Elsevier

Science of The Total Environment

Volumes 563–564, 1 September 2016, Pages 513-529
Science of The Total Environment

Bioextraction potential of seaweed in Denmark — An instrument for circular nutrient management

https://doi.org/10.1016/j.scitotenv.2016.04.010Get rights and content

Highlights

  • Offshore seaweed production for nutrient circular management is assessed.

  • The impact of different management strategies on eutrophication is calculated.

  • LCA of nutrient and biomass management strategies is developed.

  • Seaweed bioextraction of nutrients is a key for circular resource management.

  • Seaweed cultivation is an instrument to achieve national water quality goals.

Abstract

The aim of the study is to assess the efficacy of seaweed for circular nutrient management to reduce eutrophication levels in the aquatic environment. We performed a comparative Life Cycle Assessment (LCA) of two reference waste management systems treating seaweed as biowaste, i.e. landfill disposal and combustion, and an alternative scenario using the seaweed Saccharina latissima as a resource for biobased fertilizer production. Life Cycle Impact Assessment (LCIA) methods were improved by using a cradle-to-cradle approach, quantifying fate factors for nitrogen and phosphorus loss from fertilized agriculture to the aquatic environment. We also differentiated between nitrogen- and phosphorus-limited marine water to improve the traditional freshwater impact category, making this indicator suitable for decision support in relation to coastal water management schemes. Offshore cultivation of Saccharina latissima with an average productivity of 150 Mg/km2 in Danish waters in 2014 was applied to a cultivation scenario of 208 km2. The bioresource scenario performs better than conventional biowaste management systems, delivering a net reduction in aquatic eutrophication levels of 32.29 kg N eq. and 16.58 kg PO43  eq. per Mg (dry weight) of seaweed, quantified by the ReCiPe and CML impact assessment methods, respectively. Seaweed cultivation, harvest and reuse of excess nutrients from the aquatic environment is a promising approach for sustainable resource cycling in a future regenerative economy that exploits manmade emissions as a resource for closed loop biobased production while significantly reducing eutrophication levels in 3 out of 7 Danish river basin districts. We obtained at least 10% bioextraction of phosphorus manmade emissions (10%, 89% and > 100%) and contributed significantly to local nitrogen reduction goals according to the Water Framework Directive (23%, 78% and > 100% of the target).

Introduction

Marine biomass accounts for over 50% of the primary production of global biomass (Carlsson et al., 2007). Compared to terrestrial biomass, only a small fraction of this is used for production. Coastal ecosystems, which cover < 0.5% of the sea bed, capture 55% of world green (biological) carbon (Nellemann et al., 2009).

This fundamental service is endangered by linear production systems characterized by one-way flow of nutrients, i.e. manmade emissions, from the lithosphere to the hydrosphere, resulting in excess nitrogen and phosphorus that give rise to eutrophication of natural marine and freshwater ecosystems. Manmade emissions are nutrients lost to marine water bodies from Danish land-based activities, e.g. NO3 from agriculture, NH3+ from fish farming; here referred as “emission supply to seaweed cultivation”.

Green-engineered nutrient bioextraction, presented in this study as offshore seaweed production systems floating in open waters, may be used to mitigate continuing eutrophication of marine systems. Cultivation of seaweed in green-engineered open water systems, i.e. on an artificial substrate (ropes deployed in marine water), is isolated from natural habitats since it does not compete with the natural benthic community for the occupation of the sea bottom (Buschmann et al., 2014, Zhang et al., 2009).

Such biobased production systems are a key for transforming linear production systems into circular systems. Engineered production of blue carbon is a circular nutrient management system using land-based emission as a resource for biobased production, thus contributing to restoration of biogeochemical balance. Offshore cultivation of seaweed is a relatively new technology in Europe (www.netalgae.eu), but is developing rapidly and attracting funding in northern European countries such as Denmark (e.g. www.MAB3.dk, www.submariner-project.eu), the Netherlands, Ireland and Scotland (e.g. www.noordzeeboerderij.nl, www.enalgae.eu, www.atsea-project.eu, www.biomara.org).

Conceiving emissions as a resource for seaweed cultivation, if successfully implemented, may be a key green-engineered system for future sustainable blue growth (COM, European commission, 2012, Quilliam et al., 2015). Furthermore, seaweed production and utilization is compatible with the circular economy principle of transforming CCS into carbon capture and use (CCU) by biobased production systems. In this regard, it is important to evaluate the key factors making engineered seaweed cultivation systems sustainable with respect to restoration of marine environmental conditions supporting the conservation of natural ecosystem services (Nellemann et al., 2009).

In this study we consider the most simple and immediate example of how seaweed can transform emissions into bioresources, establishing a circular flow through using harvested seaweed biomass as fertilizer. Loss of nutrients from the lithosphere to the hydrosphere is therefore reduced by returning them to soil. Denmark used cast seaweed as soil fertilizer and conditioner in the 19th century, a practice which has also been popular in other parts of the world, e.g. Spain and Ireland (Villares et al., 2007, Mouritsen, 2013). Seaweed enhances soil quality by improving soil texture and water retention (Craigie, 2011). It also enhances soil microbial biomass and soil respiration rate (Haslam and Hopkins, 1996). The value of the world's seaweed industries producing agrochemicals (fertilizers and biostimulants) is estimated at about US$ 10 m (Craigie, 2011).

The purpose of this paper is: 1) to evaluate the impact of seaweed production and utilization on aquatic eutrophication and 2) to assess to what extent it is possible to counterbalance yearly manmade emissions with a seaweed bioextraction system.

To meet the first aim we perform a Life Cycle Assessment (LCA) on the production and use of seaweed, considering Denmark as case study. For the second aim we compare the bioextraction potential of seaweed with yearly manmade emissions for three different time horizons, taking Denmark as case study.

Section snippets

Goal and scope

We performed comparative LCA of three scenarios for production and utilization of seaweed biomass. The goal of the LCA is to evaluate the impact of three different seaweed biomass management options on aquatic eutrophication (Fig. 1): one scenario applies the bioresource management option, in which 1. macroalgae used as fertilizer (MaFe); the others use two existing disposal options: 2. landfilling and 3. incineration.

The MaFe scenario is a simple system for circular nutrient management to

Life Cycle Inventory (LCI)

The Life Cycle Inventory for the system includes nutrient bioextraction during seaweed cultivation, during which element bioextraction occurs, transport for: 1. pretreatment for biofertilizer production and use; 2. landfilling; 3. incineration with energy production and associated emissions to air and water (Fig. 1). The collected data is presented in Table 1, Table 2.

Life Cycle Impact Assessment methods

Two different impact assessment methodologies consistent with the goal of the LCA were selected at midpoint: ReCiPe (V1.06) (Goedkoop et al., 2013) and CML-IA (baseline V3.03) (Guinée, 2002), the first of which is recommended by Dong et al. (2013) since it has the most updated model for atmospheric fate and the most consistent framework to calculate characterization factor (CF).

Both methods have a spectrum of impact categories that represent environmental issues of concern. Through a

Life Cycle Impact Assessment — results and discussion

The results of LCIA performed on three seaweed management scenarios (Fig. 1) are shown in Table 3 and refer to the functional unit of 1 Mg DW of seaweed. A net negative result means that eutrophication impact is reduced compared to a situation without seaweed cultivation, harvest and management according to the options in Fig. 1. The MaFe management scenario performed best for the impact category marine eutrophication (ReCiPe), eutrophication (CML) and P-limited marine eutrophication. For

Efficacy of seaweed as nutrient management tool

In order to understand to what extent it is possible to counterbalance yearly manmade emissions by seaweed bioextraction, we complemented LCA with a comparison between nutrient emission supply to Danish marine waters and the bioextraction potential of seaweed biomass as a function of: 1) local environmental parameters influencing growth (Seghetta et al., 2016c, Bruhn et al., 2016); 2) size of cultivation area.

A conceptual framework model for future coastal and marine nutrient management is now

Conclusions

The first part of the study used LCA to quantify the impact of three seaweed biomass management scenarios. We proposed improving on the conventional aquatic eutrophication impact categories of ReCiPe and CML by including fate factors for a correct analysis of circular nutrient management. The use of seaweed biomass as fertilizer, i.e. the MaFe scenario, had the lowest environmental impact in terms of marine eutrophication (− 32.29 kg N eq./Mg DW seaweed according to ReCiPe) and aquatic

Acknowledgements

Financial support from the Danish Council for Strategic Research (project no. 11-116872) via the MacroAlgaeBiorefinery (MAB3) project and the Graduate School of Science and Technology, Aarhus University, is gratefully acknowledged. The authors thank Professor Jens Kjerulf Pedersen, head of the Danish Shellfish Centre, Peter Schmedes and Teis Boderskov from Hjarnø Havbrug A/S and Michael Bo Rasmussen (Aarhus University, Denmark) for guided tours and fieldwork-supporting information on the

References (79)

  • Statutory Order no. 1650 on the use of waste for agricultural purposes

  • P. Andersen et al.

    Etablering af nyt havbrug ved Endelave. NATURA 2000 konsekvensredegørelse

  • BIM, Bord Iascaigh Mhara

    The European market for sea vegetables

  • A. Bruhn et al.

    Indholdsstoffer i Tang fra LIMFJORDEN

    (2015)
  • A. Bruhn et al.

    Impact of Local Environmental Conditions on Biomass Yield and Quality of Saccharina latissima

    (2016)
  • A.S. Carlsson et al.

    Micro- and Macro-algae: Utility for Industrial Applications. Outputs from the EPOBIO Project

    (2007)
  • Pia B. Christensen

    Combined Uses — Marine Biomass from Offshore Wind Parks

    (2013)
  • COM, European commission

    Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions Blue Growth Opportunities for Marine and Maritime Sustainable Growth

    (2012)
  • D.J. Conley et al.

    Hypoxia in the Baltic Sea and basin-scale changes in phosphorus biogeochemistry

    Environ. Sci. Technol.

    (2002)
  • D.J. Conley et al.

    Controlling eutrophication: nitrogen and phosphorus

    Science

    (2009)
  • J.S. Craigie

    Seaweed extract stimuli in plant science and agriculture

    J. Appl. Phycol.

    (2011)
  • DAFA

    Danmarks Salg af Handelsgødning 2010/2011

    (2012)
  • DAFA

    Vejledning om Gødsknings og Harmoniregler

    (2013)
  • DCE

    Danish Centre for Environment and Energy

    Denmark's national inventory report 2015

    (2015)
  • DEPA

    Miljøgodkendelse: Hjarnø Havbrug A/S: Endelave

  • Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000. Establishing a Framework for Community Action in the Field of Water Policy

    (2016)
  • DME

    BEATE — Benchmarking af Affaldssektoren 2013, Deponering

    (2013)
  • Y. Dong et al.

    Recommended Assessment Framework, Characterisation Models and Factors for Environmental Impacts and Resource Use

    (2013)
  • M. Edwards et al.

    Cultivating Laminaria digitata

    (2011)
  • ESRI

    ArcGIS Desktop: Release 10

    (2011)
  • A.M. Fredenslund et al.

    Udnyttelse af Tang og Restprodukter til Produktion af Biogas

    (2010)
  • M. Goedkoop et al.

    ReCiPe 2008, a life cycle impact assessment method wich comprises harmonised category indicators at the midpoint and the endpoint level. Report 1, characterization

    (2013)
  • G. Guinée

    Handbook on Life Cycle Assessment, Operational Guide to the ISO Standards

    (2002)
  • B. Hasler et al.

    Structure of BALTCOST Drainage Basin Scale Abatement Cost Minimization Model for Nutrient Reductions in Baltic Sea regions. Deliverable 8.1. The BONUS project RECOCA

    (2012)
  • R. Heijungs et al.

    Environmental Life Cycle Assessment of products. Guide and Backgrounds

    (1992)
  • HELCOM

    HELCOM Baltic Sea Action Plan

  • R.W. Howarth et al.

    Nitrogen as the limiting nutrient for eutrophication in coastal marine ecosystems: evolving views over three decades

    Limnol. Oceanogr.

    (2006)
  • B.H. Jacobsen

    Analyse af Omkostningerne ved en Yderligere Reduktion af N-tabet fra Landbruget med 10.000 tons N

    (2012)
  • M.D. Jensen et al.

    Bæredygtig udnyttelse af fosfor fra spildevand. En operativ vejledning til de danske vandselskaber

    (2015)
  • Cited by (65)

    • Seaweed farming for food and nutritional security, climate change mitigation and adaptation, and women empowerment: A review

      2023, Aquaculture and Fisheries
      Citation Excerpt :

      By analyzing the life cycle, Alvarado-Morales et al. (2013) documented that the total amount of CO2 elimination from the atmosphere through biofuel production from seaweed farming is around 961 kg CO2 per tonne dry weight seaweed. Using highly nutritive leftovers from biofuel production as fertilizer could help retain carbon in soil (Seghetta et al., 2016). The idea of seaweed cultivation as a non-traditional biofuel feedstock aligned with the goals of Climate Resilient Agriculture (Zacharia et al., 2015).

    View all citing articles on Scopus
    View full text