Spread of Halophila stipulacea in the Caribbean: A Growing Concern

 
 
Dr. Lisamarie Carrubba
NOAA Fisheries, Caribbean Field Office,
Protected Resources Division
 
Spread of the Non-Native
Seagrass, 
Halophila stipulacea
, in
the Caribbean
 
Atlantic Cod EFH
 
Eggs
 
Larvae
 
Juveniles
 
Adults
 
Native to western Indian Ocean – Red Sea and
Persian Gulf, as well as coastal islands of Eastern
Africa and Southeast coast of Indian subcontinent
In 1800’s began to invade Eastern Mediterranean Sea
via Suez Canal
Reached Malta in 1970, Ionian Sea in 1992, and
north coast of Sicily in 1997
First reported in Caribbean in 2002. Thought to have
originally come from pleasure yacht traffic between
Mediterranean and Caribbean.
 
 
 
History of Spread
 
History of 
Halophila stipulacea 
in Caribbean
 
1.
Observed in Flamingo Bay, Grenada in 2002 (Ruiz and Ballantine 2004)
2.
Documented in Dominica and St. Lucia in 2009, including competition with
Syringodium filiforme 
(manatee grass) (Willette and Ambrose 2009)
3.
Reported from Aruba, Curaçao, Grenadines (Grenada), St. Eustatius, St. John
(USVI), St. Martin (France), and St. Vincent and the Grenadines (Willette et al.
2014)
4.
Site of Westin Hotel, Cruz Bay, St. John surveyed in 2005, 2012, and 2013 for
dock replacement project – no seagrass in footprint. Site resurveyed in March
2015and approximately 0.4 acre area around dock colonized by 
Halophila
stipulacea.
5.
Benthic surveys for projects in Charlotte Amalie and Crown Bay areas, St.
Thomas, found it dominates in portions of Long Bay and Crown Bay (2014-2015)
6.
Site inspections by NMFS to Flamingo Bay (dominant species) and Honeymoon
Bay (patch), Water Island (July 2015)
7.
UVI tracking it in Brewers Bay (2010 – not present, now spreading)
8.
Recently observed in 3 locations around Culebra and
          associated islands/cays (July 2015)
 
 
Characteristics of 
Halophila stipulacea
 
1.
Can tolerate a wide range of salinities
2.
Can grow in very shallow water as well as depths
greater than 50 m
3.
Can grow in a range of substrate types
4.
Speculated survival for extended periods as floating
fragments and in vessel anchor wells
5.
Rapid vegetative expansion
6.
Adaptation to high irradiance
7.
Male and female and have been observed flowering
in Caribbean
 
Capacity for Spread
 
Preliminary experiments off St. John in 2014
showed lateral growth up to > 6 m/day
Up to 50% increase in biomass in 7 days
Fish and invertebrates preferentially grazed
on native seagrass species
Density up to > 10,000 shoots/m
2
 
Capacity for Spread
 
Steiner and Willette (2014) observed an
increase and replacement of native species
over 5 years and extension into reef halos
 
NOAA CRCP FY16 RFP includes jurisdictional
priority from USVI DPNR to “to support the
investigation of effects and management of
invasive species, such as addressing key gaps for
improving the understanding of ecosystem
impacts from 
Halophila stipulacea”
 
Opportunity
 
Partners: UVI, NPS, and Dr. Willette (UCLA)
Education and Outreach:
updates to UVI webpage for reporting sightings
(
http://geocas.uvi.edu/citseagrass.php
)
Workshop to discuss potential impact in region (led by Dr. Wyllie-
Echeverria who led work on 
Zostera japonica 
in Northeast Pacific)
Questions:
Degree to which 
Halophila stipulacea 
provides habitat to marine
organisms (nutritional content, herbivory levels, habitat use)
Whether it co-exists or out-competes native seagrass species
Dispersal predictions based on data on current spread
 
Collaboration
 
CFMC categorizes seagrass as EFH – no
species-specific designation
ESA language about habitat for green sea
turtle also discusses broad category of
seagrass
More projects with impacts to 
Halophila
stipulacea
 affect EFH and ESA consultations
and mitigation decisions
 
Regulatory Context
 
Questions?
 
Flamingo Bay, Water Island
 
Dakity, Culebra Island
 
M. Padover
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The non-native seagrass, Halophila stipulacea, has rapidly spread throughout the Caribbean, impacting the marine ecosystem. Originally from the western Indian Ocean, it invaded the Mediterranean and then reached the Caribbean in 2002. Its characteristics include tolerance to various conditions, rapid growth, and high adaptability. Studies show its capacity for extensive spread, outcompeting native species. Efforts are underway to monitor and manage its proliferation to protect the biodiversity of the region.

  • Halophila stipulacea
  • Seagrass spread
  • Invasive species
  • Caribbean marine ecosystem
  • Biodiversity conservation

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  1. Spread of the Non-Native Seagrass, Halophila stipulacea, in the Caribbean Dr. Lisamarie Carrubba NOAA Fisheries, Caribbean Field Office, Protected Resources Division

  2. History of Spread Native to western Indian Ocean Red Sea and Persian Gulf, as well as coastal islands of Eastern Africa and Southeast coast of Indian subcontinent In 1800 s began to invade Eastern Mediterranean Sea via Suez Canal Reached Malta in 1970, Ionian Sea in 1992, and north coast of Sicily in 1997 First reported in Caribbean in 2002. Thought to have originally come from pleasure yacht traffic between Mediterranean and Caribbean. Eggs Larvae Juveniles Adults Atlantic Cod EFH

  3. History of Halophila stipulacea in Caribbean 1. 2. Observed in Flamingo Bay, Grenada in 2002 (Ruiz and Ballantine 2004) Documented in Dominica and St. Lucia in 2009, including competition with Syringodium filiforme (manatee grass) (Willette and Ambrose 2009) Reported from Aruba, Cura ao, Grenadines (Grenada), St. Eustatius, St. John (USVI), St. Martin (France), and St. Vincent and the Grenadines (Willette et al. 2014) Site of Westin Hotel, Cruz Bay, St. John surveyed in 2005, 2012, and 2013 for dock replacement project no seagrass in footprint. Site resurveyed in March 2015and approximately 0.4 acre area around dock colonized by Halophila stipulacea. Benthic surveys for projects in Charlotte Amalie and Crown Bay areas, St. Thomas, found it dominates in portions of Long Bay and Crown Bay (2014-2015) Site inspections by NMFS to Flamingo Bay (dominant species) and Honeymoon Bay (patch), Water Island (July 2015) UVI tracking it in Brewers Bay (2010 not present, now spreading) Recently observed in 3 locations around Culebra and associated islands/cays (July 2015) 3. 4. 5. 6. 7. 8.

  4. Characteristics of Halophila stipulacea 1. Can tolerate a wide range of salinities 2. Can grow in very shallow water as well as depths greater than 50 m 3. Can grow in a range of substrate types 4. Speculated survival for extended periods as floating fragments and in vessel anchor wells 5. Rapid vegetative expansion 6. Adaptation to high irradiance 7. Male and female and have been observed flowering in Caribbean

  5. Capacity for Spread Preliminary experiments off St. John in 2014 showed lateral growth up to > 6 m/day Up to 50% increase in biomass in 7 days Fish and invertebrates preferentially grazed on native seagrass species Density up to > 10,000 shoots/m2

  6. Capacity for Spread Steiner and Willette (2014) observed an increase and replacement of native species over 5 years and extension into reef halos

  7. Opportunity NOAA CRCP FY16 RFP includes jurisdictional priority from USVI DPNR to to support the investigation of effects and management of invasive species, such as addressing key gaps for improving the understanding of ecosystem impacts from Halophila stipulacea

  8. Collaboration Partners: UVI, NPS, and Dr. Willette (UCLA) Education and Outreach: updates to UVI webpage for reporting sightings (http://geocas.uvi.edu/citseagrass.php) Workshop to discuss potential impact in region (led by Dr. Wyllie- Echeverria who led work on Zostera japonica in Northeast Pacific) Questions: Degree to which Halophila stipulacea provides habitat to marine organisms (nutritional content, herbivory levels, habitat use) Whether it co-exists or out-competes native seagrass species Dispersal predictions based on data on current spread

  9. Regulatory Context CFMC categorizes seagrass as EFH no species-specific designation ESA language about habitat for green sea turtle also discusses broad category of seagrass More projects with impacts to Halophila stipulacea affect EFH and ESA consultations and mitigation decisions

  10. Questions? Flamingo Bay, Water Island M. Padover Dakity, Culebra Island

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