of the various behaviors and adaptations that have evolved in marine environments , bioluminescence stands out as one of the particular importance , given the fact that it has evolved independently more than 40 times ( haddock et al . 2010 ) . while it does not necessarily give specific advantage to species in cold environments , the long periods of continuous darkness that characterize winters at high latitudes create an environment , at least with respect to light , that is similar to the deep - sea . depending on which taxa
these include defensive functions such as the  counter - illumination ,  the  burglar alarm  and offensive mechanisms such as  prey attraction  and  intraspecific communication 
other adaptations have evolved in both phytoplankton and zooplankton to survive in these harsh conditions that relate more to metabolic rates and the actual vertical space occupied in the water column within which a species spends the winter months .
one such strategy is to enter a dormant state and overwinter at depth , seen for the copepods calanus glacialis and c. hyperboreus which are commonly reported to enter a state of diapause at depth during winter months ( fortier et al .
they , then , return to shallower water in the summer to take advantage of the high productivity rates ( ashjian et al .
2009 ) for the first time provide acoustic evidence of active vertical migrations of zooplankton throughout the polar night in the high arctic .
more recently , this phenomenon was corroborated in the southern hemisphere where diel vertical migration ( dvm ) was shown to continue through the austral winter in the lazarev sea , but ceased during the austral summer ( cisewski et al .
the goal of the current study was to characterize plankton abundance and distribution patterns during a time of year that has rarely been studied by means of vertical net tows and autonomous underwater vehicle ( auv ) surveys .
fitted on the auv were adcps , a ctd and a bathyphotometer designed to register bioluminescence potential in the water column .
data were collected off the coast of ny lesund in kongsfjord , svalbard ( 7857 n , 1156 e ) in ~120  m of water from january 19 to 22 , 2010 .
spatial and temporal dynamics of acoustic backscatter , salinity , temperature and bioluminescence were measured using a remus-100 auv ( moline et al . 2005 ) .
the vehicle was equipped with upward and downward facing rd instruments 1,200-khz workhorse navigator acoustic doppler current profilers ( adcp ) , configured in this study to provide relative acoustic backscatter as an estimate of scattering volume , rather than current velocities , a neil - brown ctd and a bioluminescence bathyphotometer ( bp ; moline et al .
the bp utilizes an impeller to continuously draw a measured volume of water into a chamber through the front of the nosecone where bioluminescence is measured by a photomultiplier tube at 60  hz [ see herren et al .
( 2005 ) for details ] . for statistical purposes , we restricted our analysis to the non - zero observations .
the auv was deployed at 10:27 , 12:25 and at 13:40 ( local time 19th of january ) at depths of 15 , 45 and 75  m , respectively .
the vehicle was also deployed at 21:30 ( 19th of january ) along the same transect as during the  day  but ran one mission surveying the transect at 15 , 45 and 75  m successively without breaks between each depth .
adcp data were processed to remove noise and calculate relative backscatter coefficient ( sv ) according to deines ( 1999 ) for the data collected between 0.5 and 5.0  m away from either side of the vehicle . following the auv deployments ,
continuous bp observations were made from 15:00 on january 21 , 2010 until 09:00 on january 22 , 2010 at 1  m depth at the ny lesund harbor about 2  km from the study site . for logistical reasons ( power supply , stable holdfast for the instrument and weather conditions ) ,
it was not possible to carry out the continuous bp observations in the fjord at the same place as the auv deployments .
however , given the short distance between the two locations and the absence of any physical barriers , the two sites are regarded as comparable for the examination of circadian rhythm ( see also " discussion " ) .
concurrent with the remus deployments , vertical net hauls were conducted using a wp2 plankton net , 180-m mesh size with a 0.25  m opening . in order to collect vertical net hauls from the same depths surveyed by the remus adcp ,
two replicates from each depth were taken from 300  m , 600  m and from 900  m between 10:3013:00 lt . during the nighttime auv deployment , replicate hauls were taken between 300  m , but inclement weather resulted in only one sample from 600  m was collected and none between 900  m. to determine species composition and abundance for specific depth intervals of 6030  m and 9060  m , the results from 300  m were subtracted from those of 600  m , and results from 600  m from those of 900  m , respectively . additionally , the remus bp was equipped with cylindrical plankton nets ( 20-m mesh size ) , and these nets were fitted to each of the two exhausts of the bp ( moline et al .
2009 ) , which hence provided two replicate samples from each of the depths ( 15 , 45 and 75  m ) sampled using the auv . for all plankton samples ,
samples were later enumerated and identified to the lowest possible taxonomic unit using a leica stereomicroscope with 6.340 magnification .
the temperature , salinity and density profiles were similar between night and day during the sample period ( fig .  1 ) and did hence not reveal any major advection events that would otherwise influence the measurements and results presented below . based upon willis et al . ( 2006 )
, physical parameters indicated that the water mass in kongsfjord was of artic water origin .
bioluminescence was detected throughout the water column both night and day , with higher bioluminescence at depth during the day and increased surface bioluminscence at night ( fig . 
comparison of the bioluminescence at the specific depths also provided that this result with significantly greater bioluminescence intensity per flash was observed at 75  m during the day and at 15  m at night ( table  1 ) , suggesting that the organisms with more intense flashes , i.e. , larger zooplankton ( see moline et al .
1vertical profiles of a temperature ( c ) , b salinity ( ppt ) , c density ( kg  m ) and d bioluminescence ( photons / l ) as a function of depth ( m ) taken from the remus auv during the final ascents from 75  m during the day and night deployments .
daytime observations represented in gray and nighttime in black . for this profile , bioluminescence for the upper water column ( < 45  m ) was significantly less than that for the lower water column during the day ( mann  whitney , p  =  0.009 , n  =  102 ) and higher bioluminescence in the upper water column at nighttable  1mean bioluminescence intensity per flash ( se ) surveyed by the auv at the three different depths during the daytime and nighttime deployments ( lt is local time)depth ( m)mean intensity / flash ( 10 ) daytime ( 10:3014 :    25 lt)mean intensity / flash ( 10 ) daytime ( 21:3022:30 lt)mean s 
 v difference ( day 
night)159    2 * 160    142 
 16457    28    3357518    6 * 
 4    1 
 17significant differences were found between depths using mann
 whitney ( *  p  =  0.016 , n  =  1,030 ; 
 p  =  0.025 , n  =  286 ; 
 p  =  0.022 , n  =  126 ) , and additionally , the difference in the mean acoustic backscatter coefficients ( s 
 v ) between day and night is shown for each depth .
the differences in s 
 v between day and night were significant ( mann  whitney , p  <  0.001 ) at all depths vertical profiles of a temperature ( c ) , b salinity ( ppt ) , c density ( kg  m ) and d bioluminescence ( photons / l ) as a function of depth ( m ) taken from the remus auv during the final ascents from 75  m during the day and night deployments .
daytime observations represented in gray and nighttime in black . for this profile , bioluminescence for the upper water column ( < 45  m ) was significantly less than that for the lower water column during the day ( mann  whitney , p  =  0.009 , n  =  102 ) and higher bioluminescence in the upper water column at night mean bioluminescence intensity per flash ( se ) surveyed by the auv at the three different depths during the daytime and nighttime deployments ( lt is local time ) significant differences were found between depths using mann 
whitney ( *  p  =  0.016 , n  =  1,030 ; 
 p  =  0.025 , n  =  286 ; 
 p  =  0.022 , n  =  126 ) , and additionally , the difference in the mean acoustic backscatter coefficients ( s 
 v ) between day and night is shown for each depth .
the differences in s 
 v between day and night were significant ( mann  whitney , p  <  0.001 ) at all depths it is important when interpreting changes in bioluminescence signals that the circadian rhythms in the bioluminescence potential of planktonic organisms be taken into account ( batchelder et al .
the continuous bp observations at the ny lesund harbor showed no evidence of a circadian rhythm in the bioluminescence signal ( fig . 
2 ) in a location ( sheltered by the pier and with a max depth of 5  m ) where vertical migration of zooplankton would be restricted .
organisms collected by net hauls next to the moored bp and by nets connected to the bp during this period using identical methods described above for the auv showed > 80% similarity to the study transects ( data not shown ) , thus making these results applicable to the observations made by the auv.fig . 
2hourly means of log bioluminescence potential ( solid black line ) with standard deviations ( dotted black lines ) collected at 1  m depth from 15:00 lt on january 21 to 09:00 lt on january 22 , 2010 , ( n  =  9,545 , non - zero observations ) . flashes per unit time were also found to be consistent throughout the time series hourly means of log bioluminescence potential ( solid black line ) with standard deviations ( dotted black lines ) collected at 1  m depth from 15:00 lt on january 21 to 09:00 lt on january 22 , 2010 , ( n  =  9,545 , non - zero observations ) . flashes per unit time were also found to be consistent throughout the time series estimates of relative backscatter coefficient as a relative measure of zooplankton biomass in a 10-m swath around the prescribed vehicle depths showed significantly higher intensity between 70 and 80  m during the day , and between 10 and 20  m and 4050  m at night ( table  1 ) . in combination with the changes in bioluminescence intensity , these data demonstrated a coordinated movement of biomass indicative of dvm .
plankton enumerations from wp2 vertical net hauls show an increase above 60  m in the majority of the most abundant zooplankton taxa at night , including pseudocalanus spp .
these genera have been reported to present throughout the year in this regions ( lischka and hagen 2005 ) .
table  2 provides specific species classification and shows that this increase above 60  m at night is also apparent in the enumerations of other less abundant taxa including calanus finmarchicus , acartia longiremis , oncaea borealis and eukrohnia hamata . of these , metridia lucens , metridia longa , oncaea borealis , thysanoessa inermis and thysanoessa longicaudata most likely account for the increase in high - intensity bioluminescent flashes at 15 and 45  m during the night ( table  1).table  2concentrations of the plankton captured by the 180  m wp2 plankton net during the day and at night for depth intervals 300 , 6030 and 9060  mtaxadepth ( m)ind./m ( day)ind./m ( night)taxadepth ( m)ind./m ( day)ind./m ( night ) 
 calanus finmarchicus 
 030  5082 
 heterorhabdus norvegicus*030  < 1<13060  411483060  < 166090 
896090  4 
 calanus glacialis 
 030  410 
 harpacticus chelifer 
 030  9503060  31313060  543060901476090  < 1 
 calanus hyperboreus 
 030  < 11harpacticoida spp.030  2<13060 
< 1<13060  11<16090  46090  < 1 
 pseudocalanus spp.030  3,10010,300 
 oithona atlantica 
 030  3887253060  < 116,8203060  < 15556090  7756090  < 1 
 microcalanus spp.030  5632,300 
 oithona similis 
 030  4008253060  1631,9003060  < 11,3356090 
636090  131 
 metridia lucens*030  317appendicularia*030  17153060  4183060  336090  66090  96 
 metridia longa*030  < 1<1 
 limacina helicina 
 030  2<13060  < 133060  < 116090  116090  12 
 acartia longiremis 
 030  175375 
 sagitta elegans 
 030  < 123060  < 13853060  5116090  < 16090  12 
 paraeuchaeta norvegica 
 030  < 1<1 
 eukrohnia hamata 
 030  4303060  1<13060  2216090 
< 16090  11 
 diastylis lucifera * 
 030  < 1<1 
 thysanoessa longicaudata*030  < 123060  1<13060  376090  < 16090  2 
 bradyidius similis 
 030  < 11 
 thysanoessa inermis*030  < 1<13060  < 133060  < 1226090  66090  < 1 
 oncaea borealis*030  12<13060  512006090  < 1asterisks indicate organisms known to be bioluminescent concentrations of the plankton captured by the 180  m wp2 plankton net during the day and at night for depth intervals 300 , 6030 and 9060 
m asterisks indicate organisms known to be bioluminescent plankton enumerated from the > 20  m net collection of the bp exhaust suggests that during the day , the greatest biomass occurred at 45  m and was dominated by copepod nauplii , copepod eggs and the tintinnid acantostomella norvegica ( table  3 ) .
the same three groups of organisms dominated the biomass at 15 and 75  m. other major contributors at each of these three depths were ceratium and protoperidinium spp .
microcalanus spp . , oithona similis and oithona atlantica ( table  3 ) , consistent with the wp2 nets samples ( table  2).table  3concentrations of the plankton captured by the 20  m plankton nets covering the remus bp exhaust for daytime deployments at 15 , 45 and 75  mtaxadepth ( m)ind / m 
 taxadepth ( m)ind / m 

 ceratium arcticum 
 15229copepod nauplii*151,40945352452,72675246751,403 
 ceratium fusus * 
 159.6copepod eggs159034591.3451,6317580.3751,372 
 ceratium furca 
 15<1 
 oncaea borealis * 
 15545134552754754 
 protoperidinium spp.*15211 
 harpacticoida spp . 

microsetella norvegica 
 1574539145775387754diatom spp.151015545594577580754 
 acantostomella norvegica 
 151,252 
 oithona atlantica 
 1567452,02345117758277559 
 salpingella acuminata 
 15241 
 oithona similis 
 157245163451117512275108 
 heliocostomella subulata 
 152 
 eukrohnia hamata 
 15<1451345175<175<1 
 parafavella denticulata 
 157gastropoda larvae15234533453375457511 
 calanus finmarchicus 
 158appendicularia*1511458453975117521 
 paraeuchaeta norvegica ciii 
 15<1membranipora larvae1519451452075<17521 
 acartia longiremis 
 1529bivalve larvae15<1457457751875<1 
 pseudocalanus spp.15205 
 limacina helicina 
 15<14521545<175154754 
 microcalanus spp.15137 
 thysanoessa longicaudata * 
 15<14543745<175140751asterisks indicate organisms known to be bioluminescent concentrations of the plankton captured by the 20  m plankton nets covering the remus bp exhaust for daytime deployments at 15 , 45 and 75  m asterisks indicate organisms known to be bioluminescent evident from organisms collected from both net sampling approaches is that the day / night changes in the vertical distributions of bioluminescence and acoustic scattering resulted from the larger zooplankton .
and appendicularia ) collected by the wp2 vertical net tows showed decreased abundance at the surface ( upper two depth layers ) during the day than during the night and the highest abundance of this size class was found at depth during the day ( table  2 ) . the smaller size class ( pseudocalanus spp , microcalanus spp .
histograms of the bioluminescence intensity ( data not shown ) in conjunction with plankton enumerations from each depth suggest that an underlying low - to - intermediate - intensity bioluminescence was consistent between day and night and likely attributed to the dinoflagellates , from protoperidinium that occurred throughout the water column and to a lesser degree , ceratium furca and c.fusus that were present in significantly lower abundances ( table  3 ) .
though ubiquitous in the world s oceans and important from an ecological and evolutionary perspective ( for review see haddock et al .
2010 ) , few studies have described bioluminescent communities and their distributions in the arctic , particularly during the winter darkness .
buskey ( 1992 ) , and lapota et al . ( 1989 , 1992 ) examined bioluminescence distributions and community structure with the goal of developing methodology to use bioluminescence as a way to measure total biomass and light budgets of a given water mass during the spring in the greenland sea , during the fall in the beaufort sea and in summer in a norwegian fjord , respectively .
in contrast , this study quantified the bioluminescent community during the polar night and demonstrated the absence of circadian rhythm in bioluminescence .
furthermore , both the diurnal distribution of bioluminescence intensity and concurrent changes in acoustic backscattering provide independent evidence for an active dvm of the larger bioluminescent zooplankton ( and likely non - bioluminescent zooplankton ) within the upper 75  m of the water column .
histograms of intensities showed the major differences between day and night occurring at the highest intensities , which is consistent with larger zooplankton ( lapota et al .
1992 ; moline et al . 2009 ) and with the enumerations in this study .
bioluminscence and acoustic backscatting may in fact not be directly linked , but the circumstantial evidence provided herein suggests that the diurnal signal in bioluminescence is in fact caused by vertically migrating organisms .
numerous studies have examined proximal triggers for dvm ( forward 1988 ; ringelberg 1995 ; ringelberg and van gool 2003 ; benoit - bird et al . 2009 ) , and many others have looked at triggers for the inhibition of bioluminescence as related to its circadian rhythm ( batchelder et al .
1992 ; kelly and katona 1966 ; raymond and devries 1976 ; swift et al . 1995 ) .
interestingly all studies have in one way or another implicated a relative or absolute change in irradiance intensity , angle or daylength as a means of regulation for both dvm and the circadian rhythm of bioluminescence . although changes in light during the time of this study are not visible to the human eye , it is possible that they were sufficient to initiate dvm in the organisms present at the time of the study as was suggested in the study by berge et al .
( 2009 ) . however , while external light cues may play a role in regulating dvm , it might not be the only factor relevant to consider for understanding this behavior .
it has been well established for photosynthetic dinoflagellates and for heterotrophic dinoflagellates of the protoperidinium genus that the bioluminescent inhibition occurs when light intensities are greater than the intensity of bioluminescence of the organisms themselves ( sweeney et al .
this phenomenon could explain why no circadian rhythm existed in bioluminescence during december and january in antarctica ( raymond and devries 1976 ) and may also be related to the absence of a circadian rhythm in bioluminescence in the current study .
previous studies have found that protoperidinium spp contributed between 20 and 90% of the total light budget from the surface to a depth of 100  m in the beaufort sea ( lapota et al .
1992 ) and that dinoflagellates were estimated to account for 96% of the total light budget in vestfjord , norway ( lapota et al .
1989 ) , so it is reasonable to assume that they were significant contributors to the overall light budget during this study .
wherein the lack of sunlight facilitated an environment where the intensity of bioluminescence was not inhibited by light greater than the bioluminescence of the organisms themselves .
while this regulatory factor has been established for dinoflagellates , it is possible that it plays a role in other bioluminescent taxa as well , such as copepods , appendicularians and arctic krill as in the case of this study .
the most notable finding in this study is the detection of bioluminescent activity among zooplankton during the polar night , which may be an important ecological feature . while the ultimate and proximate explanations for both the bioluminescence and the dvm behavior detected during the campaign fall outside the data collected during this study , these results provide evidence for both endogenous and exogenous control of poorly understood or previously unknown processes
. also , during this expedition , which took place during the darkest period of the polar night , we observed five different species of seabirds actively foraging at sea ; little auk ( alle alle ) , black - legged kittiwake ( rissa tridactyla ) , northern fulmar ( fulmarus glacialis ) , black guillemot ( cepphus grylle ) and brnnich s guillemot ( uria lomvia ) .
these seabirds have , to the best of our knowledge , not been reported to overwinter at these latitudes .
whether bioluminescence and/or dvm are playing roles in the foraging behavior of these visual predators is an exciting possibility , although still an open question . despite the limited scope of this study , results open new lines of enquiry regarding the function and process during a time of year when classical paradigms of arctic ecosystems postulate that organisms are predominately in a state of hibernation ( see berge et al .
ultimately , these questions also have implications for human activities ( i.e. , oil exploration ) in the high arctic , which up until to now has been considered  without life  during the polar night .
 this study examines the composition and activity of the planktonic community during the polar night in the high arctic kongsfjord , svalbard . 
 our results are the first published evidence of bioluminescence among zooplankton during the arctic polar night . 
 the observations were collected by a bathyphotometer detecting bioluminescence , integrated into an autonomous underwater vehicle , to determine the concentration and intensity of bioluminescent flashes as a function of time of day and depth . to further understand community dynamics and composition , 
 plankton nets were used to collect organisms passing through the bathyphotometer along with traditional vertical net tows . additionally , using a moored bathyphotometer closed to the sampling site , the bioluminescence potential itself was shown not to have a diurnal or circadian rhythm . 
 rather , our results provide evidence for a diel vertical migration of bioluminescent zooplankton that does not correspond to any externally detectable changes in illumination . 