Sustainable production of marine equipment in a circular economy: deepening in material and energy flows, best available techniques and toxicological impacts.

Nowadays a radical revolution in the production field is possible thanks to policies to fight against the environmental crisis and the technological progress, like Circular Economy. Leisure activities at sea are anthropogenic activities that have a potential impact, not only on the marine environment in the use stage (e.g. microplastics) and the end-use stage (e.g. ocean plastic wastes), but also on the manufacturing stage of its life cycle. This last stage is also the most important to prevent and/or reduce the impacts by means, for example of eco-design. This work aims to analyse the marine equipment manufacturing sector using fibre reinforced polymers (that potentially emits VOC with the consequently toxicological impact) from the circular economy prospective to identify sustainable solutions for the manufacturing process stage. The selected case study is a marine equipment job-shop using a Fibre Reinforced Polymers. A methodology to identify sustainable industrial systems previously validated is modified, adapted and applied to this case. The methodology applies 3 tools: Material and Energy Flow Analysis to identify the Improvable Flows of the process, Best Available Techniques analysis, to propose the most appropriate techniques to improve those improvable flows, and the Impact Analysis to evaluate and compare the effects on humans and ecosystems, on both the case study scenario and the improved ones. Ten Improvable Flows have been identified for the process; consequently, fifteen candidates to Best Available Techniques have been proposed aiming to act upon these flows. The application of these techniques in an improved system, allows reducing the amount of material and emissions reducing the impact. The combination of those tools has confirmed to be a very good option for process evaluation considering sustainability criteria. The Impact Assessment has permitted to compare the base case scenario showing a reduction of the impacts by the selected Best Available Techniques.

[1]  A. B. Sebitosi,et al.  Material and energy flow analysis of the Malawian tea industry , 2016 .

[2]  M C Barros,et al.  Integrated pollution prevention and control for heavy ceramic industry in Galicia (NW Spain). , 2007, Journal of hazardous materials.

[3]  Valérie Laforest,et al.  Best Available Techniques: An integrated method for multicriteria assessment of reference installations , 2018 .

[4]  Kai Li,et al.  Research on structural optimization method of FRP fishing vessel based on artificial bee colony algorithm , 2018, Adv. Eng. Softw..

[5]  Brinkmann Thomas,et al.  Best Available Techniques (BAT) Reference Document for Common Waste Water and Waste Gas Treatment/Management Systems in the Chemical Sector. Industrial Emissions Directive 2010/75/EU (Integrated Pollution Prevention and Control) , 2016 .

[6]  Laura Cristóbal Andrade,et al.  Optimization of Improvable Flows by combining BAT Analysis and process simulation , 2014 .

[7]  M T Torres Rodríguez,et al.  Combining LCT tools for the optimization of an industrial process: material and energy flow analysis and best available techniques. , 2011, Journal of hazardous materials.

[8]  Julian M. Allwood,et al.  Sustainable Materials - With Both Eyes Open , 2012 .

[9]  Pere Fullana,et al.  Introducing life cycle thinking to define best available techniques for products: Application to the anchovy canning industry , 2017 .

[10]  M. Huijbregts,et al.  European characterization factors for human health damage of PM10 and ozone in life cycle impact assessment , 2008 .

[11]  M. Ormazábal,et al.  Towards a consensus on the circular economy , 2017 .

[12]  Laura Cristóbal Andrade Development and application of methodologies to get Sustainable industrial systems , 2013 .

[13]  L. Laurin,et al.  Life Cycle Environmental Impact Assessment , 2017 .

[14]  F B Dilek,et al.  Analysis of the best available techniques for wastewaters from a denim manufacturing textile mill. , 2017, Journal of environmental management.

[15]  Karlson Hargroves,et al.  Whole System Design: An Integrated Approach to Sustainable Engineering , 2008 .

[16]  B Hanoune,et al.  Impact of kerosene space heaters on indoor air quality. , 2015, Chemosphere.

[17]  K. Czaplicka-Kolarz,et al.  Material and Energy Flow Analysis (MEFA) of the unconventional method of electricity production based on underground coal gasification , 2014 .

[18]  Darryl Davis,et al.  POLLUTION REDUCTION STRATEGIES IN THE FIBERGLASS BOATBUILDING AND OPEN MOLD PLASTICS INDUSTRIES. , 1987 .

[19]  Laura Cristóbal Andrade,et al.  Material Flow Analysis in a cooked mussel processing industry , 2012 .

[20]  P. M. Bello Bugallo,et al.  Integrated environmental permit through Best Available Techniques: Evaluation of the dairy industry , 2017 .

[21]  Conrad Luttropp,et al.  EcoDesign: what's happening? An overview of the subject area of EcoDesign and of the papers in this special issue , 2006 .

[22]  Seyoum Eshetu Birkie,et al.  Circular economy as an essentially contested concept , 2018 .

[23]  Dirk Cattrysse,et al.  Ease of disassembly of products to support circular economy strategies , 2017, Resources, conservation, and recycling.

[24]  Antoine Esnouf,et al.  Representativeness of environmental impact assessment methods regarding Life Cycle Inventories. , 2017, The Science of the total environment.

[25]  M. C. Taboada Gómez,et al.  Towards sustainable systems configurations: application to an existing fish and seafood canning industry , 2016 .

[26]  Anna Whicher,et al.  Design for circular economy: Developing an action plan for Scotland , 2018 .

[27]  An Derden,et al.  Best available techniques and the value chain perspective , 2018 .