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CITI-SENSE Citizens' Observatory products and tools for air quality studies in cities.

Stojanovic, M.J. Liu, H.-Y.; Berre, A.; Fredriksen, M.F.; Kobernus, M.; Davidovic, M.; Topalovic, D.; CITI-SENSE consortium, Bartonova, A.

2016

CITI-SENSE Citizens' observatories toolbox - user's perspective.

Liu, H.-Y.; Berre, A.; Fredriksen, M.F.; Kobernus, M.J.; CITI-SENSE consortium, Bartonova, A.

2016

CITI-SENSE Citizens' observatories toolbox - developer's perspective.

Fredriksen, M.F.; Liu, H.-Y.; Berre, A.; CITI-SENSE consortium.

2016

CITI-SENSE Citizens' Observatories Architecture

Liu, Hai-Ying; Berre, Arne- Jørgen; Kobernus, Michael John; Fredriksen, Mirjam; Rombouts, Richard; Tamlin, Andrei; Cole-Hunter, Tom; Santiago, Leonardo; Bartonova, Alena

This paper introduces the architecture of the CITI-SENSE Citizens’ Observatories based on the ISO 19119 reference model. It describes the various parts of the architecture including boundary services with sensors and apps and data management services with the CITI-SENSE data model. It also describes the Web Feature Service (WFS) storage support and the reusable visualisation widgets used for both apps and web portals in various Citizens’ Observatories.

European Commission Joint Research Centre

2018

CITI-SENSE Citizen observatory for air quality - Collected data and reusable software and tools.

Bartonova, A.; Liu, H.-Y.; Fredriksen, M.; Berre, A.J.; Citi-Sense consortium.

2016

Circumpolar transport and air-surface exchange of atmospheric mercury at Ny-Ålesund (79° N), Svalbard, spring 2002.

Sommar, J.; Wängberg, I.; Berg, T.; Gårdfeldt, K.; Munthe, J.; Richter, A.; Urba, A.; Wittrock, F.; Schroeder, W.H.

2007

Circular Economy Resource Information System – CE-RISE

Bouman, Evert Alwin; Guerreiro, Cristina

2024

Circular economy for aquatic food systems: insights from a multiscale phosphorus flow analysis in Norway

Pandit, Avijit Vinayak; Dittrich, Nils Maximilian; Strand, Andrea Viken; Lozach, Loïs; Las Heras Hernandez, Miguel; Reitan, Kjell Inge; Mueller, Daniel Beat

As wild-caught fish become scarce, feed ingredients for farming fish, such as salmon, are increasingly sourced from agricultural plants that depend on mineral fertilizers. Since these fish are naturally carnivorous, they have difficulty digesting the phosphorus in plant-based feed. So additional phosphorus supplements are added to the feed, resulting in a disproportionate increase in mineral phosphorus use and emission. Aquatic food production is increasingly relying on agriculture and mineral phosphorus resources. The feed surplus and the excreta are seldom collected and recycled, leading to a massive loss of nutrients to water bodies and the seafloor, resulting in local risk for eutrophication. Norway currently produces more than half of the world’s Atlantic salmon, and it is set to increase production from currently 1.5 to 5 Mt. in 2050. This has large implications for feed supply and emissions globally. There is a lack of studies that analyze the phosphorus system in aquatic food production at a sufficient spatial and temporal granularity to effectively inform interventions for a more circular use of phosphorus. Here, we present a multi-scale phosphorus flow analysis at monthly resolution ranging between 2005 and 2021 for aquatic food production in Norway and quantitatively discuss the effectiveness of alternative strategies for improving resource efficiency. The results indicate that P emissions from aquaculture have nearly doubled in the period between 2005 and 2021. The P use efficiency (PUE) in Norwegian aquaculture was 19% in 2021. The addition of phytase to the feed could improve the PUE by 8% by reducing P supplements and emissions by 7 kt/y. The use of Integrated Multi-Trophic Aquaculture close to fish farming sites could absorb emissions by 4 kt/y by creating new marine food products. Sludge collection systems could reduce P emissions by 4 to 11 kt/y, depending on the technology. Using the sludge in local agriculture would exacerbate the current P accumulation in soils close to the coastline, given that the animal density in this region is already high. Hence, a large and sophisticated processing infrastructure will be needed to create transportable, high-quality secondary fertilizers for effective sludge recycling in regions with a P deficit.

Frontiers Media S.A.

2023

Chromosomal damage as markers of genotoxicity and carcinogenesis.

Vodicka, P. E.; Vodickova, L.; Polivkova, Z.; Musak, L.; Dusinska, M.; Vodenkova, S.; Vymetalkova, V.; Kroupa, M.; Naccarati, A.; Kumar, R.; Hemminki, K. J.

2016

Chromium (VI) speciation through the environment. NILU PP

Aspmo, K.; Uggerud, H.; Vadset, M.; Brorström-Lundén, E.; Kaj, L.; Woldegiorgis, A.

2007

Chlorpyrifos and neurodevelopmental toxicity: Critical assessment and expert elicitation. NILU OR, 80/2010

Magnanti, B.L.; Carreira, S.; Saunders, M.; Koppe, J.G.; Calamandrei, G.; Keune, H.; Bartonova, A.; von Krauss, M.K.

2010

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