Suchergebnisse

One of key activity in the Baltic Sea Region strategy is in transition from linear economy to circular economy. The one of the first step to circular economy is to reduce flow of potentially recyclable material and substance flow to waste pool. The one of possible solution is phytoremediation. The aim of this study is to highlight phytoremediation advantages and limitations in circular economy context at Baltic Sea Region. The first task is to identify phytoremediation technologies for soil and groundwater remediation, second task is to evaluate phytoremediation technologies in Baltic Sea Region context, third task is to give recommendation for land owners, municipalities and governments for phytoremediation technologies application. The results show high potential of phytoremediation technologies in non-point source pollution reduction in agricultural sector. The high potential of phytoremediation technologies application is in decentralized sewage water management systems. The circular economy approach can be applied to digester, wood ash and sewage sludge phytoremediation integration in renewable energy sector by wood chips production. The phytoremediation show high potential as circular economy driving force in Baltic Sea Region. ; One of key activity in the Baltic Sea Region strategy is in transition from linear economy to circular economy. The one of the first step to circular economy is to reduce flow of potentially recyclable material and substance flow to waste pool. The one of possible solution is phytoremediation. The aim of this study is to highlight phytoremediation advantages and limitations in circular economy context at Baltic Sea Region. The first task is to identify phytoremediation technologies for soil and groundwater remediation, second task is to evaluate phytoremediation technologies in Baltic Sea Region context, third task is to give recommendation for land owners, municipalities and governments for phytoremediation technologies application. The results show high potential of phytoremediation technologies in non-point source pollution reduction in agricultural sector. The high potential of phytoremediation technologies application is in decentralized sewage water management systems. The circular economy approach can be applied to digester, wood ash and sewage sludge phytoremediation integration in renewable energy sector by wood chips production. The phytoremediation show high potential as circular economy driving force in Baltic Sea Region.

Biomass is defined as organic matter from living organisms represented in all kingdoms. It is recognized to be an excellent source of proteins, polysaccharides and lipids and, as such, embodies a tailored feedstock for new products and processes to apply in green industries. The industrial processes focused on the valorization of terrestrial biomass are well established, but marine sources still represent an untapped resource. Oceans and seas occupy over 70% of the Earth's surface and are used intensively in worldwide economies through the fishery industry, as logistical routes, for mining ores and exploitation of fossil fuels, among others. All these activities produce waste. The other source of unused biomass derives from the beach wrack or washed-ashore organic material, especially in highly eutrophicated marine ecosystems. The development of high-added-value products from these side streams has been given priority in recent years due to the detection of a broad range of biopolymers, multiple nutrients and functional compounds that could find applications for human consumption or use in livestock/pet food, pharmaceutical and other industries. This review comprises a broad thematic approach in marine waste valorization, addressing the main achievements in marine biotechnology for advancing the circular economy, ranging from bioremediation applications for pollution treatment to energy and valorization for biomedical applications. It also includes a broad overview of the valorization of side streams in three selected case study areas: Norway, Scotland, and the Baltic Sea. ; This publication is based upon work from COST Action CA18238 (Ocean4Biotech), supported by COST (European Cooperation in Science and Technology). AR and KK: this research was funded by the Slovenian Research Agency (research core funding P1-0245 and P1-0237). AR: this publication has been produced with financial assistance of the Interreg MED Programme, co-financed by the European Regional Development Fund (Project No. 8MED20_4.1_SP_001, internal ref. 8MED20_4.1_SP_001) – B-Blue project. SG, CT, and JO: this work is financed by national funds from FCT – Fundação para a Ciência e a Tecnologia, I.P., in the scope of the project UIDP/04378/2020 and UIDB/04378/2020 of the Research Unit on Applied Molecular Biosciences - UCIBIO and the project LA/P/0140/2020 of the Associate Laboratory Institute for Health and Bioeconomy – i4HB. JaB and WH: the preparation of the manuscript was supported by the Project CONTRA (Conversion of a Nuisance to a Resource and Asset #R090, 2018–2021) of the INTERREG Baltic Sea Region Program, and Polish Ministry of Science and Higher Education from the 2019–2021 science funding allocated for the implementation of international co-financed project W24/INTERREG BSR/2019. Research of Maris Klavins, VB, and LA was supported by ERDF project 1.1.1.1/16/A/050 "Variable fuel gasification for municipal solid waste recovery." MC acknowledges the funding from CEEC program supported by FCT/MCTES (CEECIND/02968/2017) and Strategic Funding UIDB/04423/2020 and UIDP/04423/2020 supported by national funds provided by FCT and ERDF. AD acknowledges financial support provided by European Union's Horizon 2020 research and innovation program under the grant agreement No 857287 and Latvian Council of Science research project No. lzp-2020/1-0054. MKa: the Interreg LAT_LIT Programme, co-financed by the European Regional Development Fund (LLI-525 ESMIC). LB acknowledges the funding from Erasmus + Project No. ECOBIAS 609967-EPP-1-2019-1-RS-EPPKA2-CBHE-JP; GA.2019-1991/001-001. Development of master curricula in ecological monitoring and aquatic bioassessment for Western Balkans HEIs/ECOBIAS. IS and KP acknowledge financial support provided by the projects CZ.02.1.01/0.0/0.0/17_048/0007323 and CZ.02.1.01/0.0/0.0/16_019/0000754 (Ministry of Education, Youth and Sports of the Czech Republic). ZV-G acknowledges support within the project No.1.1.1.2/VIAA/1/16/029 (Formula of peat-free soil conditioner with controlled-release fertilizing effect applicable for soil remediation and quality improvement of agricultural production). IZ: the projects SLTKT20427, KIK 17431 and SARASWATI 2.0. JuB: the project No.1.1.1.2/VIAA/3/19/531 (Innovative technologies for stabilization of landfills – diminishing of environmental impact and resources potential in frames of circular economy). The work conducted by CR, LA-H, and MA was fully financed by Møreforsking AS. ; Peer reviewed