Seagrass Meadows, Spain Case Study

Case Study Components

Introduction to the Site

Location: 36.7390 N, 3.4711 W

Observed ecosystem changes

Extinction of Zostera marina and Cymodocea nodosa meadows

CLIMAREST Objectives

Restore Zostera marina and Cymodocea nodosa meadows

Features of Paraje Natural Maro Cerro Gordo

Zostera marina and Cymodocea nodosa meadows, once established on the region's sandy substrate, became regionally extinct in 2007

Rehabilitating seagrass meadows is a key goal for the region, with efforts focused on restoring favorable conditions for their recovery

Ongoing measures aim to mitigate environmental stressors, particularly anchoring and trawling, which are believed to have contributed to their decline

Map indicating the location of Maro Cerro Gordo Natural Protected area, where the restoration project is ongoing. 

Driving Factors and Motivations

Within the Natural Protected Area of Maro Cerro Gordo, there is motivation to restore the extinct Zostera marina and Cymodocea nodosa meadows to enhance ecosystem function and services which includes carbon sequestration water quality improvement, coastal protection, biodiversity conservation, and the enhancement of nursery and breeding habitats for commercially important species.

To facilitate restoring these meadows, the area has set many environmental management strategies in place to mitigate stressors that may have contributed to the meadows' extinction.

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Assessment Phase

Key Factors Considered for Site Assessment

Historical records of meadow existence

Ongoing environmental management efforts

Reduction in fishing activities

Before
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Planning and Design Phase

Primary Objective: Test methodologies for seagrass restoration to find most appropriate methods for the Maro region

Additional objectives

Evaluating possible methods with shoots
Identify the most effective and scalable method for seagrass rehabilitation using shoots for Zostera marina and Cymodocea nodosa
Evaluating seed-based techniques
Evaluate the effectiveness and scalability of seed-based techniques for Zostera marina rehabilitation, with measures such as number of sprigs, sprig length, rhizome elongation, carbohydrate content, pigment concentration, and germination rate
Assess the current status
Assess seagrass meadow rehabilitation in Maro, including sediment and water characterization
Ecosystem services
Investigate meadow's abilities to provide services such as water purification, and oxygen production
Carbon sequestration
Estimate the ability of the meadow to sequester carbon
Nutrient demand
Effect of surplus nutrients on meadow growth
Impacts of seagrass rehabilitation
Evaluate the impact of seagrass rehabilitation on biodiversity, including infauna, seaweeds, and fishes (especially those of commercial interest)
Review calcareous organisms in seagrass leaves
Estimate the amount of calcareous organisms in seagrass leaves per square meter at the moment of maximum leaf length (August-October)

Permits

Regional government of Andalusia

  • Permitting for transplanting Z. marina and Cymodocea nodosa in Maro
  • Permit for the collection of Z. marina from Belyuonech (Morocco) and Cymodocea nodosa from La Garrofa

Relevant EU regulations

EU Nature Restoration Law

  • Sets legally binding targets for restoration of degraded ecosystems
  • Member States are required to restore at least 20% of EU land and sea areas by 2030

Habitats Directive (92/43/EEC)

  • Requires strict protection and conservation measures for Natura 2000 sites

Marine Strategy Framework Directive (2008/56/EC)

  • Mandates achieving Good Environmental Status (GES) of marine waters 

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Implementation Phase

Implementation Process

Conduct literature review and meta-analysis

  • Standarisation of success rate by species, plant portion and area
  • Identification of restoration techniques and large-scale actions
  • Highlight important knowledge gaps in seagrass restoration regarding techniques and environmental measurements

Evaluate environmental and technical factors influencing restoration and rehabilitation outcomes

  • Water and sediment characterisation to assess site viability
  • Assessed different techniques to determine the best for transplanting Zostera marina

Establish a control site within donor population

  • Conducted the same experiments in the donor population to have procedural control
  • Minimisation of donor meadow impact by spreading collection efforts

Complete evaluation of ecosystem services

  • Organic matter accumulation
  • Associated biodiversity
  • Habitat forming by counting eggs and juvenils of different important species
  • Carbon retention

Develop suitability models

  • Assessed historical presence and key environmental variables such as currents, storms, and heatwaves to guide model development

Investigate and assess genetic connectivity and diversity

  • Different populations analysed to assess genetic connectivity and diversity
  • Samples collected and DNA extracted in the Royal Botanic Garden Edinburgh

Monitoring and Data Collection Process

Success indicators

Number of shoots

Leaf length

Meadow area

Additional biochemical analyses on leaves and rhizomes

Scale of replicates

1 meter squared per replicate when comparing methods

0.25-6 meters squared when optimising initial shoot density for method most suitable and scalable

<em> Visualization of Replicate Scale
Visualization of Replicate Scale
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Ongoing Management, Monitoring, and Evaluation Phase

Initial results from the demonstration site

Restoration challenges

Bureaucracy of permitting
Took several months to receive the required permitting
Assessment timeframe
Ecosystem services and long-term restoration success cannot be accurately measured within a three-year project, as many ecological benefits take decades to fully develop