66 D aan , N . an d R ingelberg, J. (1969). F u rth e r stu d ies o f th e positive a n d negative p h o to tactic reactio n s o f D aphnia m agna S tra u s. N e th . J . Z o o l. 19: 525— 540. D artn all. H . J. A . (1974). A ssessing th e fitness o f visual pigm ents fo r th e ir p h o tic environm ents. In: A li, M . A . (ed.) Vision in Fish. P lenum P ress, New Y o rk , p. 543— 563. D ouglass, J. K . (1986). T h e o ntogeny o f light a n d d a r k a d a p ta tio n in th e c o m p o u n d eyes o f grass sh rim p , Palaem onetes pugio H o lth u is. P h .D . thesis, D u k e U niversity. Ew ald, W . F. (1910). U b e r O rien tieru n g L o k o m o tio n u n d L ic h t-reak tio n en einiger C ladoceren u n d deren B edeutung fu r die T heorie d e r T ro p ism e n . Biol. Z b l. 30: 1— 16; 49— 63; 379— 384; 385— 399. F o rw ard , R . B., J r. (1976). L ight a n d d iu rn a l v ertical m ig ratio n : p h o to b e h a v io r a n d photophysioIogy o f p la n k to n . In: S m ith, K . (ed.). P hotochem ical and P hotobiological Review, Vol. 1. Ple­ n u m Press, N ew Y ork, p. 157— 209. F o rw ard , R . B., Jr. (1986). A co m p a ra tiv e stu d y o f c ru stace an larv al p h o to resp o n ses (in press). F o rw ard , R . B., J r., C ro n in , T . W . (1979). S p ectral sensitivity o f larv ae fro m in tertid al crustaceans. J. Com p. P hysiol. 133A: 311— 315. F o rw ard . R. B.. J r., C ro n in . T . W ., S te a m s, D . E. (1984). C o n tro l o f diel vertical m igration: P h o to re sp o n se s o f a larval cru stace an . L im nol. Oceanogr. 29: 146— 154. Jerlov, N . G . (1968). O ptical O ceanography. E lsevier. A m sterd am , p. 1— 194. L ang, W . H ., F o rw a rd . R. B., Jr.,-M iller, D . C . (1979). B ehavioral responses o f Balanus improvisus n auplii to lig h t intensity an d sp e ctru m . B iol. Bull. 157: 166— 181. L ythgoe, J. N . (1966). Visual pigm ents a n d u n d e rw a te r vision. In: B ainbridge, R . Evans, G . C. R ack h am , O . (eds.) L ight as an E cological Factor. O xford: B lackw ell, p. 375— 391. Lythgoe, J. N . 1968. V isual p igm ents a n d v isu a l ra n g e u n d erw ater. Vision R es. 8: 997— 1012. M c F a rlan d , W . N „ M u n z, F . W . (1975). T h e ev o lu tio n o f p h o to p ic visual pigm ents in fish. Vision Res. 15: 1071— 1080. M unz. F. W . (1958). T h e photosensitive retin al pigm ents o f fish from relatively tu rb id coastal w aters. J . gen. P hysiol. 42: 445— 459. M unz, F. W „ M c F a rla n d . W . N . (1973). T h e significance o f sp e ctral p o sitio n in th e rh o d o p sin s o f tro p ical m arin e fishes. Vision Res. 13: 1829— 1874. R ingelberg, J. (1964). T h e p ositively p h o to ta c tic re a c tio n o f D aphnia m ag n a S tra u s: a c o n trib u tio n to th e u n d e rsta n d in g o f d iu rn al vertical m ig ra tio n . N eth. J. Sea. R es. 2: 319— 406. Ritz, D . A . (1972). B ehavioral response to light o f th e new ly h atch ed P h y llo so m a larvae o f Panuli­ rus longipes cygnus G eorge (C rustacea: D ecap o d a: P alin u rid ae ). J. exp. m ar. Biol. Ecol. 10: 105— 114. Rose. M . (1925). C o n trib u tio n à l'é tu d e de la biologie d u p la n k to n : le problèm e des m igrations verticales jo u rn aliè res. A rch. Z o o l. exp. Gen. 64: 387— 542. R ozenberg, G . V. (1966). Tw ilight — A stu d y in atm ospheric optics. P len u m Press, N ew Y ork. Russell, F. S. (1927). T h e vertical d istrib u tio n o f p la n k to n in th e sea. B iol. Revs. Biol. Proc. Cambridge Phil. Soc. 2: 213— 262. Shanks, A . L. (1986). V ertical m ig ra tio n a n d cro ss-sh elf dispersal o f larv al Cancer spp. an d R an­ dallia ornata (C ru stacea , B rachyura) o f f th e c o a s t o f so u th e rn C a lifo rn ia . M ar. Biol, (in press). Visscher, J. P., L uce, R. H . (1928). R e actio n s o f cyprid larv ae o f b arn acles to light w ith special reference to sp e ctral color. Biol. Bull. 54: 336— 350. W hite, G . M . (1924). R eactio n s o f la rv a e o f th e sh rim p P alaem onetes vulgaris a n d th e s q u id L oligo pea lii to m o n o c h ro m a tic light. Biol. B ull. 47: 265— 272. P ro ce ed in g s o f th e 21st E M 8 S G d a n s k . 14— 19 S ep tem b er 1986 p. 67— 7 5 1989 P L IS S N 0078-3234 P o lish A c ad em y o f Sciences — In s titu te o f O c ean o lo g y Vlaams Instituut voor de Zee Flanders Marine Institute R ESPIR A TIO N D U R IN G H Y PO X IA O F T H E SH R IM PS CRANGON CRANGON AND PALAEM O N AD SP ERSU S FR O M B R A C K ISH W ATER L. H a g e r m a n 1, A. S z a n i a w s k a 2 1 M arine Biological L ab o rato ry , S tra n d p ro m en ad en . DK.-3000 H elsingor, D en m ark 2 Insty tu t O ceanografii, U niw ersytet G dariski, al. Czolgistów 46, 81-378 G d y n ia, P o lan d A B ST R A C T The respiration o f Crangon crangon a n d Palaem on adspersus w as m easu red u n d e r n o rm o x ic an d hypoxic conditions. All experim ents w ere ru n fo r at least 24 hours (S, 20%o; T , 20°C). In norm oxia Crangon show s a clear diel resp irato ry p attem : highest resp iratio n d u rin g early night an d early m orning, low est in d ay tim e. T his resp irato ry rhythm can be co rre la te d to th e diel activity p attem . T he resp irato ry rh y th m icity d isa p p ears when oxygen tension decreases below ca 100 to rr d u e to a n increase in the average activity o f Crangon (a response to av o id the hypoxic conditions). Crangon can m ain tain its ro u tin e resp iratio n independent o f oxygen ten sio n in the m edium (Pw0 3) dow n to a P wO , o f 30 to rr, th e so-called Pc. T he typical diel m ean ro u tin e re sp ira ­ tory level for in term o u lt Crangon (w.w. 0.25 a n d 1.1 g) are 0.9 a n d 0.2 ml 0 2g _ ’h _1 respectively w hen sa n d is supplied a s su b stra te a n d 1.6 a n d 0.65 m l 0 ;g _1h _1 w hen n o su b s tra te is su p p lied . M oulting h as n o t been n o ted d u rin g th e hy p o x ia resp iratio n experim ents. Palaemon adspersus show s no diel resp irato ry rhythm icity un d er th e given exp erim en tal co n d i­ tions, possibly a result o f a “w ro n g " su b stra te in th e experim ental cham ber. Palaem on can m a in ­ tain its respiratory independency d o w n to a PwO , o f 45 to rr. Typically Palaem on w ith a w et w eight o f for instance 0.7; 1.0 a n d 2.1 g h as a resp iratio n o f 0.65; 0.41 an d 0.13 ml 0 , g - 1 h -1 respectively. T he results are discussed in relatio n to the ecology o f the species a n d specially in relatio n to hypoxic conditions increasingly o ccu rrin g in shallow eu tro p h icated w aters. IN T R O D U C T IO N The increasingly eutrophicated brackish w ater areas are the h a b ita t o f a shrim p stock, which is im p o rta n t from both an ecological as well as an economic viewpoint. In D anish w aters both Crangon crangon and Palaemon adspersus are locally subject to an intense fishery. One consequence o f e u tro ­ phication is im paired oxygen conditions in the shallow w ater, resulting in sh o r­ ter or longer periods o f low oxygen concentrations. M ost o f these periods occur in the sum m ertim e (M iljostyrelsen, 1984) when due to high w ater tem pe­ rature the solubility o f oxygen is already lowered and the m etabolic rate o f 69 68 m ost organism s is higher. Since th e m etab o lic ra te o f th e anim als is influenced and because species show different degrees o f tolerance to changed oxygen conditions, such periods o f low er oxygen co nditions m ay change the balance o f the whole ecosystem. O ur knowledge of the resp irato ry rate ( M 0 2) of brackish w ater anim als is now reasonably good due to im proved techniques a n d b etter understanding o f the physiological processes in the organism s. H ow ever, m ost results published deal w ith sh o rt tim e experim ents, i.e. von O ertzen (1984), H agerm an an d W e­ ber (1981), van D onk an d de W ilde (1981) a n d only few e.g. B utler et al. (1978) record the M 0 2 fo r extended periods. As the respiration is likely to vary w ith time it is im portant (i) to record M 0 2 a fte r th e anim al has recovered from handling and acclimated to the new enviro nm ent an d (ii) to record M O , long enough to reveal any rhythm icity. T hese p recau tio n s m ake it necessary to use a flow -through system for recording the M O ,. Such a system is, however, always better th an a closed one (von O ertzen, 1984). The purpose o f the present p a p e r is th u s to record th e M O , o f Crangon crangon and Palaemon adspersus u n d e r n o rm oxic an d hypoxic conditions for a t least diel periods. R ESU LTS R e s p i r a t i o n ( M 0 2) a n d w e t w e i g h t T he relations between routine M 0 2 a n d wet weight for Palaemon adspersus (n = 16) and for Crangon crangon (n = 12) during day-time are shown in Fig. 1. 2 .0 . 1.5. 1.0 . 'a 0 .5 . E O •2 100 Oxygen consum ption m easurem ents (M O ,) w ere perform ed in a flow through system. The shrim p was placed in a resp iration ch am b er (8 cm long, 2.5 cm inner diam .) and sand o r a piece o f n e t was ad d ed as substrate. T he oxygen tension o f the w ater entering an d leaving th e cham b er w as m o n ito red co n tin u ­ ously by two R adiom eter E 5047 electrodes connected to tw o R adiom eter PH M 71b acid-base analysers a n d a G o erz S ervogor 220 recorder. T h e therm ostatted w ater was pum ped via a C ole-P alm er peristaltic pum p and tygon tubing was used. T he flow th ro u g h th e ch a m b er w as ad ju sted to give a M 0 2 o f around 15% o f the available oxygen, w h at norm ally m ean t a flow o f 1.2— 3.2 m l-m in- 1 , depending on the size o f the shrim p. C o n tro ls were run before and after each experim ent w ith su b strate in the ch am b er b u t w ithout the anim al. T he shrim p was allowed to recover from handling a n d to get used to the respiration cham b er fo r a couple o f h o u rs b efore th e a ctu a l experim ent started. A plastic sheet prevented the shrim p from receiving any visual stim uli from the surrounding. Each experim ent was run, unless otherw ise stated , for at least 24 hours. Lower, stable, PwO , were o b ta in e d b y blow ing N , th ro u g h the reservoir water. 400 1000 3000 m g w e t w e ig h t M A T E R IA L A N D M E T H O D S Crangon crangon and Palaemon adspersus were collected in August— Septem­ ber in the Rockilde-and Isefjord area, N orth ern Sealand, (S, 20%o; T, 15— 20°C) on sandy Zostera covered b o tto m s a t d epths o f 0.5— 1.5 m by m eans o f a sm all handoperated trawl. In the la b o ra to ry the shrim ps were stored (S, 20%o; T, 20°C) for at least 3— 4 days before experim entation. M ysids were provided as food. 200 Fig. I . Crangon crangon (o) a n d Palaem on adspersus ( • ) . R o u tin e o xygen co n su m p tio n rate as a fu n ctio n o f wet w eight (M O , = aW b) (log— log scale). S, 20%o; T , 20°C. The general expression M 0 2 = aW b relating respiration and weight was for Crangon M 0 2 = 0.19 W 0-78 (r = 0.80) an d for Palaemon M 0 2 = 0.28 W 0-85 (r = 0.84). The coefficient b is well within the range of the general coefficient for all crustaceans (b = 0.81; W inberg, 1950). The constant a gives a species difference o f 0.09 and this difference and the difference in b are responsible for the higher weight specific M 0 2 for Palaemon. As is seen from Fig. 1 Palaemon h ad a M O , 0.15— 0.3 ml 0 , g - l h -1 higher than for Crangon o f sim ilar w eight. D ie l n o r m o x ic M O, Palaemon show ed very sm all diel deviations from the 24-hour m ean M O , (Fig. 2) and thus no clear diel respiratory pattern was evident for this species. Crangon, on the other h and, (Fig. 2; 4 individual 24-h cycles chosen fo r each species, the rest showed the sam e p attern, n = 12 for Palaemon, n = 12 for Crangon) showed a clear diel respiratory rhytmicity where lowest M 0 2 occurred during the day (September— October: 8 to 17 o’clock). This M 0 2 was generally ca. 15% lower, in extrem e cases 40% lower, than the 24 h o u r m ean. T he highest M 0 2 w as consequently found during night-time w ith values up to 30% higher than the corresponding 24 h o u r mean. The shrim ps did m oult occasio­ nally during the norm oxic experim ents, increasing the M O , du rin g the ecdysis w ith around 16%. 71 70 C ra n g o n 30 9b 50 9b £ 7 ~ \ —i •S c 60 9b c» fi P O , 7 0 o/o Tim « of th a day 6 12 T im e of th e day Fig. 2. Crangon crangon a n d P alaem on adspersus. D iel v a ria tio n s in M O , fo r four specim ens o f each species u n d e r n o rm o x ic co n d itio n s. M O , expressed a s in teg rated p ercentage h o u rly d ev iatio n s from the 24 h o u r m ean. S, 20%o; T , 20°C. Fig. 3. Crangon crangon. E xam ples o f diel v ariatio n s in M O , u n d e r hypoxic con d itio n s ( % sa tu ra tio n ). xMO, expressed as in teg rated percentage h o u riy d ev iatio n s fro m the 24 h o u r m ean. S, 20%o; T , 20°C. D ie l h y p o x ic M O, A t a w ater oxygen sa tu ra tio n (Pw0 2) o f less th a n 70% , the diel respiratory pattern o f Crangon was d isturbed an d only m inor deviations from the 24 h o u r m ean occurred (Fig. 3). A covariance analysis also show ed th a t the 24 h o u r m ean in P 20 , 70, 50, and 35% sa tu ra tio n was higher th an the corresponding norm oxic 24 h o u r m ean M 0 2 (p < 0.01). In P w0 2 70% M 0 2 increase was 10 to 50% (from for instance 0.25 to 0.37 ml 0 2g -1 h - * for a Crangon of 0.56 g w.w.). In Pw0 2 50% the increase was betw een 20 to 90% (from for instance 0.26 to 0.49 ml 0 2g - 1 h -1 fo r a Crangon o f 0.47 g w.w.) an d in P w0 2 30 to 35% it was 16 to 50% o f the 24 h o u r m ean norm oxic M O ,. T his M O , change corresponds to the change found earlier w hen Crangon changes its activity level from ro u ti­ ne to swim m ing (H agerm an an d Szaniaw ska, 1986). U nder hypoxic conditions longer th an 24 h o u rs (up to 72 hours) M 0 2 rem ained at the sam e level as during the first diel period. M o u ltin g did n o t occur during the hypoxia experi­ ments. M 0 2 u n d e r h y p o x i a ( d e f i n i t i o n o f th e P J T he possibility to m ain tain M O , independent o f P w0 2 w as tested in a series o f short-term experim ents w here the Pw0 2 was low ered 5— 10% per hour. The percentage change from th e n orm oxic M 0 2 fo r th e tw o shrim p species are show n in Fig. 4. Both Crangon an d Palaemon show ed a considerable ability to co n tro l th eir resp iratio n irrespective o f the PwO ,, Crangon dow n to a Pw0 2 o f © s % P, 02, **> Fig. 4. Crangon crangon (o) a n d Palaemon adspersus (•). R elative changes in ro u tin e M O , w ith decreasin g oxygen ten sio n o f th e w ater. T he big half-filled d o t a t P wO , 100% indicates th e relativ e M 0 2 for settled anim als. S, 20%o; T, 20°C. 20% , Palaemon dow n to a P w0 2 o f 30% . This ability seem ed independent o f size, even if, o f course, the M O , varied according to the size o f the individual. Both Crangon an d Palaemon show ed an increase in M 0 2 w hen P w0 2 decreased from norm oxia. In Fig. 4 this increase is n o t so evident, because in these short-term experi­ m ents the specim ens were n o t allow ed to settle dow n long enough in the respi ration cham ber. Settled anim als have a respiration ca. 25— 30% low er th a n non-settled anim als (H agerm an an d Szaniawska, 1986). T hus the starting point in Fig. 4 a t PwO , 100% should be placed lower for settled anim als w hich w ould m ake th e hypoxia M 0 2 increase evident. 73 This increase occurred for Palaem on in the Pw0 2 80— 30% , for Crangon in the P w0 2 50— 30% . F o r Crangon this Pw0 2 corresponds to the em ersion res­ ponse (Hagerman and. Szaniawska, 1986) and for Palaemon to the range where an increased locom otory activity has been noted (H agerm an an d W eber, 1981; von Oertzen, 1979). D IS C U S S IO N In the present w ork it w as fo u n d th a t Palaemon adspersus always h ad a higher M 0 2 than sim ilar sized Crangon crangon. In n atu re both species are subjected to roughly sim ilar variations in the environm ental conditions (S, T, O), b u t inhabit different biotopes. T he burying Crangon alw ays is associated w ith sandy bottom s while Palaemon inhabits algae an d plants and thus does not have the ability to bury in a su bstrate. Bridges a n d B rand (1980) n o te d general­ ly low er M O , in burrow ing crustaceans com pared to non-burrow ing species. T his is probably also valid fo r o th er groups, for instance de W ilde (1973) found reduced M O , in the b uried bivalve M acom a com pared to epifaunal bivalves. R eduction in M 0 2 has also been noted intraspecific in buried com pa­ red to non-buried horseshoe crab s (Johansen a n d Petersen, 1975) a n d in buried/non-buried Nephrops norvegicus (H agerm an and U glow , 1985) and recent­ ly in Mesidoihea entomon (H agerm an a n d Szaniaw ska, in prep.). A typical routine respiratory level fo r interm oult Crangon (w.w. 0.25 and 1.1 g) und er norm oxic co nditions are 0.9 an d 0.2 m l 0 2g - I h -1 in the present investigation. E arlier w o rk o n th e resp iratory rates o f Crangon has show n values slightly higher th an those found here (H agerm an, 1970) o r in the same range (van D o n k a n d de W ilde, 1981). T he differences are often caused by the different techniques used, fo r instance H agerm an (1970) used a closed respira­ tory system and the experim ents were short-term (a couple o f hours) where handling and o th er types o f stress caused a respiration higher th an th a t show ed by an anim al adap ted to a long term experim ent, preferably not less th an 24 hours. It has been show n also by v o n O ertzen (1975) a n d by K ristensen (1983) th a t the M 0 2 for Gammarus and and fo r Nereis were m uch higher in short-term th an in long-term experim ents. In this connection the necessity o f a co r­ rect substratum m ust be stressed if a reliable value o f M 0 2 is to be obtained. If Crangon has no suitable substrate, in n atu re corresponding to displacem ent to a rocky o r h ard substrate, th e diel lo co m o to ry rhythm icity breaks dow n (H a­ germ an, 1970) and the respiratory ra te increases to 1.6 an d 0.65 ml O , g - 1 h -1 fo r th e specim ens m entioned above. R eg n au lt an d L agardère (1983) observed th a t an increased noise level (co m p ared to the b ackground noise always prevai­ ling a t sea) increased the m etabolic rate in Crangon w hen m easured both as am m onia excretion and as oxygen consum ption. A com m on response to all kinds o f disturbancies is certainly a m odification o f the activity level an d rhyth­ micity resulting in an increased M 0 2. Typical routine M O , for Palaemon adspersus in the present investigation were (wet weight 0.7, 1.0 and 2.1 g) 0.65, 0.41 and 0.13 ml 0 2g -1 h -1 un d er normoxic conditions. These values can be com pared to earlier findings o f M 0 2 of 0.15 for an individual o f 2.5 g w et w eight (H agerm an and W eber, 1981) and 1.35 pi 0 2g D W _1h _1 as found by von O ertzen (1984) u n d er sim ilar environ­ mental conditions. In Crangon the diel norm oxic M O , can be correlated to th e diel locom oto­ ry pattern (H agerm an, 1970), i.e. M 0 2 shows peaks during the same diel pe­ riods as Crangon is active. Crangon is a voracious predator, feeding m ainly ju st after daw n an d before dusk (Pihl a n d R osenberg, 1984). T he locom otory acti­ vity of Crangon is m ainly influenced by exogenous factors (H agerm an, 1970) and as the m etabolic cost o f sw im m ing is low (H agerm an and Szaniawska, 1986) the noted respiratory rhythm icity is probably endogenous in origin, ref­ lecting digestive and endocrine processes in the animal. F o r Palaemon adspersus the absence o f a pronounced diel rhythm icity will, despite a nocturnal locom otory activity (H agerm an and 0 s tr u p , 1980) reflect endogenous processes at, how ever, a higher rate th a t in Crangon. The latter can in the respiration cham ber bury in the sand, while Palaemon always will be more exposed to external stim uli an d thus keeps its m etabolic state at a m ore vigilant level. Sm it (1965) noted in goldfish an increased M O z th a t was not reflected in activity changes an d H alcrow and Boyd (1967) show ed that exci­ ted, but not m oving, Gammarus had a higher M 0 2. In addition m easurem ents of heart rate has show n a large excitem ent dependent variability (Dyer and Uglow, 1978) in shrim ps an d crabs an d these authors also show ed th at heart and ventilatory rates, an d thus M 0 2, decreased when specim ens buried. It is now generally accepted th a t m ost crustaceans th a t in nature m ight be exposed to v ariation in external PwO , have developed an ability to m aintain respiratory independence during hypoxia. Such an ability is also found in som e molluscs where T aylor and B rand (1975) found an increase in the ability o f bivalves to m aintain oxygen independence w ith increasing size during hypoxia. Fam m e and K ofoed (1980) noted th at the M O , of M ytilus to a certain extent was independent o f the Pw0 2. The PwO , where oxygen consum ption independence no longer can be m ain­ tained is usually defined as the so-called Pc (Newell, 1979; H erreid, 1980). In the present investigation the M 0 2 o f Palaemon and Crangon rose during prog­ ressive hypoxia, specially w hen a P w0 2 o f ca 45— 60 to rr was reached. T his is interpreted as an increase in the activity w hen the anim al perceives an d /o r reacts to the decreasing Pw0 2 a ro u n d 75— 60 torr. Below this the M O , is still high due to the stress caused by the still decreasing Pw0 2. T he Pc, as defined above, is for Crangon obviously a t a very low Pw0 2 (ca 30 to rr). How ever, this point reflects only the PwO , w here oxygen independence can no longer be m aintained, i.e. where the active M 0 2 is decreasing. O xygen supply to the tissues for routine/basal m etabolism is still adequate and the P c is in this sense thus n o t critical as the anim al can sustain these conditions for extended pe- nods. However, when the oxygen supply fo r the basic m etabolic needs is distur­ bed, i.e. when anaerobic m etabolism is initiated, a real critical p o int („P,actate” ) is reached. This level is ca 15 to rr in Crangon (H agerm an and Szaniawska, 1986) where, as a result o f an aerobiosis, lactate is beginning to accum ulate. In Crangon, a species show n to be to leran t to hypoxia, the trad itio n al Pc and the p oint where anaerobic m etabolism accelerates,are very close to each o ther but there is an evident difference in the level o f M O r H ow ever, under in ap p ro p ria­ te experim ental conditions o r w ith d isturbed anim als the traditional Pc will certainly m ove upw ards (H erreid, 1979; B utler et al., 1978; Dali, 1986). A nalo­ gically to this the Pw0 2 for the trad itio n al P c in Palaemon was ca.45 to rr while the level where an anaerobic m etabolism was found to increase was 30 torr. Both values are higher th a n for Crangon but well in agreem ent with the ecology of the species. REFERENCES Bridges, C. R ., B rand, A . R. (1980). T h e effect o f h y p o x ia o n oxygen c o n su m p tio n a n d blood lactate levels o f som e m arin e cru stace a. Com p. Biochem . P hysiol. 65A: 399— 409. B utler. P. J., T ay lor, E. W., M c M a h o n , B. R. (1978). R e sp ira to ry a n d circu lato ry changes in the lo b ster (H om arus vulgaris) d u rin g lo n g term ex p o su re to m o d e ra te hypoxia. J. exp. Biol. 73: 131— 146. D ali, W . (1986). E stim atio n o f ro u tin e m etab o lic ra te in a p en aeid p raw n . Penaeus esculentus H as well. J. exp. m ar. Biol. Eco I. 86: 57— 74. D o n k , E. van, W ilde, P. A . W . J., de (1981). O xygen c o n su m p tio n a n d m otile activity o f th e brow n sh rim p Crangon crangon related to te m p e ra tu re a n d b o d y size. N e th . J. Sea R es. 15: 54— 64. D yer, M . F ., U glow , R . F. (1978). H e a rt a n d sc a p h o g n a th ite b e a t b e h a v io u r in lab o rato ry -h eld Crangon crangon (L.). J. exp. m ar. Biol. Ecol. 32: 209— 218. F am in e, P., K o fo ed , L. H . (1980). T h e v en tila to ry c u rre n t a n d cten id ial fu n ctio n related to oxygen u p ta k e in declining oxygen ten sio n by th e m ussel M y tilu s edulis. L . Comp. Biochem. Physiol. 66A: 161— 171. H ag erm an , L. (1970). L o co m o to ry activity p a tte rn s o f Crangon vulgaris (F a b r.) (C ru stacea , N a ta ­ n tia). Ophelia 8: 255— 266. H ag erm an , L ., 0 s tr u p , J. (1980). S easo n al a n d diel activity v a ria tio n s in the shrim p Palaemon adspersus R a th k e from a b rack ish , n o n -tid a l are a . M ar. Ecol. Prog. Ser. 2: 329— 335. H ag erm an , L ., W eber, R . (1981). R e sp ira to ry rate, h em o ly m p h oxygen tension a n d hem ocyanin levels in the shrim p Palaemon adspersus R a th k e . J. exp. m ar. B iol. Ecol. 54: 13— 20. H ag erm an , L ., U glow , R . F . (1985). E ffects o f h y p o x ia on the re sp ira to ry a n d circu lato ry regula­ tio n o f Nephrops norvegicus. M ar. B iol. 87: 273— 278. H ag erm an , L ., S zaniaw ska, A . (1986). B eh av io u r, to leran ce a n d a n a e ro b ic m etabolism under hy p o x ia in th e b rack ish w a te r shrim p C rangon crangon L . M a r. Ecol. Prog. Ser.. 34: 125— 132. H alcrow , K . R., Boyd, C. M . (1967). T he oxygen co n su m p tio n a n d sw im m ing activity o f the am phip o d G am m arus oceanicus a t d ifferen t te m p e ra tu re s. Comp. B iochem . P hysiol. 23A: 233— 242. H erreid , C . F. (1980). H y p o x ia in in v erteb rates. Com p. Biochem . P hysiol. 67A: 311— 320. Jo h a n sen , K ., P etersen, J . A. (1975). R e sp ira to ry a d a p ta tio n s in L im ulus polyphem us. In: V em berg (ed.). Ecophysiology o f estuariae organism s. U niv. S o u th C a ro lin a Press, C olum bia, p. 129— 145. K risten sen , E. (1983). V entilation a n d oxygen u p ta k e by th ree species o f N ereis (A nnelida: Poly­ ch aeta). I. E ffect o f h ypoxia. M ar. Ecol. Prog. Ser. 12: 289— 297. M iljostyrelsen, (1984). Iltsvind og fis k e d e d i 1981. O m fang og àrsager. C o p en h ag en , M inistry o f E n v iro n m e n ta l P ro tectio n . NewelL R. C. (1979). Biology of in tertid al anim als. M arine Ecological Surveys L td , F av ersh am . Oertzen, J.-A . von (1975). L ong-term c o n tin o u s resp iratio n m easurem ents as a p recau tio n f o r th e assessm ent o f secondary p ro d u c tio n . M eren tu tk. Ju lk. Havsf. S kr. 239: 213— 221. Oertzen, J.-A . von (1979). Versuch einer kausalekologischen Leistungsanalyse an brackwasserleben­ den Tieren. Thesis. 188 p p ., W ilhelm -P ieck-U niversität R ostock. O ertzen, J.-A . v o n (1984a). Influence o f stead y -state an d fluctuating salinities o n th e oxygen consum ption a n d activity o f so m e b rack ish w ater shrim ps a n d fishes. J. exp . m ar. B iol. Ecol. 80: 29— 46. O ertzen, J.-A . von (1984b). O pen an d closed system — their suitability fo r fu n ctio n al resp iratio n m easurem ents. Lim nologica (Berlin) 15: 541— 545. Pihl, L ., R osenberg, R . (1984). F o o d selectio n a n d c o n su m p tio n o f th e sh rim p Crangon crangon in som e shallow m arin e areas in w estern Sw eden. M a r. Ecol. Prog. Ser. 15: 159— 168. R egnauit, M ., L agardière, J.-P . (1983). E ffects o f am b ien t noise on the m etab o lic level o f Crangon crangon. M a r. Ecol. Prog. S er. 15: 159— 168. Smit, H . (1965). Som e experim ents on th e oxygen con su m p tio n o f goldfish (Carassius L.) in relation to sw im m ing speed. Can. J . Z o o l. 43: 623— 633. T aylor. A . C ., Brand. A. R. (1975). E ffects o f h y p o x ia an d body size on th e oxygen co n su m p tio n o f th e bivalve A rctica islandica L . J . exp. mar. Biol. Ecol. 19: 187— 196. W ilde, P . A . W . J . d e (1973). A c o n tin u o u s flow a p p a ra tu s fo r long term re c o rd in g o f pxygen u p tak e in burrow ing in v erteb rates, w ith som e rem ark s on the u p tak e in M acom a balthica. N eth. J. Sea R es. 6: 157— 162. W inberg, G . G . (1950). M etab o lic in ten sity a n d c ru stace an size. Z . Obshch. B iol. 11: 367— 380.