Keifuku Consultant - Wakasa Bay

Restoration Project

Keifuku Consultant - Wakasa Bay

Restoration Objective:

This study aimed to determine how long the seaweed species composition and coverage on the artificial reef takes to reach the climax as the natural reef? To address the above research question, the objective of this study is to monitor and compare the brown seaweed, especially the Sargassaceae distribution and coverage multi-temporally at five points, as well as to investigate their succession over the observation times (second and fourth years) on the artificial reef constructed in Wakasa Bay, Japan.

Site Selection Criteria:

The artificial reefs were constructed in Wakasa Bay (Fig. 1). This bay is located in the Japan Sea at Honshu Island between the Cape Echizen at the east and the Cape Kyoga at the west. Fukui Prefecture installed the artificial reef near a natural reef in Hiruga offing in the east part of the bay. The water depth on the east side (Stns. 1–4) is approximately 8–10 m and that on the west side is approximately 6–8 m, and the bottom sediment is sand. On the other hand, the water depth on the natural reef (Stn. 5) is approximately 5–6 m, and the bottom sediment is greenstone (Nakae et al., 2002). A natural reef extends from the artificial reef toward the land side.

Cause Of Decline:

Unfortunately, 6,400 ha of seagrass and seaweed beds have been lost along Japan’s coast, of which Sargassaceae beds accounted for 22% from 1978 to 1991 due to the increase in coastal landfill sites at ports (Terawaki et al., 2003).

Key Reasons For Decline:

Water Pollution

Scientific Paper

Secular change in seaweed species composition and coverage of Sargassaceae on the artificial reef in Wakasa Bay, Japan

Matsui, A., Kawamura, M., Nozawa, S., Takeyama, M., & Inoue, N. (2024)..https://pubmed.ncbi.nlm.nih.gov/39412541/

Organisation:

Site Observations:

Observation Date

1st Nov 2017 – 1st Oct 2021

Action Summary:

An artificial reef was constructed nearby a natural kelp forest to promote restoration of Sargassum in the area. Monitoring occured for 4 years following construction.

Lessons Learned:

Long-term monitoring of species composition is essential, as overall seaweed coverage on artificial reefs may recover rapidly while ecological succession continues over several years. Community composition shifted from early colonising species such as Sargassum horneri and Sargassum confusum toward later dominance by Myagropsis myagroides and Sargassum patens, while differences among sampling sites suggested that proximity to nearby natural reefs may influence restoration trajectories and species colonisation patterns.

Project Outcomes:

The seaweed coverage on the artificial reef was already over approximately 80% in the second year after construction. However, the dominant species changed to S. horneri in the second year after construction and M. myagroides in the fourth year after construction. Thus, the recovery of species composition takes longer than that of coverage. Therefore, observing species composition recovery is essential when constructing the artificial reef.

Area of Restoration (Ha)

2

Distance to nearest kelp forest (in metres)

50

Indicator Data:

Indicator:

Ending Value:

Starting Value:

Kelp Cover

88.0000
%
0.0000
%