ArticlePDF Available

Bathyal feasting: Post-spawning squid as a source of carbon for deep-sea benthic communities

The Royal Society
Proceedings of the Royal Society B
Authors:
  • Smithsonian Institution National Museum of Natural History

Abstract and Figures

In many oceanic carbon budgets there is a discrepancy between the energetic requirements of deep-sea benthic communities and the supply of organic matter. This suggests that there are unidentified and unmeasured food sources reaching the seafloor. During 11 deep-sea remotely operated vehicle (ROV) surveys in the Gulf of California, the remains (squid carcasses and hatched-out egg sheets) of 64 post-brooding squid were encountered. As many as 36 remains were encountered during a single dive. To our knowledge this is one of the largest numbers of natural food falls of medium-size deep-sea nekton described to date. Various deep-sea scavengers (Ophiuroidea, Holothuroidea, Decapoda, Asteroidea, Enteropneusta) were associated with the remains. Although many of the 80 examined ROV dives did not encounter dead squids or egg sheets (n = 69), and the phenomenon may be geographically and temporally restricted, our results show that dead, sinking squid transport carbon from the water column to the seafloor in the Gulf of California. Based on food fall observations from individual dives, we estimate that annual squid carcass depositions may regionally contribute from 0.05 to 12.07 mg C m-2 d-1 to the seafloor in the areas where we observed the remains. The sinking of squid carcasses may constitute a significant but underestimated carbon vector between the water column and the seafloor worldwide, because squid populations are enormous and are regionally expanding as a result of climate change and pressure on fish stocks. In the future, standardized methods and surveys in geographical regions that have large squid populations will be important for investigating the overall contribution of squid falls to regional carbon budgets.
Content may be subject to copyright.
rspb.royalsocietypublishing.org
Research
Cite this article: Hoving HJT, Bush SL,
Haddock SHD, Robison BH. 2017 Bathyal
feasting: post-spawning squid as a source of
carbon for deep-sea benthic communities.
Proc. R. Soc. B 284: 20172096.
http://dx.doi.org/10.1098/rspb.2017.2096
Received: 25 September 2017
Accepted: 20 November 2017
Subject Category:
Ecology
Subject Areas:
ecology
Keywords:
biological carbon pump, deep sea,
Cephalopoda, food falls, nekton
Author for correspondence:
H. J. T. Hoving
e-mail: hhoving@geomar.de
Electronic supplementary material is available
online at https://dx.doi.org/10.6084/m9.
figshare.c.3946252.
Bathyal feasting: post-spawning squid
as a source of carbon for deep-sea
benthic communities
H. J. T. Hoving1, S. L. Bush2,3, S. H. D. Haddock2and B. H. Robison2
1
GEOMAR, Helmholtz Centre for Ocean Research Kiel, Du¨sternbrooker Weg 20, 24105 Kiel, Germany
2
Monterey Bay Aquarium Research Institute, Moss Landing, CA 95039, USA
3
Monterey Bay Aquarium, 886 Cannery Row, Monterey, CA 93940, USA
HJTH, 0000-0002-4330-6507; SLB, 0000-0001-5169-7686
In many oceanic carbon budgets there is a discrepancy between the energetic
requirements of deep-sea benthic communities and the supply of organic
matter. This suggeststhat there are unidentified and unmeasured food sources
reaching the seafloor. During 11 deep-sea remotely operated vehicle (ROV) sur-
veys in the Gulf of California, the remains (squidcarcasses and hatched-out egg
sheets) of 64 post-brooding squid were encountered. As many as 36 remains
were encountered during a single dive. To our knowledge this is one of the lar-
gest numbers of natural food falls of medium-size deep-sea nekton described to
date. Various deep-sea scavengers (Ophiuroidea, Holothuroidea, Decapoda,
Asteroidea, Enteropneusta) were associated with the remains. Although
many of the 80 examined ROV dives did not encounter dead squids or egg
sheets (n¼69), and the phenomenon may be geographically and temporally
restricted, our results show that dead, sinking squid transport carbon from
the water column to the seafloor in the Gulf of California. Based on food fall
observations from individual dives, we estimate that annual squid carcass
depositions may regionally contribute from 0.05 to 12.07 mg C m
22
d
21
to
the seafloor in the areas where we observed the remains. The sinking of
squid carcasses may constitute a significant but underestimated carbon
vector between the water column and the seafloor worldwide, because squid
populations are enormous and are regionally expanding as a result of climate
change and pressure on fish stocks. In the future, standardized methods and
surveys in geographical regions that have large squid populations will be
important for investigating the overall contribution of squid falls to regional
carbon budgets.
1. Introduction
Most deep-sea benthic communities depend on particulate organic carbon (POC)
that is synthesized in surface waters and eventually settles upon the seabed. Sedi-
ment traps have been used for decades to collect and measure this sinking
material, allowing insight into local carbon budgets [1]. Deep-sea carbon budgets
are often not closed; discrepancies exist between the amount of POC that is cap-
tured in sediment traps and the carbon required to sustain the measured biomass
and respiration of deep-benthic communities [2,3]. However, in situ observations
suggest that the remains of various megafaunal organisms and gelatinous plank-
ton, which are excluded from sediment trap analysis, may locally constitute
significant sources of carbon [49]. The role of medium-sized nektonic carrion
(here defined as the remains of squids, chondrichthyans and teleost fishes of
1100 cm in length) in carbon budgets is largely unknown. Natural observations
of such carrion are so rare that typically only individual observations are pub-
lished [5,10– 12]. The paucity of observations stems from limited access to
the deep-sea habitat with the imaging tools required to observe and quantify
naturally deposited, rapidly consumed carcasses.
&2017 The Author(s) Published by the Royal Society. All rights reserved.
on December 21, 2017http://rspb.royalsocietypublishing.org/Downloaded from
Squids are opportunistic, typically fast-growing carnivores
that constitute a pivotallink between zooplankton, micronekton
and top predators [13]. They appear to be proliferating in the
ocean as a result of teleost overexploitation, warming waters
and deoxygenation [14–17]. Squids have one reproductive
cycle after which they die (semelparity) [18]. Many shallow-
water squid species aggregate to mate and to spawn, which
may locally result in high biomasses. Post-spawning mortality,
after securing egg cases to the seafloor in shallow water, results
in the deposition of squid carcasses—a phenomenon that has
been documented for neritic squid in the family Loliginidae
[19]. Squids are abundant in the open ocean and deep sea,
and carcass deposition should thus also occur in oceanic regions
where large squid populations exist. This is supported by the
fact that squid flesh can be found in the stomachs of abundant
deep-seafloor scavengers [20– 22]. Although the reproductive
behaviour of oceanic squid is poorly known, some species
(e.g. ommastrephids) aggregate for reproduction [23,24].
Nevertheless, observations of squid carrion on the deep seafloor
(greater than 200 m) are very rare; the only published account
involves carcasses of Brachioteuthis, observed off Cape Hatteras,
NC, USA, which were consumed by brittle stars and a type of
crab [23]. Scattered remotely operated vehicle (ROV) obser-
vations of post-spawning ommastrephids on the seafloor have
also occurred (M. Vecchione 2017, personal communication).
Accounts of squid carcasses at the sea surface involve spent
individuals of squid species that experience ‘gelatinous
degeneration’ [25]. The females of these species undergo
mantle tissue breakdown as a result of maturation and spawn-
ing, then float to the surface after release of the eggs [25].
There they are consumed by seabirds and other epipelagic
oceanic scavengers [25]. Various lines of evidence suggest that
postspawning dead squid also transport carbon to seafloor
communities in the deep sea, but in the absence of direct obser-
vations and measurements, the role of squid carrion in the
carbon cycle remains unknown. Here we report on squid food
falls on the deep seafloor of the Gulf of California, Mexico.
2. Results
Between February and April of 2012 and 2015, the Monterey
Bay Aquarium Research Institute conducted surveys in the
deep basins of the Gulf of California using their ROV Doc Rick-
etts. Squid carcasses and the remains of squid egg sheets were
observed on the seafloor during the course of 11 ROV dives (of
a total of 80 dives that reached the bottom) (see: http://mbari.
org/squid-carrion-images). Nine squid carcasses were encoun-
tered, at depths from 1246 to 1698 m, during six of the 11 dives
(figure 1; electronic supplementary material, table S1). Recent
carcass deposition was indicated by the fact that the mantles
of several individuals were still purple due to expanded chro-
matophores, while the arms were white (figure 1; http://
mbari.org/squid-carrion-images). Average mantle length of
squid carcasses was 351 +57 mm (range 281 –452 mm: n¼7)
(for measurements and estimations, see electronic supplemen-
tary material, SM1). A black, elongated mass was in close
proximity to six of the observed squid. Close-up imagery and
sample collection showed that these masses were hatched-
out egg sheets (figure 1). Gonatid squids brood their young
by holding darkened sheets with embedded developing
embryos in their arms [26]. Fragments of egg sheets (without
squid) of up to 540 mm in length were observed between
1072 and 3016 m depth (electronic supplementary material,
table S1). Some locations had multiple fragments, and we sus-
pect that some of these fragments came from the same egg
sheet (as indicated in electronic supplementary material,
table S1). Overall, we examined 55 individual squid food fall
locations based on the observed egg sheet fragments (see:
http://mbari.org/squid-carrion-images). Some of the food
fall locations were more than 450 km apart (electronic sup-
plementary material, table S1). While ROV bottom surveys
were performed in relatively shallow (less than 1000 m), inter-
mediate (1000– 2000 m) and deep (greater than 3000 m)
regions, most squid remains (62 remains) were found during
nine dives in waters between 1072 and 1698 m. The maximum
number of observed squid remains encountered during a
single dive included five squid carcasses and 31 egg sheet
remains (electronic supplementary material, tables S1 and
S2). The two dives that encountered the highest numbers and
densities of squid remains were at the same location (latitude
(a)
(b)
(c)
Figure 1. In situ ROV observations of living squid and squid carrion in the
Gulf of California. (a) Brooding gonatid squid (mantle length approx. 25 cm,
1100 m, dive 344; 24.48N 109.98W). (b) Dead squid with hatched-out egg
mass with seastars (Nymphaster diomedeae) and lithodid crab Paralomis mul-
tispina (1246 m, dive 344; 24.48N 109.98W). (c) an isolated empty squid
egg sheet (length 50 cm, 1615 m, dive 368, 26.68N 1118W). The laser
dots in (a) and (c) are 29 cm apart.
rspb.royalsocietypublishing.org Proc. R. Soc. B 284: 20172096
2
on December 21, 2017http://rspb.royalsocietypublishing.org/Downloaded from
24.408N, longitude 109.888W, in the Cerralvo Trough) in 2012
and in 2015. During ROV dives in the water column, brooding
squid (figure 1) were observed and three collected specimens
of younger ontogenetic stages were identified as Gonatopsis
octopedatus or a closely related species (R. E. Young 2012,
personal communication), suggesting that the dead squid
on the seafloor could belong to this species. Fauna observed
in the vicinity of, or scavenging on, these food falls included
Enteropneusta, Ophiuroidea, Holothuroidea, Decapoda
and Asteroidea (figure 1; electronic supplementary material,
table S1). A ratfish, Hydrolagus melanophasma, was observed
with a roughly 150 50 mm piece of carrion in its mouth
just 150 m from a squid carcass.
3. Discussion
The animal groups that were associated with the squid carcasses
have been observed at other natural food falls [27]. Conversely,
we did not observe grenadier fishes, isopods, zoarcids, liparids
or hagfish—scavengers that are reported to be abundant at arti-
ficial and natural food falls [5,11,27]. While all observed squid
carcasses and the remains of some hatched-out egg sheets had
scavenging fauna associated with them, the majority of the
latter did not, suggesting that this material is less palatable.
Gonatid squid appear to incorporate ink in the egg sheets
[28], which may act as a deterrent to some organisms, including
microbiota [29], thus increasing the time it takes to be con-
sumed. The longer residence time of egg sheet remnants
allowed us to trace back to already-consumed squid, assuming
that for each sheet a spent female squid reached the seafloor.
The 64 occurrences of squidand egg sheets are to our knowl-
edge the largest number of natural deep-sea food falls of
medium-sized nekton reported to date (electronic supplemen-
tary material, table S1). Smith [10] reported 12 food falls in the
Catalina Basin, of which eight may have had a pelagic origin.
Roper & Vecchione [23] reported two presumably spent bra-
chioteuthid squid on the seafloor, which were consumed by
brittle stars and a crab. These authors state that ‘spent, dying
squids that sink to the bottom could provide a significant
source of energy to the deep benthic fauna’ ( p. 59).
We estimate that the average observed carcass, excluding
egg sheets, of 351 mm mantle length (n¼7; see also electronic
supplementary material, SM1) weighs 1.9 kg [30]. Assuming a
scavenging rate of 5 kg d
21
[5,31], such a carcass would take
an average of 9 h to be consumed. However, Collins et al. [31]
also report that in three of nine experimental squid falls, the
bait remained untouched and in two experiments little of the
bait was consumed within the experimental period. Therefore,
9 h may be an underestimate, and squid may lie longer on the
seafloor. In any case, provided the rarity of observations in the
literature, our encounters with these food falls were likely fortu-
nate, and there is potential for high squid carcass turnoveron the
seafloor in certain areas of the Gulf of California. The high con-
centration of squid remains in some areas (up to 0.023 m
22
)also
suggests a regional abundance of these food falls, but the
absence of carcass observations during the majority of the
dives indicates heterogeneity in their deposition. Additionally,
we encountered remains more than 450 km apart, supporting
the notion that this carbon input is not limited to just one
basin within theGulf of California. The finding of squid remains
in two separate years between February and April suggests an
annual event that is spread over at least three months, but
whether or not the deposition of squid carcasses is a continuous,
episodic or seasonal process remains a matter of speculation.
Our data allowed careful estimations of the role of squid
carcass deposition in local carbon budgets. If we assume that
for each egg sheet, a squid carcass was also deposited, then
the density of carcasses would be 00.023 m
22
for a single
dive location (electronic supplementary material, table S2).
Assuming that the pulse of carcasses is an annual event, the
carcasses could locally contribute from 0.05 to 12.07 mg C
m
22
d
21
to the deep seafloor in the areas where they were
observed (electronic supplementary material, SM1 and table
S2). Estimates of POC flux to the deep seafloor greater than
1000 m in the Gulf of California are absent, to our knowledge.
Published records of POC flux measured by sediment traps in
the Guaymas Basin, Gulf of California at 475 m ranged from 2
to 58 mg POC m
22
d
21
(mean ¼21 mg POC m
22
d
21
) [32]. A
direct comparison would suggest that squid food falls may
locally contribute the equivalent of 0.257.4% of the mean
annual sediment trap flux. However, we should emphasize
that (i) the measured POC flux from sediment traps is from
shallower depths than the observed squid remains, and (ii)
the squid food fall calculations are based on individual dives
and squid carcasses were observed on only some of the benthic
dives (11 of 80 dives). Our estimated values of carbon associ-
ated with the carcasses of what is probably a single squid
species are locally relatively high. They exceed estimates for
other nekton food falls [5,10], but they are less than estimates
for certain gelatinous zooplankton species [4,6,8]. Our esti-
mations may be conservative because our calculations are
based on female squid only while male squid are also semel-
parous. Also, we have assumed that the observed carcasses
were the only carcasses deposited in that area that year (i.e.
not taking into account scavenging rates), while deposition
must occur more often. Our estimate of the area observed by
the ROV may be conservatively large, meaning that the density
may be higher than our current measurements. Finally, our cal-
culations only included the carbon associated with the squid
bodies and the squid bodies presumed to have been deposited
with the egg sheets, but not the hatched-out egg sheets them-
selves. An overestimation of our calculated flux could result
if the squid have a lower body mass than estimated here,
because female squid mobilize nutrients from their mantle
and digestive gland to fuel the long brooding time [26,28].
Also, it is possible that in some cases the squid associated
with the egg sheet observed on the sediment was consumed
by benthopelagic predators before it reached the seafloor.
Finally, it is possible that some of the egg sheet fragments
observed in the Cerralvo Trough originated from the same
squid, while we counted them as separate food falls. The
Gulf of California is a suitable area to investigate the role of
nektonic carrion in benthic carbon budgets and future research
efforts should focus on performing standardized survey
studies using in situ observations.
These first quantitative estimates of squid carrion in the
deep sea and the associated scavenging fauna suggest that
sinking squid could be an important local source of carbon,
but this source is currently not taken into account in carbon
budgets. By feeding intensively on mesopelagic prey [33],
and through high growth and metabolic rates [34], gonatid
squid very efficiently capture carbon that is stored in meso-
pelagic communities, including myctophids, which comprise
some of the largest fish biomasses on the planet [35]. As they
descend to meso- and bathypelagic depths for reproduction
rspb.royalsocietypublishing.org Proc. R. Soc. B 284: 20172096
3
on December 21, 2017http://rspb.royalsocietypublishing.org/Downloaded from
and subsequent death, gonatids, and probably other squids,
transport carbon from the epi- and mesopelagic layers to the
deep seafloor. This pathway circumvents the conventional
carbon pump concept of passively sinking particles, and results
in rapid transportation of carbon to the deep sea [22]. Our
results shed light on a process that is probably of global impor-
tance, and one that further links the largest habitats on the
planet, the deep seafloor and the pelagic realm. Squid popu-
lations worldwide are massive, supporting large industrial
fisheries [36]. Annually, sperm whales alone are estimated to
consume as much squid as all human fisheries combined
[37]. Because of the single reproductive cycle, and the typically
short lifespan of squids, populations may provide the deep sea
with annual pulses of carbon worldwide, as suggested from
the diets of abundant deep-sea scavengers [20– 22]. The
squid-associated carbon flux is probably also dynamic. Squid
populations respond flexibly and in some cases positively to
regional environmental change [15– 16]. Together with overex-
ploitation of fishes, this has resulted in a trend observed in
different marine systems where cephalopods are proliferating
[17]. Such potential ecosystem shifts probably change the
squid-associated carbon flux to the seafloor and may locally
result in an alteration of the ocean carbon pump.
Ethics. Our study is mostly based on deep-sea video observations. The
three ROV-captured squid specimens were flash-frozen at 280 C,
and subsequently defrosted and preserved in formalin for preser-
vation and examination. The expedition ‘MBARI’s 2012 Gulf of
California Expedition, R/V Western Flyer.’ (Cruise no. F2011-068)
was approved by the Mexican government via permits CTC/
001340 (from La Secretaria de Relacione Exteriores) and H00/
INAPESCA/DGIPPN/831 (Secretaria de Agricultura, Ganaderia,
Desarrollo Rural, Pesca Y Alimentacion). The expedition ‘2015 R/V
Western Flyer Gulf of California Expedition.’ (Cruise no. F2014-075)
was approved by the Mexican government via permits CTC/
01700/15 (La Secretaria de Relacione Exteriores) and DGOPA-
02919/14 (Secretaria de Agricultura, Ganaderia, Desarrollo Rural,
Pesca Y Alimentacion).
Data accessibility. The data are made available in electronic supplemen-
tary material, tables S1 and S2. ROV track coordinates on which the
distances (d) calculated in electronic supplementary material, SM1
are based and the images of food falls can be found at http://
mbari.org/squid-carrion-images.
Authors’ contributions. H.J.T.H. conceived of the study, designed the
study, helped collect the field data, analysed the data and drafted
the manuscript. S.L.B. helped collect the field data, analysed the
data and helped to draft the manuscript. S.H.D.H. and B.H.R. col-
lected field data and helped to draft the manuscript. All authors
gave final approval for publication.
Competing interests. We have no competing interests.
Funding. Financial support for this study came from the David and
Lucile Packard Foundation (H.J.T.H., S.L.B., B.H.R., S.H.D.H.), the
Monterey Bay Aquarium’s support of S.L.B., the Netherlands Organ-
ization for Scientific Research (NWO) through a Rubicon grant (no.
825.09.016) to H.J.T.H. and by a grant (CP1218) to H.J.T.H. of the
Cluster of Excellence 80 ‘The Future Ocean’. ‘The Future Ocean’ is
funded within the framework of the Excellence Initiative by the
Deutsche Forschungsgemeinschaft (DFG) on behalf of the German
federal and state governments.
Acknowledgements. We thank the MBARI ROV pilots and MBARI’s
video laboratory for their help with collecting, accessing and analys-
ing the ROV video and data. We thank Mariah Salisbury (MBARI) for
making the website with data and images. Two reviewers improved
the manuscript from its original version. Drs Ivo Bobsien and Bas
Hofman are thanked for their help with GIS.
References
1. Ramirez-Llodra E et al. 2010 Deep, diverse and
definitely different: unique attributes of the world’s
largest ecosystem. Biogeosciences 7, 2851 2899.
(doi:10.5194/bg-7-2851-2010)
2. Smith KL, Kaufmann RS. 1999 Long term
discrepancy between food supply and demand
in the deep eastern North Pacific. Science 284,
11741177. (doi:10.1126/science.284.5417.1174)
3. Rabouille C, Caprais JC, Lansard B, Crassous P,
Dedieu K, Reyss JL. 2009 Organic matter budget in
the southeast Atlantic continental margin close to
the Congo Canyon: in situ measurements of
sediment oxygen consumption. Deep Sea Res. Part II
56, 2223 2238. (doi:10.1016/j.dsr2.2009.04.005)
4. Sweetman AK, Chapman A. 2015 First assessment
of flux rates of jellyfish carcasses ( jelly-falls) to the
benthos reveals the importance of gelatinous
material for biological C-cycling in jellyfish-
dominated ecosystems. Front. Mar. Sci. 2, 47.
(doi:10.3389/fmars.2015.00047)
5. Higgs ND, Gates AR, Jones DOB. 2014 Fish food in
the deep sea: revisiting the role of large food falls.
PLoS ONE 9, e96016. (doi:10.1371/journal.pone.
0096016)
6. Lebrato M, Jones DOB. 2009 Mass deposition event
of Pyrosoma atlanticum carcasses off Ivory Coast
(West Africa). Limnol. Oceanogr. 54, 1197– 1209.
(doi:10.4319/lo.2009.54.4.1197)
7. Robison BH, Reisenbichler KR, Sherlock RE. 2005
Giant larvacean houses: rapid carbon transport to
the deep sea floor. Science 308, 16091611.
(doi:10.1126/science.1109104)
8. Smith Jr KL, Sherman AD, Huffard CL, McGill PR,
Henthorn R, von Thun S, Ruhl HA, Ohman MD,
Kahru M. 2014 Large salp bloom export from the
upper ocean and benthic community response in
the abyssal northeast Pacific: day to week
resolution. Limnol. Oceanogr. 59, 745757.
(doi:10.4319/lo.2014.59.3.0745)
9. Christiansen B, Boetius A. 2000 Mass sedimentation
of the swimming crab Charybdis smithii (Crustacea:
Decapoda) in the deep Arabian Sea. Deep Sea Res.
Part II 47, 26732685. (doi:10.1016/S0967-
0645(00)00044-8)
10. Smith C. 1985 Food for the deep sea: utilization,
dispersal, and flux of nekton falls at the Santa
Catalina Basin floor. Deep Sea Res. 32, 417– 442.
(doi:10.1016/0198-0149(85)90089-5)
11. Klages M, Vopel K, Bluhm H, Brey T, Soltwedel T,
Arntz WE. 2001 Deep-sea food falls: first
observations of a natural event in the Arctic Ocean.
Polar Biol. 24, 292– 295. (doi:10.1007/
s003000000199)
12. Soltwedel T, von Juterzenka K, Premke K, Klages M.
2003 What a lucky shot! Photographic evidence for
a mediumsized natural food-fall at the deep-
seafloor. Oceanol. Acta 26, 623– 628. (doi:10.1016/
S0399-1784(03)00060-4)
13. Clarke MR. 1996 Cephalopods in the world’s oceans:
cephalopods as prey. III. Cetaceans. Phil.
Trans. R. Soc. Lond. B 351, 10531065. (doi:10.
1098/rstb.1996.0093)
14. Zeidberg LD, Robison BH. 2007 Invasive range
expansion by the Humboldt squid, Dosidicus gigas,
in the eastern North Pacific. Proc. Natl Acad. Sci. USA
104, 12 948 –12 950. (doi:10.1073/pnas.
0702043104)
15. Stewart JS, Hazen EL, Bograd SJ, Byrnes JEK, Foley
D, Gilly WF, Robison BH, Field JC. 2014 Combined
climate and prey mediated range expansion of
Humboldt squid (Dosidicus gigas), a large marine
predator in the California current system. Glob.
Change Biol. 20, 1832 1843. (doi:10.1111/
gcb.12502)
16. Hoving HJT et al. 2013 Extreme plasticity in life
history strategy allows a migratory predator ( jumbo
squid) to cope with a changing climate. Glob.
Change Biol. 19, 2089 2103. (doi:10.1111/
gcb.12198)
17. Doubleday ZA et al. 2016 Global proliferation of
cephalopods. Curr. Biol. 26, R406R407. (doi:10.
1016/j.cub.2016.04.002)
18. Boyle PR, Rodhouse P. 2005 Cephalopods: ecology
and fisheries. Oxford, UK: Blackwell Science Ltd.
rspb.royalsocietypublishing.org Proc. R. Soc. B 284: 20172096
4
on December 21, 2017http://rspb.royalsocietypublishing.org/Downloaded from
19. Fields WG. 1965 The structure, development, food
relations, reproduction, and life history of the squid
Loligo opalescens Berry. Calif. Dept. Fish Game, Fish.
Bull. 131, 1 108.
20. Martin B, Christiansen B. 1997 Diets and standing
stocks of benthopelagic fishes at two
bathymetrically different midoceanic localities in
the northeast Atlantic. Deep Sea Res. Part I 44,
541558. (doi:10.1016/S0967-0637(97)00008-3)
21. Drazen JC, Bailey DM, Ruhl HA, Smith KL. 2012 The
role of carrion supply in the abundance of
deepwater fish off California. PLoS ONE 7, e49332.
(doi:10.1371/journal.pone.0049332)
22. Drazen JC, Popp BN, Choy CA, Smith KL. 2008
Bypassing the abyssal food web: macrourid diet in
the eastern North Pacific inferred from stomach
content and stable isotope analysis. Limnol.
Oceanogr. 53, 2644 2654. (doi:10.4319/lo.2008.
53.6.2644)
23. Roper CFE, Vecchione M. 1996 In situ observations
on Brachioteuthis beanii Verrill: paired behavior,
probably mating (Cephalopoda, Oegopsida). Am.
Malacol. Bull. 13, 55– 60.
24. Perez JAA, Silva TN, Schroeder R, Schwarz R,
Martins RS. 2009 Biological patterns of the
argentine shortfin squid Illex argentinus in the slope
trawl fishery off Brazil Lat. Am. J. Aquat. Res. 37,
409 428. (doi:10.3856/vol37-issue3-fulltext-11)
25. Nesis KN, Nigmatullin CM, Nikitina IV. 1998 Spent
females of deepwater squid Galiteuthis glacialis
under the ice at the surface of the Weddell Sea
(Antarctic). J. Zool. 244, 185200. (doi:10.1111/j.
1469-7998.1998.tb00024.x)
26. Seibel BA, Robison BH, Haddock SHD. 2005 Post
spawning egg-care by a squid. Nature 438, 929.
(doi:10.1038/438929a)
27. Britton JC, Morton B. 1994 Marine carrion and
scavengers. Oceanogr. Mar. Biol. 32, 369– 434.
28. Seibel BA, Hochberg FG, Carlini DB. 2000 Life history
of Gonatus onyx (Cephalopoda: Teuthoidea): deep-
sea spawning and post-spawning egg care. Mar.
Biol. 137, 519 526. (doi:10.1007/s002270000359)
29. Derby CD, Kicklighter CE, Johnson PM, Zhang X.
2007 Chemical composition of inks of diverse
marine molluscs suggests convergent chemical
defenses. J. Chem. Ecol. 33, 1105 1113. (doi:10.
1007/s10886-007-9279-0)
30. Katugin ON, Shevtsov GA, Zuev MA. 2014
Distribution, size, maturity and feeding habits of
the squid Gonatopsis octopedatus (Cephalopoda:
Gonatidae) in the Sea of Okhotsk and Northwest
Pacific Ocean. Veliger 51, 177– 193.
31. Collins MA, Yau C, Nolan CP, Bagley PM, Priede IG.
1999 Behavioural observations on the scavenging
fauna of the Patagonian slope. J. Mar. Biol. Assoc. U.K.
79, 963 970. (doi:10.1017/S0025315 499001198)
32. Thunell R, Benitez-Nelson C, Varela R, Astor Y,
Muller-Karger F. 2007 Particulate organic carbon
fluxes along upwelling-dominated continental
margins: rates and mechanisms. Glob. Biogeochem.
Cycles. 21, 1 12. (doi:10.1029/2006GB002793)
33. Nesis KN. 1997 Gonatid squids in the subarctic
North Pacific: ecology, biogeography, niche diversity
and role in the ecosystem. Adv. Mar. Biol. 32,
243324. (doi:10.1016/S0065-2881(08)60018-8)
34. Seibel BA, Drazen JC. 2007 The rate of metabolism
in marine animals: environmental constraints,
ecological demands and energetic opportunities.
Phil. Trans. R. Soc. B 362, 2061– 2078. (doi:10.
1098/rstb.2007.2101)
35. Irigoien X et al. 2014 Large mesopelagic fishes
biomass and trophic efficiency in the open ocean.
Nat. Commun. 5, 3271. (doi:10.1038/ncomms4271)
36. Arkhipkin AI et al. 2015 World squid fisheries. Rev.
Fish. Sci. Aquaculture 23, 92– 252. (doi:10.1080/
23308249.2015.1026226)
37. Whitehead H. 2003 Sperm whales: social evolution in
the ocean. Chicago, IL: University of Chicago Press.
rspb.royalsocietypublishing.org Proc. R. Soc. B 284: 20172096
5
on December 21, 2017http://rspb.royalsocietypublishing.org/Downloaded from
... Other documented megafaunal food falls include a whale shark, mobiliid rays (Higgs, Gates, and Jones 2014), and a penguin (Stauffer et al. 2022). It is hypothesized that medium-sized food falls (1-100 cm) such as fishes, crustaceans, cephalopods and large zooplankton contribute significantly to local carbon budgets (Hoving et al. 2017;Smith 1985). Indeed, observations and quantification show that such food fall pulses may locally be similar or even exceed the carbon flux of particulate organic matter, and can supply the seafloor with organic matter over extended regions (Hoving et al. 2017(Hoving et al. , 2023Simon-Lledó et al. 2023;Sweetman and Chapman 2015). ...
... It is hypothesized that medium-sized food falls (1-100 cm) such as fishes, crustaceans, cephalopods and large zooplankton contribute significantly to local carbon budgets (Hoving et al. 2017;Smith 1985). Indeed, observations and quantification show that such food fall pulses may locally be similar or even exceed the carbon flux of particulate organic matter, and can supply the seafloor with organic matter over extended regions (Hoving et al. 2017(Hoving et al. , 2023Simon-Lledó et al. 2023;Sweetman and Chapman 2015). Medium-sized carcasses are rapidly scavenged, typically within hours Scheer et al. 2022). ...
... This suggests no sequential feeding on several food-falls within a short time, or a very rapid digestion. Sinking of larger nekton carrion is mostly unpredictable in space and time except for seasonal die offs after spawning events (Havermans and Smetacek 2018;Hoving et al. 2017). Eurythenes amphipods are indeed able to cope with periods of starvation of up to several months in between meals (Hargrave et al. 1994) due to both morphological (Dahl 1979;De Broyer, Nyssen, and Dauby 2004) and behavioral adaptations (Hargrave 1985;Hargrave et al. 1994 ...
Article
Full-text available
Many benthic deep‐sea animals rely on carcasses from the overlying water column that sink to the seafloor and form local organic enrichments known as food falls. This flux of organic carbon from the shallow pelagic to the deep sea is part of the biological carbon pump (BCP) and as such contributes to carbon sequestration. For a complete understanding of local carbon budgets, it is crucial to identify the diversity and distribution of sinking carcasses which are difficult to detect by observational methods. Here, we analyzed the diet of the abundant amphipod scavenger, Eurythenes gryllus, by DNA metabarcoding to assess their potential to identify food falls in the Fram Strait, a gateway to the Arctic. E. gryllus scavenges on nekton but so far it was not certain whether this represents their main diet. We detected dietary taxa (26 in total) in 20 out of 101 analyzed amphipods. We found that amphipods primarily fed on larger nekton including fish, cephalopods, and mammals, with bony fish being the most targeted food source in terms of diversity and abundance. Only one amphipod had fed on a gelatinous organism. These results support the hypothesis that E. gryllus targets mostly nekton food falls. The diversity of dietary taxa differed between the Eastern and Western Fram Strait, which suggests regional variability in food falls availability. We also detected, for the first time in E. gryllus, infections with the parasitic dinoflagellate Hematodinium. This detection demonstrates the potential of metabarcoding for revealing both food web dynamics and host–parasite interactions in the deep sea. E. gryllus seems a promising “natural sampler” to monitor the diversity of deep‐sea food falls which will help to investigate the importance of medium‐sized food falls in local vertical carbon export in a rapidly changing Arctic Ocean.
... A whale fall occurs when a whale dies and its carcass sinks to the seafloor, creating a fresh supply of labile organic matter that sustains a diverse and unique ecosystem for extended periods. The active organic carbon content of a fully grown whale carcass is equivalent to the background organic carbon flux of 100 m 2 of the deep seafloor over 1000 years (Smith et al., 2014), which can support a diverse ecosystem for approximately 100 years (Li et al., 2022;Smith and Baco, 2003;Hoving et al., 2017). Whale-fall communities typically undergo several successional stages that sometimes overlap (Smith and Baco, 2003). ...
... Although a fully grown whale carcass creates a habitat for diverse and unique organisms over a long period of time, large whale carcasses are rarely found in the natural environment. Small-to medium-sized organic falls or food falls (1-100 cm) (Hoving et al., 2017) are even more challenging to detect in the deep sea because they are rapidly consumed by scavengers (Amon et al., 2017;Scheer et al., 2022). However, food falls including fish carcasses (Amon et al., 2017;Yamamoto et al., 2009;Higgs et al., 2014;Stauffer et al., 2022), cephalopods (Hoving et al., 2017), tunicates (Stenvers et al., 2021), jellyfish (Sweetman and Chapman, 2011), sunken wood (Turner, 1977;Bernardino et al.;Samadi et al., 2010;Fagervold et al., 2012), and plant remains (Wolff, 1979;Vetter and Dayton, 1999) have been reported. ...
... Small-to medium-sized organic falls or food falls (1-100 cm) (Hoving et al., 2017) are even more challenging to detect in the deep sea because they are rapidly consumed by scavengers (Amon et al., 2017;Scheer et al., 2022). However, food falls including fish carcasses (Amon et al., 2017;Yamamoto et al., 2009;Higgs et al., 2014;Stauffer et al., 2022), cephalopods (Hoving et al., 2017), tunicates (Stenvers et al., 2021), jellyfish (Sweetman and Chapman, 2011), sunken wood (Turner, 1977;Bernardino et al.;Samadi et al., 2010;Fagervold et al., 2012), and plant remains (Wolff, 1979;Vetter and Dayton, 1999) have been reported. Additionally, porpoise (Jones et al., 1998a) and dolphin (Kemp et al., 2006) carcasses have been reported at bathyal depths. ...
... produce a single egg mass which is brooded at bathypelagic depths (Seibel et al., 2005). After a single reproductive event, the females die and presumably sink to the seafloor as is known for gonatids in the Gulf of California (Hoving et al., 2017). This life history strategy suggests annual pulses of gonatid carcasses to the seafloor (Hoving et al., 2017), also in the Fram Strait. ...
... After a single reproductive event, the females die and presumably sink to the seafloor as is known for gonatids in the Gulf of California (Hoving et al., 2017). This life history strategy suggests annual pulses of gonatid carcasses to the seafloor (Hoving et al., 2017), also in the Fram Strait. We detected Gonatus sp. ...
Article
Full-text available
The Arctic Ocean is home to a unique fauna that is disproportionately affected by global warming but that remains under‐studied. Due to their high mobility and responsiveness to global warming, cephalopods and fishes are good indicators of the reshuffling of Arctic communities. Here, we established a nekton biodiversity baseline for the Fram Strait, the only deep connection between the North Atlantic and Arctic Ocean. Using universal primers for fishes (12S) and cephalopods (18S), we amplified environmental DNA (eDNA) from seawater (50–2700 m) and deep‐sea sediment samples collected at the LTER HAUSGARTEN observatory. We detected 12 cephalopod and 31 fish taxa in the seawater and seven cephalopod and 28 fish taxa in the sediment, including the elusive Greenland shark (Somniosus microcephalus). Our data suggest three fish (Mallotus villosus, Thunnus sp., and Micromesistius poutassou) and one squid (Histioteuthis sp.) range expansions. The detection of eDNA of pelagic origin in the sediment also suggests that M. villosus, Arctozenus risso, and M. poutassou as well as gonatid squids are potential contributors to the carbon flux. Continuous nekton monitoring is needed to understand the ecosystem impacts of rapid warming in the Arctic and eDNA proves to be a suitable tool for this endeavor.
... Food falls are parcels such as carrion, wood, or macroalgae that sink to the seafloor where they are consumed by benthic and demersal scavengers (Drazen and Sutton 2017;Havermans and Smetacek 2018). Recent studies reveal that food falls are an important food source for deep benthic communities and may at least partly explain the observed discrepancy between particulate organic carbon (POC) input and carbon demand at deep-sea sites (Henschke et al. 2013;Sweetman and Chapman 2015;Hoving et al. 2017;Lebrato et al. 2019). Variations in nutritional value, chemical composition, distribution, and frequency of deposition of food-fall types may be a bottom-up driver of deep-sea scavenger evolution (Havermans and Smetacek 2018). ...
Article
Full-text available
Human pressures are changing ocean environments, such as a shift from fish‐ to squid‐dominated ecosystems in overfished, poorly oxygenated environments. After death, carcasses of upper ocean fauna sink to the seafloor where they provide food for demersal scavengers. It is unclear how shifts in carcass type impact abyssal scavengers. We performed baited benthic camera lander deployments in the Cabo Verde Abyssal Basin to test how a shift from fish‐ to squid‐dominated carrion could modify abyssal scavenger ecology. At the fish bait, peak scavenger abundance was greater and occurred later for the majority of observed fauna. However, removal rates of squid bait were up to 10‐fold greater, and a significantly different community composition developed, favoring faster organisms with lower chemosensory thresholds. At the fish bait, slower organisms were less disadvantaged as the bait persisted for longer periods allowing the development of a more complex community and dense amphipod aggregations. The rapid squid consumption indicates that the accumulation of this type of food fall at the seafloor may not occur, preventing scientific observations necessary to estimate the importance of squid carrion to the biological C pump and deep‐sea food webs. As such, the flux of squid carrion to the seafloor is likely greater than currently recognized in this part of the Atlantic. The differences observed between bait types indicate how future changes in upper ocean ecosystems may impact abyssal scavengers and their ecosystem functions, including controlling seafloor biomass, regulating the behavior of benthic fauna, and contributing to nutrient cycling and energy transfer.
... Given the generally low food availability in deep-sea ecosystems, carbon subsidies associated with abyssal aggregations like M. robustus (particularly semelparous species) should have larger impacts on local energy budgets than in energy-rich shallow or terrestrial ecosystems. Breeding aggregations worldwide generate food subsidies for local biological communities (47), but few such carbon subsidies are known from deep-sea environments [e.g., (48)]. The C subsidy at the Octopus Garden is proportionately large because abyssal habitats are food poor. ...
Article
Does warmth from hydrothermal springs play a vital role in the biology and ecology of abyssal animals? Deep off central California, thousands of octopus (Muusoctopus robustus) migrate through cold dark waters to hydrothermal springs near an extinct volcano to mate, nest, and die, forming the largest known aggregation of octopus on Earth. Warmth from the springs plays a key role by raising metabolic rates, speeding embryonic development, and presumably increasing reproductive success; we show that brood times for females are ~1.8 years, far faster than expected for abyssal octopods. Using a high-resolution subsea mapping system, we created landscape-scale maps and image mosaics that reveal 6000 octopus in a 2.5-ha area. Because octopuses die after reproducing, hydrothermal springs indirectly provide a food supplement to the local energy budget. Although localized deep-sea heat sources may be essential to octopuses and other warm-tolerant species, most of these unique and often cryptic habitats remain undiscovered and unexplored.
... How senescence impacts these life cycles is currently unknown because senescent animals are rarely found, likely due to predation. However, senescent specimens either remain in the same habitat as adults (small-egged octopods), float to the surface (Rodhouse et al., 1987;Xavier et al., 2013) or may sink to the bottom (Roper and Vecchione, 1996;Nesis et al., 1998;Hoving et al., 2017). Based on this and the fact that these habitat changes are not under active control of the organism, the Senescent phase was not treated in Figure 5. ...
Article
Full-text available
Life cycle definitions provide the background for conceptualizing meaningful questions to address the mechanisms that generate different life cycle patterns. This review provides explicit definitions and explanations of the steps in a cephalopod life cycle, from fertilization to death. Each large step, or phase, is characterized by a particular developmental process and morphology. Each phase is composed of smaller developmentally distinct steps, or stages. The cephalopod life cycle is comprised of all or some of the following phases: Embryonic, Paralarval, Juvenile, Subadult, Adult and Senescent, and each life cycle is taxon-specific. All cephalopods have direct development and maintain a consistent body plan throughout ontogeny (i.e., no true larval phase and no metamorphosis). Most cephalopods have a life cycle marked by a long early life and a short adult life followed by senescence. Cephalopods have two developmental modes: they produce either small planktonic hatchlings as paralarvae, or large hatchlings as juveniles. All cephalopods go through a Hatchling stage soon after eclosion during which they rely on two modes of nutrition: endogenous (yolk) and exogenous (prey). Many cephalopods with planktonic paralarvae will become benthic early in their life cycle during their Settlement stage or remain pelagic during their Metapelagic stage. Juvenile growth is fast and ontogenetic changes (outside of gonadal maturation) generally cease at the end of the Juvenile phase. The Subadult phase begins when the definitive adult morphology (except for size and body proportions) is acquired (e.g., full complement of photophores). Sexual organs undergo most of their development during the Subadult phase. The Adult phase starts with spawning competency and concludes when gonads are spent. The Senescent phase begins with spent gonads and ends with death. Using this new terminology, we examine the patterns of cephalopod life cycles and find that there are four main patterns based on the presence of a Paralarval phase and the habitat occupied by each phase: Holopelagic (all phases are pelagic), Holobenthic (all phases are benthic), Merobenthic and Meropelagic (phases alternate between benthic and pelagic environments). In these two last patterns, the main difference is the presence of a Paralarval phase in Merobenthic species. The definitions and terminology proposed here provide a unifying framework for future ecological, evolutionary and life cycles research on cephalopods.
Presentation
Full-text available
A 12-minute presentation on my PhD research on deep-sea squid trophic ecology that was presented during the New Zealand Ecological Society conference in Rotorua.
Preprint
Košťák et al. (2021) is important in presenting the first known Cenozoic fossil of a vampyromorph. Some modifications to the interpretations are needed, however. The first concerns inferring water depth habitat of non-benthic animals from fossils found in deep water sediments. The second concerns the water depth estimates for the La Voulte-sur-Rhône exceptionally preserved biota (La Voulte EPB), and the third, the implications for the model of post-Jurassic migration of Loligosepiids into deep water oxygen-depleted environments.
Article
Fish and other metazoans play a major role in long-term sequestration of carbon in the oceans through the biological carbon pump. Recent studies estimate that fish can release about 1,200 to 1,500 million metric tons of carbon per year (MtC year-1) in the oceans through feces production, respiration, and deadfalls, with mesopelagic fish playing a major role. This carbon remains sequestered (stored) in the ocean for a period that largely depends on the depth at which it is released. Cephalopods (squid, octopus, and cuttlefish) have the potential to sequester carbon more effectively than fish because they grow on average five times faster than fish and they die after reproducing at an early age (usually 1–2 years), after which their carcasses sink rapidly to the sea floor. Deadfall of carcasses is particularly important for long-term sequestration because it rapidly transports carbon to depths where residence times are longest. We estimate that cephalopod carcasses transfer 11–22 MtC to the seafloor globally. While cephalopods represent less than 5% of global fisheries catch, fishing extirpates about 0.36 MtC year-1 of cephalopod carbon that could otherwise have sunk to the seafloor, about half as much as that of fishing large fish.
Article
Full-text available
When pelagic organisms die and fall onto the deep-sea floor they create food falls, i.e., parcels of organic enrichment that subsidize deep benthic scavenging communities. The diversity and quantities of food falls remain unstudied for many ocean regions since they are stochastically deposited and rapidly scavenged. The Southern Ocean habitat supports large populations of megafauna but few food falls have been documented. To investigate the diversity and quantity of food falls in the northwestern Weddell Sea, we analyzed 8476 images from the deep seafloor that were captured during the expedition PS118 on RV Polarstern in 2019 by the camera system OFOBS (Ocean Floor Observation and Bathymetry System). OFOBS was towed 1.5 m above the seafloor along five transects (400 to 2200 m seafloor depth) east of the Antarctic Peninsula. We observed the carcasses of one baleen whale, one penguin, and four fish at depths of 647 m, 613 m, 647 m, 2136 m, 2165 m, and 2112 m, respectively, as well as associated scavenging fauna. To the best of our knowledge, we describe here the first in situ observations of deep-sea food falls for penguins and fish in the Southern Ocean. While the whale carcass seemed in an intermediate successional stage, both the penguin and the fish were likely recently deposited and three of the fish potentially resulted from fishery discards. Our relatively small data set suggests that a diverse array of food falls provide nutrients to the slopes of the Powell Basin.
Article
Full-text available
The deep sea, the largest biome on Earth, has a series of characteristics that make this environment both distinct from other marine and land ecosystems and unique for the entire planet. This review describes these patterns and processes, from geological settings to biological processes, biodiversity and biogeographical patterns. It concludes with a brief discussion of current threats from anthropogenic activities to deep-sea habitats and their fauna. Investigations of deep-sea habitats and their fauna began in the late 19th century. In the intervening years, technological developments and stimulating discoveries have promoted deep-sea research and changed our way of understanding life on the planet. Nevertheless, the deep sea is still mostly unknown and current discovery rates of both habitats and species remain high. The geological, physical and geochemical settings of the deep-sea floor and the water column form a series of different habitats with unique characteristics that support specific faunal communities. Since 1840, 28 new habitats/ecosystems have been discovered from the shelf break to the deep trenches and discoveries of new habitats are still happening in the early 21st century. However, for most of these habitats the global area covered is unknown or has been only very roughly estimated; an even smaller – indeed, minimal – proportion has actually been sampled and investigated. We currently perceive most of the deep-sea ecosystems as heterotrophic, depending ultimately on the flux on organic matter produced in the overlying surface ocean through photosynthesis. The resulting strong food limitation thus shapes deep-sea biota and communities, with exceptions only in reducing ecosystems such as inter alia hydrothermal vents or cold seeps. Here, chemoautolithotrophic bacteria play the role of primary producers fuelled by chemical energy sources rather than sunlight. Other ecosystems, such as seamounts, canyons or cold-water corals have an increased productivity through specific physical processes, such as topographic modification of currents and enhanced transport of particles and detrital matter. Because of its unique abiotic attributes, the deep sea hosts a specialized fauna. Although there are no phyla unique to deep waters, at lower taxonomic levels the composition of the fauna is distinct from that found in the upper ocean. Amongst other characteristic patterns, deep-sea species may exhibit either gigantism or dwarfism, related to the decrease in food availability with depth. Food limitation on the seafloor and water column is also reflected in the trophic structure of heterotrophic deep-sea communities, which are adapted to low energy availability. In most of these heterotrophic habitats, the dominant megafauna is composed of detritivores, while filter feeders are abundant in habitats with hard substrata (e.g. mid-ocean ridges, seamounts, canyon walls and coral reefs). Chemoautotrophy through symbiotic relationships is dominant in reducing habitats. Deep-sea biodiversity is among of the highest on the planet, mainly composed of macro and meiofauna, with high evenness. This is true for most of the continental margins and abyssal plains with hot spots of diversity such as seamounts or cold-water corals. However, in some ecosystems with particularly "extreme" physicochemical processes (e.g. hydrothermal vents), biodiversity is low but abundance and biomass are high and the communities are dominated by a few species. Two large-scale diversity patterns have been discussed for deep-sea benthic communities. First, a unimodal relationship between diversity and depth is observed, with a peak at intermediate depths (2000–3000 m), although this is not universal and particular abiotic processes can modify the trend. Secondly, a poleward trend of decreasing diversity has been discussed, but this remains controversial and studies with larger and more robust data sets are needed. Because of the paucity in our knowledge of habitat coverage and species composition, biogeographic studies are mostly based on regional data or on specific taxonomic groups. Recently, global biogeographic provinces for the pelagic and benthic deep ocean have been described, using environmental and, where data were available, taxonomic information. This classification described 30 pelagic provinces and 38 benthic provinces divided into 4 depth ranges, as well as 10 hydrothermal vent provinces. One of the major issues faced by deep-sea biodiversity and biogeographical studies is related to the high number of species new to science that are collected regularly, together with the slow description rates for these new species. Taxonomic coordination at the global scale is particularly difficult, but is essential if we are to analyse large diversity and biogeographic trends. <br. Because of their remoteness, anthropogenic impacts on deep-sea ecosystems have not been addressed very thoroughly until recently. The depletion of biological and mineral resources on land and in shallow waters, coupled with technological developments, are promoting the increased interest in services provided by deep-water resources. Although often largely unknown, evidence for the effects of human activities in deep-water ecosystems – such as deep-sea mining, hydrocarbon exploration and exploitation, fishing, dumping and littering – is already accumulating. Because of our limited knowledge of deep-sea biodiversity and ecosystem functioning and because of the specific life-history adaptations of many deep-sea species (e.g. slow growth and delayed maturity), it is essential that the scientific community works closely with industry, conservation organisations and policy makers to develop robust and efficient conservation and management options.
Article
Full-text available
Human activities have substantially changed the world's oceans in recent decades, altering marine food webs, habitats and biogeochemical processes [1]. Cephalopods (squid, cuttlefish and octopuses) have a unique set of biological traits, including rapid growth, short lifespans and strong life-history plasticity, allowing them to adapt quickly to changing environmental conditions [2-4]. There has been growing speculation that cephalopod populations are proliferating in response to a changing environment, a perception fuelled by increasing trends in cephalopod fisheries catch [4,5]. To investigate long-term trends in cephalopod abundance, we assembled global time-series of cephalopod catch rates (catch per unit of fishing or sampling effort). We show that cephalopod populations have increased over the last six decades, a result that was remarkably consistent across a highly diverse set of cephalopod taxa. Positive trends were also evident for both fisheries-dependent and fisheries-independent time-series, suggesting that trends are not solely due to factors associated with developing fisheries. Our results suggest that large-scale, directional processes, common to a range of coastal and oceanic environments, are responsible. This study presents the first evidence that cephalopod populations have increased globally, indicating that these ecologically and commercially important invertebrates may have benefited from a changing ocean environment.
Article
Visual behaviors are prominent components of intra- and interspecific communication in shallow-water cephalopods. Meso- and bathypelagic cephalopods were believed to have limited visual communication, other than bioluminescence, due to the reduced illumination at depth. To explore potential visual behaviors in mesopelagic squid, we used undersea vehicles to observe 76 individuals of Octopoteuthis deletron. In contrast to predictions, we found this species capable of a variety of visually linked behaviors not previously reported for a deep-ocean cephalopod. The resultant ethogram describes numerous chromatic, postural, locomotor, and bioluminescent behavioral components. A few common body patterns—the whole appearance of the individual involving multiple components—are characterized. The behaviors observed from individual squid were compared using a Non-metric Multi-Dimensional Scaling (NMDS) ordination, onto which hydrographic and observation parameters were mapped. Observation length, specimen collection, and contact with the vehicle affected which behaviors were performed. A separate NMDS, analyzing the body patterns, indicated that these sets of behavioral components could be visualized as groups within the NMDS ordination. While the functional roles of the behaviors described are not yet known, our findings of numerous behaviors in O. deletron clearly indicate that bioluminescence is not the sole method of visual communication by deep-sea squid.
Article
A behavior that has never been seen in cephalopods was observed three times in a large aggregation of Brachioteuthis beanii Verrill, 1881. During a series of submersible dives off Cape Hatteras, North Carolina, eastern U. S., three pairs of Brachioteuthis were seen, and one pair was video-taped. In all three pairs one squid grasped the other by the posterior mantle in its arm crown. This paired behavior involved brief periods in which the grasped squid bent its head and body posteriorly and vigorously moved its arms around the head and mantle opening of the grasping squid. Although we were unable to capture any of the coupling pairs to determine their stage of maturity, we believe this unusual activity represents mating behavior.
Article
Squid, cuttlefish and octopuses, which form the marine mollusc group the cephalopods, are of great and increasing interest to marine biologists, physiologists, ecologists, environmental biologists and fisheries scientists. Cephalopods: ecology and fisheries is a thorough review of this most important animal group. The first introductory section of the book provides coverage of cephalopod form and function, origin and evolution, Nautilus, and biodiversity and zoogeography. The following section covers life cycles, growth, physiological ecology, reproductive strategies and early life histories. There follows a section on ecology, which provides details of slope and shelf species, oceanic and deep sea species, population ecology, trophic ecology and cephalopods as prey. The final section of the book deals with fisheries and ecological interactions, with chapters on fishing methods and scientific sampling, fisheries resources, fisheries oceanography and assessment and management methods. This scientifically comprehensive and beautifully illustrated book is essential reading for marine biologists, zoologists, ecologists and fisheries managers. All libraries in universities and research establishments where biological sciences and fisheries are studied and taught should have multiple copies of this landmark publication on their shelves.