AMLR 2009 Leg 1 Weekly
Report No. 3
17-24
January 2009
The
crew experienced gray skies, rain, snow and rough seas for most of the Elephant
Island Area, with the worst storm occurring on the 22nd and 23rd of January. A
series of small low pressure systems crossed the area
and produced a confused sea state for most of the sampling dates. Although the
barometric pressure dropped only 42 millibars during
the strongest storm, winds were strong and peaked at more than 50 knots over a 6 hour period. The confused sea state prior to the storm
contributed to intermediate seas of up to 6 meters.
Despite
challenging conditions, the oceanographic crew successfully completed 47 CTD
stations across the Elephant Island Area. Where CTD casts were not possible, XBTs were launched to collect environmental data.
A
series of minor electrical gremlins caused a data-logging computer to crash,
resulting in the partial loss of some data. No other problems were encountered,
besides the normal underwater connector maintenance. Work resumed once the
CTD/SCS computer was replaced, approximately 2.5 hours later.
Phytoplankton
distribution in the West Area and in the western portion of the Elephant Island
Area
Chlorophyll-a (Chl-a) concentration values were monitored
at each station to estimate phytoplankton biomass. In the West Area, Chl-a averaged 0.58 +/- 0.59 mg m-3 at 5 m depth in the West Area.
Elephant Island Area values averaged 0.70 +/- 0.57 mg m-3 over 25
stations at 5 m depth.
In
both Areas, there is a significant difference in the distribution and biomass
of phytoplankton in pelagic waters (depth > 1000 m) as compared to coastal
waters:
* In
the West Area, Chl-a concentration values were 0.37 +/-0.48 mg m-3
in pelagic waters and 1.04 +/- 0.60 mg m-3 in coastal waters.
* In
the Elephant Island Area, Chl-a concentration values were 0.48 +/- 0.57 in pelagic waters and
1.02 +/- 0.41 in coastal waters.
These
values are comparable to the 18-year mean values at 5 m depth recorded during
Leg 1 between 1990 and 2007:
*
0.52 +/- 0.83 mg m-3 in pelagic waters and 1.14 +/- 0.98 mg m-3
in coastal waters for the West Area
*
0.39 +/- 0.56 in pelagic waters and 1.3 +/- 1.3 in coastal waters for the
Elephant Island Area.
The
data were monitored for the presence of a Deep Chlorophyll Maximum (DCM), which
is indicative of iron limitation of phytoplankton biomass in the upper mixed
layer. Data from in-situ Chl-a fluorometer and extracted Chl-a concentration values from depths of 5,
30, 50, 75, and 100 m at every station showed a Deep Chlorophyll Maximum (DCM)
between 60 m and 90 m at nearly all the stations located in pelagic waters. No
DCM was evident at any of the coastal stations. Iron limitation primarily
occurs in the upper mixed layer of the ACC (Antarctic Circumpolar Current)
waters and is a clear indication of the patterns of mixing occurring between
various sources of coastal waters in the AMLR Survey Areas.
Acoustic
estimate of krill biomass
Stormy
weather affected the sampling of the Elephant Island Area, complicating the
estimation of acoustically determined krill biomass. However, with additional
filtering of the acoustic data, we were able to estimate that krill biomass
(g/m2) along individual transects was very low, at less than 0.25g/m2.
This data concurs with the data collected in the West Area last week, which also
produced low biomass estimates along individual
transects.
Total
krill biomass, estimated using the three-frequency krill algorithm, as well as
the SDWBA technique, showed that biomass was less than 10,000 tons! This is an
extremely low value for this Area, and is much lower than historical estimates.
In fact, krill biomass is usually higher in the Elephant Island Area than the
other Areas sampled during the AMLR cruises.
Similar
to what was observed in the West Area, a large signal from other scatterers was present in the Area. Final analysis of the
data has not been conducted, and definitive estimates of occurrence and
distribution await the completion of the survey.
Estimate
of krill and zooplankton abundance and distribution
Krill
and zooplankton were collected at 47 stations in the Elephant Island Area using
the standard IKMT net and protocol. Postlarval krill
were represented in 43 of the 47 samples from the Elephant Island Area with a
mean concentration of 23 (+/- 74) per 1000 m3, four times that in
the West Area. The two largest
catches were made northeast of Elephant Island and contained 1530 and 2340
individuals (264 and 452 per 1000 m3). The overall abundance statistics were quite similar to those
monitored in this area during January 2002 and represent below average values
within the long term data set. The interpretation of
the abundance of krill is similar to that determined using the acoustic data.
Lengths
ranged from 16 to 58 mm but demonstrated a clear bimodal distribution around 44
and 48 mm representing two- and three-year-old krill from the 2006 and 2007 year classes. Males outnumbered females by ca. 2:1 and
95% of all individuals were sexually mature. Interestingly, the two length modes were largely due to
contributions by two-year-old females and three-year-old males. Three-year-old males also dominated the
West Area catch.
Nearly
90% of the mature females were in advanced stages (with ovarian development,
gravid and spent) indicating that krill were actively mating and spawning
during the survey period. The
increased frequency (ca. 50% of samples) and abundance of early calyptopis stage larvae here compared to the West Area
suggests that the major seasonal spawning effort was initiated two to three
weeks ago (late December-early January).
The
aggregate form of the Salpa thompsoni
numerically dominated zooplankton catches for the first time since 2005. The mean abundance estimate,
1334+/-2900 per 1000 m3, is the largest encountered in the Elephant
Island Area during January, while the median catch (454 per 1000 m3)
was similar to values recorded in 1993, 1994, 1998 and 2005. This year small
aggregate salps are predominant in the catches, while
in previous years large aggregates (>35 mm) were common. The presence of
smaller aggregates suggests a delayed chain production period, probably
starting around early to mid-November.
With
mean and median concentrations of 786 +/- 1000 per 1000 m3 and 346
per 1000 m3, copepods are similar to S. thompsoni in abundance. These abundance values are similar to
those encountered over the last two January surveys. The copepod assemblage differs however, in the paucity of
the coastal species Metridia gerlachei and
dominance by small unidentified species. In terms of mean abundance, larval and postlarval Thysanoessa macrura, chaetognaths and Limacina helicina were
relatively important components of the zooplankton assemblage.
Seabird
and mammal observations
Data
on the distribution, abundance and behavior of seabirds and mammals were
collected during underway ship operations in the Elephant Island Area. Forty
transects were collected totaling approximately 690 nautical miles of survey
effort. The seabird community
consisted primarily of (percentage-wise): cape petrel, chinstrap penguin, prion, blue petrel, southern fulmar, white-chinned petrel,
black-browed albatross, gentoo penguin, Wilson's
storm petrel, black-bellied storm petrel, gray-headed albatross, southern giant
petrel, light-mantled albatross, and wandering albatross. Blue petrels, prions, and white-chinned petrels were highly conspicuous
in offshore waters, especially near the Shackleton
Fracture Zone. A strikingly similar pattern was observed in 2005, when
oceanographic conditions were similar to this year, which may suggest a link
between seabird community composition and changes in oceanographic conditions.
Seabird
feeding aggregations (composed of cape petrels, black-browed albatrosses,
gray-headed albatross, white-chinned petrel, and prions)
displayed a high degree of patchiness and were distributed in a few locations
situated along the shelf-break to the west of Elephant Island, north of
Clarence Island, and offshore in the northeast corner of the Elephant Island
grid. We found a similar spatial arrangement of seabird aggregations during
2006, when krill biomass was exceptionally low.
On
19 January we encountered a pod of 5 killer whales (60.34 S, -57 W) that just
made a kill. We were unable to determine what they were eating, but some video
footage was captured. Thousands of birds, mostly cape petrels, albatrosses,
storm petrels, white-chinned petrels, and prions congregated around the feeding
frenzy.
A
total of 225 fin whales (114 sightings) were observed. This is the highest
number of sightings ever recorded during a January AMLR survey. Based on past
AMLR surveys (6 years), we have found that fin whales tend to concentrate in
offshore waters of the Elephant Island Area, especially in the northeast
corner. However, this year fin whales were more broadly distributed throughout
pelagic waters, the shelf-break region, and in waters farther south of Elephant
Island. In addition, an all-time low number of humpback whales were recorded (3
sighting, 6 animals). Two
sightings of southern bottlenose whales were made near the Shackleton
Fracture Zone.
from a
foggy Southern Ocean
Christian
Reiss