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Results:

• 11. Funded MS student opportunity. Dust and ash re-suspension sources

  Formulating source term for dust and ash re-suspension for the NAME model. The MS student will work on the implementation of an emission scheme particularly apt for Icelandic land coverage and climate, and to validate the code using a past event. The MS student will:Formulate code; working on selected test cases.Do backward numerical runs for quantifying the temporal changes of areal source /about-imo/news/funded-ms-student-opportunity-dust-and-ash-re-suspension-sources-in-emission-models

• 12. Terms and conditions

  no authorisation is given to change data or any other information available from this web-site, unless the source and modification is stated clearly. (i.e., a description of data sourced from IMO and the subsequent changes made by others.) The Icelandic Met Office's website does not collect personally identifiable data about users. Web traffic on en.vedur.is is measured by Google Analytics, Siteimprove /about-imo/the-web/conditions/

• 13. The final CES conference, 31 May-2 June 2010

  to exchange views and acquire information about current research of climate changes and energy issues. Altogether 31 oral presentations and 21 posters were presented at the conference, including 5 keynote presentations given by invited speakers from leading research institutes on climate and energy issues. The extended abstract volume of the presentations in PDF-form is available for download /ces/nr/1979

• 14. Eriksson_1-Risk-perception

  Biosperic Altruistic Egoistic Ecological worldview (NEP) Adverse consequen- ces for valued objects (AC) Perceived responsibility to reduce threat (AR) Sense of obligation to take pro- environmental actions Activism Non-activst public-spere behaviours Private- sphere behaviours Behaviours in organizations Stern et al., (1999); Stern (2000) (2) Theory of planned behavior (TPB) Ajzen /media/loftslag/Eriksson_1-Risk-perception.pdf

• 15. Refsgaard_etal-2007-Uncertainty-EMS

  The advantage of Monte Carlo analysis is its general appli- cability and that it does not impose many assumptions on prob- ability distributions and correlations and that it can be linked to any model code. The key limitation is the large run times for computationally intensive models and the huge amount of outputs that are not always straightforward to analyse. 4.8. Multiple model simulation Multiple model /media/loftslag/Refsgaard_etal-2007-Uncertainty-EMS.pdf

• 16. VI_2016_006_rs

  of 100–140 m a.s.l. Several debris flows are recorded in Búðará since the beginning of the 20th century. It is not clear whether the upper or lower area is the main source for these debris flows. The return time for sizeable debris flows in Búðará is around 20 years. It appears that the land- slide activity has been more frequent in the last 30 years than earlier in the 20th century. 4.5 Areas 7 /media/vedurstofan-utgafa-2016/VI_2016_006_rs.pdf

• 17. Group5-Stakeholders_involvement

  Horsens case / Stakeholders involvement draft report Patience, Yuan, Emmanuel Horsens case / Stakeholders involvement • Overall objective Facilitate adaptation of horsens municipality to climate change • Purpose Negociated catalogue of coping measures adopted at the end of the participatory process • Stakeholders • Participation stages • Milestones 26 August 2011 PM/YZ /media/loftslag/Group5-Stakeholders_involvement.pdf

• 18. Gas concentrations in the Hofsjökull ice cave

  those already reported. Oxygen was measured at normal levels, so there is no evidence of carbon dioxide (CO2) accumulation, but this was not measured on these devices. Sulfur dioxide (SO2) was not detected in the cave.An addition hazard is the potential for roof collapse. During another visit in the past week, an ice block sized 2*4*0.4 m was seen to have collapsed from a side wall near /about-imo/news/gas-concentrations-in-the-hofsjokull-ice-cave

• 19. Eriksson_Garvill_Nordlund_2006

  and infringement on freedom, and indirectly associated with the acceptability of road pricing. In addition, relations between beliefs about effectiveness and acceptability of TDM measures have been shown. More specifically, the more effective a measure is perceived to be, the more acceptable it is (e.g. Bamberg & Ro¨lle, 2003; Nordlund & Garvill, 2006; Rienstra et al., 1999). For coercive measures /media/loftslag/Eriksson_Garvill_Nordlund_2006.pdf

• 20. Eriksson_2-Acceptability-of-policy

  (Stern, 2002) 4 5 (1) Concepts • Acceptability - attitude toward policy (e.g., Schade, 2003). Salient beliefs attitudes (Eagly & Chaiken, 1993). • Acceptability (before implementation) versus acceptance (after implementation) (Gärling et al. 2008) • Attitude (acceptability/acceptance) versus behaviour (Eagly & Chaiken, 1993) (2) Factors important for acceptability • Acceptability /media/loftslag/Eriksson_2-Acceptability-of-policy.pdf