel approach which combines the NOx tracer method with positive matrix factorisation (PMF) applied to particle number size distributions. NOx concentrations remained rather constant between these two years, whereas a large decrease in particle concentrations was observed, being on average 60% for BC, 50% for total particle number, and 53% for particles in the range 28–100 nm. The PMF analysis yielded three factors that were identified as contributions from gasoline vehicles, diesel fleet, and urban background. This separation allowed the calculation of the average vehicle EF for each particle metric per fuel type. In general, gasoline EF were lower than diesel EF, and EF for 2013 were lower than the ones derived for 2006. The EFBC decreased 77% for both gasoline and diesel fleets, whereas the particle number EF reduction was higher for the gasoline (79%) than for the diesel (37%) fleet. Our EF are consistent with results from other on-road studies, which reinforces that the proposed methodology is suitable for EF determination and to assess the effectiveness of policies implemented to reduce vehicle exhaust emissions. However, our EF are much higher than EF simulated with traffic emission models (HBEFA and COPERT) that are based on dynamometer measurements, except for EFBC for diesel vehicles. This finding suggests that the EF from the two leading models in Europe should be revised for BC (gasoline vehicles) and particle number (all vehicles), since they are used to compile national inventories for the road transportation sector and also to assess their associated health effects. Using the calculated kerbside EF, we estimated that the traffic emissions were lower in 2013 compared to 2006 with a 61% reduction for BC (due to decreases in both gasoline and diesel emissions), and 34–45% for particle number (reduction only in gasoline emissions). Limitations of the application of these EF to other studies are also discussed.

Supporting variables for biological effects measurements in fish and blue mussel

Hansson, T.; Thain, J.; Martínez-Gómez, C.; Hylland, K.; Gubbins, M.; Balk, L.
2017 | ICES Techniques in Marine Environmental Sciences | 60 (1-22) | ISBN: 978-87-7482-200-4 | Report No: 60

Biological effects measurements in fish and blue mussel are fundamental in marine environmental monitoring. Nevertheless, currently used biomarkers may be confounded by basic physiological phenomena, such as growth, reproduction, and feeding, as well as thereby associated physiological variation. Here, we present a number of supporting variables, which are essential to measure in order to obtain reliable biological effects data, facilitate their interpretation, and make valid comparisons. For fish, these variables include: body weight, body length, condition, gonad maturation status, various somatic indices, age, and growth. For blue mussels, these variables include: volume, flesh weight, shell weight, and condition. Also, grossly visible anomalies, lesions, and parasites should be recorded for both fish and blue mussels. General confounding factors and their effects are described, as well as recommendations for how to handle them.

Validity of serum concentration in exposure assessment to environmental pollutants – a case study of perfluoroalkyl acids in Finnish children

Koponen, J.; Winkens, K.; Airaksinen, R.; Berger, U.; Vestergren, R.; Cousins, I.T.; Karvonen, A.M.; Pekkanen, J.; Kiviranta, H.
2017 | SU

37th International Symposium on Halogenated Persistent Organic Pollutants (POPs) - DIOXIN 2017. | August 21, 2017 | Vancouver, Canada

Vitaminbrist som dödar

2017 | Forskning & Framsteg | 2017 (7) (28-33)

Brist på vitaminet tiamin har orsakat massdöd bland sjöfåglarna. Svensk forskning visar att problemet är mer utbrett än så. Nu gäller det att förstå orsaken.

Contact information

Visiting addresses:

Geovetenskapens Hus,
Svante Arrhenius väg 8, Stockholm

Arrheniuslaboratoriet, Svante Arrhenius väg 16, Stockholm (Unit for Analytical and Toxicological Chemistry)

Mailing address:
Department of Environmental Science and Analytical Chemistry (ACES)
Stockholm University
106 91 Stockholm

Press enquiries should be directed to:

Annika Hallman
Science Communicator
Phone +46 (0)8 16 15 53
Mobile +46 (0)70 664 22 64
annika.hallman@aces.su.se