The Nature Conservancy Australia - Port Phillip Bay

Restoration Project

The Nature Conservancy Australia - Port Phillip Bay

Restoration Objective:

Golden kelp forests in Port Phillip have undergone significant decline in the last two decades predominantly because of the great abundance and overgrazing by native purple urchins (Heliocidaris erythrogramma) and warming waters. Urchin barrens have replaced kelp forest across more than 60% of reefs in Port Phillip Bay (~13km2), with up to 90% of golden kelp forests lost from some parts of Port Phillip Bay. Without intervention, further losses of these important ecosystems is predicted.

This project aims to trial and develop techniques to address the loss of golden kelp forests in Port Phillip Bay, by managing urchin abundance and restoring golden kelp forests at scale on rocky reefs in Port Phillip Bay. The project aims to conduct active restoration in up to 1 hectare of urchin barrens in northern Port Phillip Bay and to reduce urchin numbers in at least 4 hectares, to levels that allow for passive and active recovery, while protecting a further 21 hectares of remnant kelp and macroalgae habitat from urchin encroachment. The project aims to trial and develop different techniques for cultivation and outplanting golden kelp, including using green gravel, twine and transplanting methods.

Site Selection Criteria:

Three sites were selected in Port Phillip Bay for the trials. Ricketts Point and Jawbone Marine Sanctuarues were established in 2002 to protect representative and important marine biodiversity. The parks values included the expansive golden kelp and macroalgae habitats found along the shallow sandstone (Ricketts Point) and basalt (Jawbone) reefs. Over the past few decades, due to the overabundance of native sea urchins and changes in water quality and the ecology in Port Phillip Bay, urchin barrens have replaced much of this important habitat in the sanctuaries. A third site is located outside, but adjacent Jawbone Marine Sanctuary. This site has similar characteristics to inside the sanctuary, but urchin densities are higher in this area compared to inside the sanctuary. The aim is to create connectivity between restored areas inside and outside of the marine sanctuary.

Cause Of Decline:

Declines are primarily due to the overabunance and overgrazing by native purple sea urchins (Heliocidaris erythrogramma); however other contributing factors contributing to the changes in kelp and urchin dynamics include warming waters associated with climate change, loss/lack of urchin predators and changes to water quality.

Key Reasons For Decline:

Overgrazing

Predator loss

Climate Change

Imbalance

Organisations:

Parks Victoria is a statutory authority of the Victorian Government responsible for managing a diverse estate of more than 4 million hectares including 3,000 land and marine parks and reserves making up 18 per cent of Victoria’s landmass, 75 per cent of Victoria’s wetlands and 70 per cent of Victoria’s coastline

Site Observations:

Observation Date

8th Apr 2024 – 16th May 2024

Action Summary:

Kelp were grown on seeded twine and seeded gravel and outplanted by divers Transplants were also harvested from healthy populations and transplanted into the restoration area and were attached to limestone boulders

Lessons Learned:

Autumn (April/May) optimum window for outplanting based on weather and water temperatures

Project Outcomes:

Still early days for asessing success, but monitoring conducted ~3 months post outplanting/transplanting indicates good growth and survival for all methods (twine, gravel, transplants)

Area of Restoration (Ha)

0.3

Distance to nearest kelp forest (in metres)

50

Indicator Data:

Transplant Info:
Life Stage:Adult
Source:Wild

Observation Date

10th May 2024 – 17th May 2024

Action Summary:

Kelp were grown on seeded twine and seeded gravel and outplanted by divers Transplants were also harvested from healthy populations and transplanted into the restoration area and were attached to basalt boulders

Lessons Learned:

  • Challenging attaching twine to basalt reef, so trialling twine on coir grow ropes as an alternative to drilling 100's of holes for anchor points
  • Autumn (April/May) optimum window for outplanting based on weather and water temperatures

Project Outcomes:

Still early days for asessing success, but monitoring conducted ~3 months post outplanting/transplanting indicates good growth and survival for all methods (twine, gravel, transplants)

Area of Restoration (Ha)

0.1

Distance to nearest kelp forest (in metres)

10

Indicator Data:

Transplant Info:
Life Stage:Adult
Source:Wild

Observation Date

1st Sep 2022 – 1st Nov 2023

Action Summary:

Native purple sea urchins (Heliocidaris erythrogramma) culled by commerciald divers to reduce densities to 2/m2 to facilitate passive recovery and active restoration

Lessons Learned:

Where urchin abunance was around 4 to 8 per m2, a 3 person dive team could cull ~0.3 hectares per day

Project Outcomes:

Passive recovery of both Ecklonia radiata and other macroalgae has been very promising after first ~12 months

Distance to nearest kelp forest (in metres)

20

Indicator Data:

Observation Date

4th Mar 2024 – 7th Jun 2024

Action Summary:

Native purple sea urchins (Heliocidaris erythrogramma) culled by commerciald divers to reduce densities to 2/m2 to facilitate passive recovery and active restoration

Lessons Learned:

Where urchin densities were high (>10/m2) and habitat is complex with ledge and cryptic habitat in particular, a 3 person dive team was culling ~10,000 urchins per day, and requiring multiple sweeps of the same area over multiple days to deal with urchin in-movement from adjacnet areas and also cryptics coming out when numbers were reduced. Some areas as small as 0.1 hectare required 2 to 4 days of culling to reduce numbers to target densities

Project Outcomes:

Very early days, but there are good signs of passive recovery in urchin barrens which appear to be in a transitional state with some macroalgae returning already

Distance to nearest kelp forest (in metres)

50

Indicator Data: