About the Expedition
On January 21, 2010, scientists from the Coral Reef Ecosystem Division of the NOAA Pacific Islands Fisheries Science Center (CRED/PIFSC), along with visiting scientists from the Hawaii Division of Aquatic Resources, Scripps Institution of Oceanography, San Diego State University, the US Fish and Wildlife Service, and local agencies in American Samoa, departed on a three month expedition to Johnston Atoll, Howland and Baker Islands, American Samoa, Jarvis Island, Palmyra Atoll, and Kingman Reef aboard the NOAA Ship Hi'ialakai. This is the fifth biennial Pacific Reef Assessment and Monitoring Program (Pacific RAMP) expedition to American Samoa and the seventh to the Pacific Remote Island Areas. The expedition is sponsored by NOAA's Coral Reef Conservation Program (CRCP) and is divided into three segment sequentially led by Chief Scientists Benjamin Richards, Rusty Brainard and Jamison Gove.READ MORE...
The strategic goal of this research is to improve scientific understanding of coral reef ecosystems throughout the Pacific, and serve as the basis for improved conservation and resource management. The recent designation of the Pacific Remote Islands Marine National Monument highlights the importance of this research.
With their extremely isolated location, many of the Pacific Remote Island Areas host a vibrate marine ecosystem. Previous Pacific RAMP cruises have documented relatively high coral cover and diversity; and high densities of large-bodied reef fish including large numbers of apex predators such as Grey Reef Sharks (Carcharhinus amblyrhynchos) and Scalloped Hammerhead sharks (Sphyraena lewini). Many of these apex predators are rare near human population centers. AS in previous years, this Pacific RAMP cruise will perform a suite of standardized multi-disciplinary methods which include Rapid Ecological Assessments (REA) for fish, corals, other large invertebrates, and algae; towed-diver surveys for large-bodied fish and habitat composition; and oceanographic studies, which include the measurement of conductivity, temperature, and density of the water column (CTD casts); water sampling; and deployment of sea-surface temperature (SST), subsurface temperature recorders (STR) and acoustic doppler current profilers (ADCP). Scientists will also be deploying Ecological Acoustic Recorders (EARs) to learn about changes in the presence and activity of marine mammals, fish, crustaceans and other sound-producing marine life when researchers aren't there to record it otherwise. Autonomous reef monitoring structures (ARMS) will also be deployed as part of the CReefs project. ARMS are simple, standardized collecting structures designed to roughly mimic the structural complexity of reef habitats. They allow for the identification of small, hard-to-sample, but ecologically important cryptic invertebrates. ARMS are being utilized throughout the Pacific and globally to systematically assess spatial patterns and temporal changes of biodiversity. Use of the EARS and ARMS are an exciting addition to RAMP data collection efforts.Follow along below to learn more about where we are going, what we are seeing, and what we have found ...
Friday, April 30, 2010
In the days since the ship returned to port we have been offloading equipment and getting everything back to its rightful place, ready for our next expedition to the Northwestern Hawaiian Islands in September of 2010. We want to thank everyone who followed along with our expedition and especially those of you who wrote in with your questions and comments. We hope that we have been able to answer most of them and look forward to hearing from you again on future expeditions.
With that, we will sign off for now. As the Northwestern Hawaiian Islands expedition begins, we will host a new blog and will post the address both here and on the CRED FaceBook page where you can follow-along with all of the most up-to-date information on our program.
Thursday, April 22, 2010
|Towed-diver Kevin Lino surveys the fish of Jarvis Island|
|Towed-diver forward-facing view; top panel; Typical photograph from the benthic towed-diver.|
- Jarvis was largely dominated island-wide by the species of hard coral Montipora aequituberculata.
- The west side has an extensive population of Sinularia (soft coral) found nowhere else around the island, extending ~ 300 meters north-south at the 50 foot survey depth, and covering nearly 100% of the bottom.
- Live, branching Pocillopora and Acropora coral fragments were found along the south-facing shore, suggesting a recent weather/wave event.
- All macroinvertebrates (crown-of-thorns sea stars, sea cucumbers, giant clams, urchins) counts were low. While the reasons for this remain unclear, potential causes include predation pressures or lack of suitable benthic habitat.
|Images obtained from towed-diver surveys of Jarvis Island: Montipora aequituberculata , left panel; Sinularia dominance on the western side of the island, upper right panel; Broken Pocillopora colonies, lower right panel|
- While towed-diver surveys recorded localized proliferation of a number of hard coral genera, the majority of benthic segments were dominated by a species of Porites along the forereef and western terrace.
- Low levels of bleaching were observed within numerous genera around Palmyra; additional analysis of towed-diver photographs will further explore the extent of coral bleaching around the atoll..
- Visible macroinvertebrates (crown-of-thorns sea stars, sea cucumbers, giant clams, urchins) were nearly absent from our surveys.
|Images obtained from towed-diver surveys of Palmyra Atoll. Partially bleached coral, left panel; forereef, left side; the forereef benthic and fish community, upper right panel; |
Missing macroinvertebrates, lower right panel
- Hard and soft coral cover varied between habitats, and varied depending upon depth and exposure to wave energy. However, overall hard coral cover for all pooled surveys was nearly identical as all pooled surveys around Palmyra.
- The southeastern backreef continues to harbor the highest concentration of giant clams (Tridacna spp.) of anywhere we surveys around the Pacific.
- The east-side backreef adjacent to the shipwreck showed a dramatic increase in cyanobacteria at 50’ – 60’ since the previous 2008 surveys, along with the presence of a fish aggregation device (FAD) not seen before.
|Images obtained from towed-diver surveys of Kingman Reef. Fish Aggregation Device (FAD) seen from below, left panel; Cyanobacteria bloom near the shipwreck , middle panel; Giant Clams along the southeastern backreef, right panel|
Tuesday, April 20, 2010
Response by Jason Helyer, Coral Reef Specialist
This is a great question, but a difficult one to provide a straight forward answer for. Some researchers believe that the cold, nutrient-rich waters that bathe the west side of Jarvis (see blog post “Questions pertaining to the Oceanography of Jarvis Island” regarding upwelling at Jarvis) may provide biological communities at Jarvis protection from climate change associated impacts. In other words, if adjacent ocean temperatures rise, the waters around Jarvis may remain cooler thanks to upwelling associated with the EUC. This cooler water could provide protection to corals at Jarvis from bleaching from rising sea surface temperatures associated with global warming. But this is just a thought shared by some scientists and we really do not know how the oceanographic conditions around Jarvis might change with a changing climate. For example, if the EUC changed as a result of a changing climate, either weakening or deepening, the effects at Jarvis could be substantial as the impact of the current on the oceanographic conditions at Jarvis is a dominant feature structuring the reef community. This uncertainty makes it difficult to answer large questions about how systems might change from global warming and is one of the main reasons why it is important to monitor both biological and physical processes at these remote reefs.
Question 2: In reference to your post that "Jarvis has about 300 times more predatory fish biomass than the entire island of Oahu." What are the factors that reduce the predatory fish volumes in Oahu?
Response to this question as well as the following are by Brian Zgliczynski, Fish Biologist
There are multiple factors that negatively impact populations of predatory fishes. They include fisheries extraction, pollution, and habitat loss. However, fisheries extraction has been shown to have the most deleterious effect on the abundance and biomass of predatory fishes globally. Artisanal, commercial, and recreational fisheries typically target large-bodied commercially-valuable fishes that play an important role in structuring marine ecosystems. As large-bodied species are removed from the system the abundance and biomass of large-bodied predatory species available in the system is reduced.
Question 3: Does illegal fishing occur in the waters around Jarvis and what impact does it have on the trophic pyramid?
Jarvis is one of the most remote and isolated islands under U.S. jurisdiction. This geographic isolation affords Jarvis some protection from anthropogenic disturbances including fisheries. However, this same geographic isolation makes Jarvis potentially vulnerable to illegal fishing activities. As fish populations near inhabited coastal areas are reduced, the threat of commercial fisheries moving offshore to exploit resources at remote and uninhabited islands like Jarvis can become a reality. Fortunately, Jarvis has been designated as a National Marine Monument and is managed and protected under U.S. law out to the 50 nautical mile boundary. This designation provides the necessary legal protection and technologies are being developed to monitor and enforce the Monument boundaries. To date, we have not observed any signs of illegal fishing activities during our biennial reef assessment and monitoring efforts.
Question 4: How does the percentage of predatory biomass at Jarvis compare to Cocos Islands and other areas with high levels of predatory biomass?
Having conducted similar surveys throughout the tropical Pacific including Cocos Island (Costa Rica), the predatory biomass densities observed at Jarvis are among the highest. Additionally, all of the sites where predatory species are abundant display similar inverted trophic pyramids with predatory species accounting for the largest proportion of total fish biomass.
Response by Jamison Gove, Oceanographer and Chief Scientist of the current expedition
Question 1: You mention that "few places on the planet have the oceanographic and coral reef environment that is found at Jarvis" could you tell me what other places in the Pacific have both the oceanographic features and the high-productivity coral reef that Jarvis does?
Due to the remote nature of the central equatorial Pacific, I imagine there may be a few islands that have similar ecosystem dynamics as those observed at Jarvis; however, it is the particular location and shape of Jarvis Island which facilitates its oceanographic and biological uniqueness, and when combined with limited human presence over the past half-century, it remains a rarity.
Question 2: I guess something similar happens around the Galapagos and that is a result of the Cromwell Current, as well, but how does the situation there compare to the oceanographic conditions at Jarvis?
They two island ecosystems are comparable as the Equatorial Undercurrent (a.k.a. Cromwell Current) fuels the high productivity at both the Galapagos and Jarvis. That being said, fundamentally different physical oceanographic dynamics occur between the two ecosystems. At the latitude of Jarvis Island, the EUC is flowing incredibly fast for an open ocean current (~1 meter/second) at a depth of 100-150 meters. When this fast moving, subsurface current interacts with Jarvis it results in a cessation of flow, and due to pressure differences, isotherms (lines of equal temperature) are forced vertically upward to the near surface. This island-current interaction driving upwelling is a result of Bernoulli dynamics, which happens to be the very same physical mechanism which gives airplane wings lift.
Due to the upward tilt of the EUC and the thermocline from west to east across the Pacific (see figure below), the EUC is near the surface (0 – 50 meters) at the latitude of the Galapagos Islands. As such, the Galapagos are surrounded by nutrient-rich waters. The productivity at the Galapagos is also enhanced (and therefore my explanation confounded) by natural iron input associated with the geological make-up of the Galapagos Islands, but that’s another question best left for another time.
The upwelling at Jarvis only occurs to the western side of the island, principally due to the fact that the EUC is an eastward flowing current. Surprisingly, there can be a 1-3 ºC difference between the western side of the island and the eastern side (see figure below). Given that Jarvis is only 4 x 2 kilometers, this is a rather substantial gradient in temperature over a very short distance.
There is definitely seasonal and interannual variability in upwelling at Jarvis. Seasonally, the strongest upwelling at Jarvis occurs during northern hemisphere spring, due to a locally shallow thermocline and shallow and strong EUC. Year to year differences in upwelling are driven by the strength of the trade winds in the western Pacific and their impacts on flow of the EUC; intensified trade winds associated with La Niña conditions favor the shoaling and strengthening of the EUC at Jarvis, and therefore strong upwelling, while a weakening of the trade winds results in a slackening and deepening of the EUC, diminishing or all together shutting down upwelling. Presumably, this variability would impact local fish and benthic coral reef communities; however, we have yet to analyze the data collected during the current El Niño to confirm this statement
Monday, April 19, 2010
‘Reef Biodiversity: an Introduction’ posted on the 4th of February introduced coral reef diversity and the Autonomous Reef Monitoring Structure (ARMS). This post will explore the recovery and processing of these platforms.
|ARMS awaiting removal on left, encapsulated ARMS on right|
We remove the ARMS from the benthos by attaching a milk crate lined with an 80 micron mesh over the center stack of plates comprising the structure. A buoyed rope is then attached to the latching straps on the crate, and the whole unit is pulled to the surface. The milk crate ensures that any recruited organisms within the ARMS will not fall out during transport. Once on the surface and in the small boat, the milk crate encapsulated ARMS is placed within seawater-filled bins and transported back to the Hi‘ialakai.
Back on the ship, the ARMS is disassembled within a tub of seawater. The milk crate is detached, and each layer (plate) is removed individually. The top and bottom of each plate is photographed to document the sessile organisms. Once photographed, a paint brush is used to lightly sweep any motile organisms off the plates and into a bucket of seawater. The plates are then placed in ethanol to preserve the DNA for future molecular processing.
|An example of a plate photograph|
The final task is to scrape the sessile organisms from the all the plates. The scrapings are bulked and preserved. In this manner, we are able to remove, preserve, and store all of the sessile and motile organisms that have recruited to the ARMS.
|ARMS processing in action. Upper left, disassembling; lower right, brushing;|
middle, photography; lower right, sieving; upper right, scraping.
|Examples of invertebrates found within the ARMS|
Saturday, April 17, 2010
|Kingman Reef from above|
|The only emergent land at Kingman; a narrow |
strip of coral rubble and coarse sand
|A cluster of Giant Clams (Tridacna maxima ) |
at Kingman Reef
Kingman Reef is an uninhabited, triangular shaped reef that is mostly submerged. A small, single strip of “dry land” composed of mainly of dead and dried coral skeletons, is located on the eastern rim of the reef. With the highest point of land at approximately 1 meter, the island is often awash during high tide and is inhospitable for most organisms. Despite the harsh surface conditions Kingman Reef supports a vast variety of marine life below. Approximately 130 species of corals are known at Kingman and giant clams are abundant in shallow waters. Predators dominate the waters at Kingman similarly to most of the uninhabited islands we visit.
|Oceanographer Chip Young surveys |
the reef at Kingman
We’ll be here for the next 6 days conducting our standard suite of work before beginning the transit home.
Thursday, April 15, 2010
Tuesday, April 13, 2010
|Chris Depkin surveys the wildlife at Jarvis Island|
|A Masked Booby
dactylatra ) chick awaits
its mother's return
The isolated nature of Jarvis Island (> 200 miles from the next nearest island) makes visitation difficult and is generally accomplished only once every two years. On 01 April, two members of the US Fish and Wildlife Service, Jiny Kim and Chris Depkin, were dropped off on the north-west shore of the island. They spent the next 5 days and 4 nights exploring the terrestrial environs for the purpose of assessing the state of the seabird communities, looking for signs of unauthorized human presence, identifying and neutralizing any hazards to wildlife, mapping and inspecting the island’s vegetation communities for changes in distribution patterns and looking for recent, non-native plant introductions.
|A White Tern
(Gygis alba) finds|
a perch to view its surroundings
|A Hermit Crab searches for food|
The region is just now emerging from the current El Niño event and our visit to Jarvis seemed to support the above. Although thousands of seabirds were present during this visit, the vast majority were in the very early stages of nesting, either sitting on eggs or standing around, on territory, getting ready. Chris and Jiny documented the presence of very few chicks either alive or dead (dead chicks indicate earlier breeding attempts that failed) which indicates little or no nesting has occurred here over the last several months. Very preliminary and crude estimates suggest there were less than 150,000 birds present on the island during this visit. Previous visits place estimates well over one-million birds present during peak nesting.
After walking more than 30 miles during the 5 day period, locating and counting breeding birds and mapping vegetation distributions, Jiny and Chris were picked up where they were dropped off, not to return for another 2 years.
Jarvis Island is without question a rare jewel set in the vastness of the Pacific Ocean. On January 6th, 2009, President George W. Bush established the Pacific Remote Islands Marine National Monument. Jarvis Island NWR along with Howland and Baker island, Johnston, Wake, and Palmyra Atolls, and Kingman Reef are all included in this new Marine Monument which contains 86,888 square miles of mostly open ocean and the above uplands. The areas designated by this new Monument are used by over 4 million breeding tropical seabirds and at least 10 million more that are pre-breeders or migrants passing through those waters on their way to Northern and Southern breeding grounds. Protecting these remote places cannot be overstated, important not only for the marine and terrestrial organisms that live there but for the enjoyment, benefit and educational opportunities afforded future generations.
|The last bit of light before the sun sets over the Pacific|
Friday, April 9, 2010
|Palmyra Atoll from above. Photograph by Stuart Sandin|
|A school of Rainbow|
Runner (Elagatis Bipinnulata).
Photograph by Danny Merritt
|Manta Ray (Manta birostris),|
Palmyra Atoll. Photograph by Chip Young
Tuesday, April 6, 2010
|Typical reef scene at Jarvis Island with large-bodied predatory species |
patrolling the reef.
|Predatory species like jacks and sharks |
are abundant at Jarvis
Saturday, April 3, 2010
|Grey Reef Sharks often congregate in the tens to hundreds at Jarvis Island|
|A few Raccoon Butterfly fish |
make their way down the reef
|Schools of small fish are common |
at Jarvis Island