Estuaries and Coasts Vol. 30, No. 3, p. 451-458 June 2007 Detrital Subsidy to the Supratidal Zone Provides Feeding Habitat for Intertidal Crabs TYLER L. LEWIS a, MALTE MEWS ~, DENNIS E. ]ELINSKI s, a n d ~[ARTfN ZIMMER e'* G;.~m, fi~r Wildti/e Ecology, Simo~ Fraser Universit),, Bun~ab7, British Cd'~cmbia, VBA .1S6, Ca~nada "~"Zoo[o~isck~;s l'~astitut Lirtmolo~, Christiar>Albrechts-U~iversitdt Kid, OMzmr 40, D-24109, s Sc]zooZ ofE%zriro'~:~.er~t~z~S~'~.di#s, ()t~.ec~z's U~ziversi~), ~i~zgs~o%, O%mrio, KTL 3N6, Ca'~.ad~z ABSTRACT: Beach-east wl"ack of tam'hie origin is considered a spafiM subsidy to the maa-hle4en-emn-ial trallsifion zone. We fotmd lhat lhe x~'ack line on sm~d aald ga'aveI beaches of Vancouver Island was fi-eq~mnted by h~terlidaI purple shore crabs~ Hernig~tpsus nudus (Daua 1851 ) and densely colonized by d e ~ h i v o r o u s talitsrid ampbipods. A m p h i p o d s s p e n d the day bm'ied in sm~d and forage on beach w*aek ditring the night. H . nudus were f o u n d in supralidal ~'rack patches hnmediately after nightly high tides in field censuses, but s p e n t m o s t o f the day and ebb tides either s u b m e r g e d subtidally or tfidden u n d e r n e a t h h~tertidal rocks and boulders. I n feeding trials, intertidal shore crabs were capable o f pre)~ng on talitfid amphipods. We consider H . nudus an orrmivore feeding on both fresh and d e c a j n g macroalgae as well as a~mnM prey. Although riving s-upratidally, a m p h i p o d s were significantly p r e f e r r e d over intertidal fitlorine snails by foraging shore mabs. Handling time of a m p h i p o d s was significantly shorter than for littorine snails. While a m p h i p o d s h a d a r e d u c e d lisk of pl~edation by H. nut/us w h e n buried in the sand, foraging t m d e m e a t h wrack patches did n o t reduce predation pressm'e on maaphipods by s h o r e crabs. Rates of a m p h i p o d c o n s u m p t i o n by shore crabs were higher at darkness than da)light. In addition to an apparent day-night rhylhrn, tidal height and lime elapsed since previous high tide h a d a significan~ influence on s h o r e crab density within the vcrack. We conclude thai beach-cast vcrack a ~ as a spatial subsidy by virtue o f providing a valuable f o o d source to talitrid amphipods, which are in turn c o n s u m e d by shore crabs thai ride the nightly high tide into supratidal wrack patches to reduce the risk o f passing bare s a n d on their way to a feeding habitat rich in valuable prey. predators, such as birds or small maritime m a m mals. I n v e r t e b r a t e predators relying on contact p e r c e p t i o n for prey capture, rather than visual cues (e.g., crabs or beetles), may be effective predators of a m p h i p o d s in wrack patches, having access to ainphipods during nocturnal hours, when amphipods are most active (Richards 1983). In a series of studies on detrital subsidies to b e a c h e s in g a r k l e y S o u n d (British C o l u m b i a , Canada), we observed dense populations of purple shore crabs (He,migrapszts ,~,udus) sheltered underneath high it~tertidal rocks within close proximity of wrack det?osizs in the supratidal beach zone, T o access these supratidal ~wack deposits as a potential f o o d source, H. ~z~d~s must leave ~heir s h e k e r and move u p the Beach platfbrm. T h e disadvantage of u n d e r t a k i n g this potentially dangerous travel may be counterbalal~ced by the advantages of using wrack as a vNuable feeding habitat. The relatively weak claws of the generalist H. ~.udt~s impose restrictions u p o n their ability to feed on some h~tertidal animal prey (Behrens Yamada and Boulding 1998), since most animal p r e y available in the intertidal zone, such as Littorina spp., are hard-shelled and require substantial claw strength or handling periods. Wrack deposits contain high densities of calorie-rich talitrid a m p h i p o d s (Gritfiths Intro duction Beach-cast deposits of macroalgae a n d seagrass, t e r m e d wrack, function as i m p o r t a n t spatial subsidies (Polis et al. 1997) of organic material to sand and cobble beaches, especially in terms os providing a rich {bod source tor a n u m b e r of consumers (Pennings et al. 2000; Dugan et al. 2003). Owing to their high location on the beach plattbrm, these beach-cast wrack deposits e x p e r i e n c e only very brief episodes of tidal inundation (cfi, Orr et at. 2005). Semiterrestrial a m p h i p o d s (Talitridae) are corfffrton detritivores in d e c o m p o s i n g wrack deposits, often occurring at high densities (Grif~iths et al. 1983; McLachlan 1985). While it is well k n o ~ l that talitrid amtphipods use wrack as a f o o d source (Grif~lt.hs et. al. 1983; Pennings et al. 2000), it remains an o p e n question whether ~,rack patches effectively serve as shelter f i o m potential predators (cs Buck et al. 2003), as is known to be the case for aquatic a m p h i p o d s (Norkko 1998; Vetter 1998; C o r o n a et al. 2000). Aanphipods resting a n d tbraging u n d e r n e a t h wrack patches would be h i d d e n f r o m visually-oriented * Corresponding author; tele: (+49) 431 880 4153; fax: (+49) 431 880 4747; e-mail: mzimmer@zoologie.uni-kieLde 9 2007 Estuarine Research Federation 451 452 T. L, Lewis et al. et al. 1983; Creswell 1994), which can be easilycrushed by the weak claws of H. ~udu.s, owing to their soft exoskeletons. Intertidal crabs are highly motile predators that exploit patches of high prey density; an attribute that permits exploitation of e p h e m e r a l p r e y patches (Behrens Yamada a n d Boulding 1996). Many crab species restrict feeding activity- to certain intertidal zones or periods of tidal inundation (Robles et al. 1989). Crabs residing within tile high intertidal zone experience reduced daih/ submersion time, significantly restricting the a m o u n t of tidally inu n d a t e d foraging time. Foraging activity of intertidal crabs m m also be highly d e p e n d e n t u p o n light levels (Dare arid Edwards 1981; Robles et at. 1989). Many crab species exhibit diel cycles of activity- with higher foraging activity- during night (Marsden a n d Dewa 1994), Increased activity during night may d a m p e n the risk of p r e d a t i o n by visual-based, diurnal predators such as birds, fish, and maritime m a m m a l s . This c o m b i n a t i o n of diel a n d tidal patterns may act in concert to regulate the daily foraging and activity- patterns of intertidal crabs. Despite the tbtct that H. ~udus are a m o n g the most a b u n d a n t intertidal crabs in coastal British Columbia, very limited information exists regarding their dietary habits a n d preferences, T h e y are described as generalist herbivores mainly feeding on diatoms, desmids, a n d green algae (Behrens Y a m a d a and Boulding 1998), b u t evidence of carnivory also exists (Dalziel and Boulding 2005). To shed m o r e light on the feeding behavior a n d t r o p h i c status of such an a b u n d a n t generalist feeder, we examine the m o v e m e n t of H. nudus to wrack patches, as well as their role as potential predators in these patches. We aim to prove that H. ~v~d,~s are omnivorous ~eeders and elucidate potential animal prey items, determine if H. nudus access supratidal ~Tack deposits, a n d if so, u n d e r which tidal and diel circumstances, a n d test the hypothesis that snpratidal talitrid a m p h i p o d s can be used as a f o o d source by- H. nudus, and are even p r e f e r r e d over other potential t b o d items of the intertidal area. nudes reside within the rock fields. During each tidal cycle, a supratidal b a n d of wrack is deposited a m o n g the rocks mad along the entire length of the beach. A rich c o m m u n i t y of talitrid a m p h i p o d s is t 0 u n d a m o n g the x~ack, with Megalorchestia pugettensis (Dana 1853) a n d Traskorchestia traskiana (Stimpson 1857) being tile most c o m m o n amphip o d species. Night Trar~sects Beach-cast uTack was sampled [br the presence ol H. nudus on the nights of August 8 (4 d alter n e a p tide), 1B, a n d 22 (5 d before spring tide), 2003. T h r e e transects were sampled p e r night, the survey of each being separated by a 2-h interval. T h e first transect p e r night coincided with the time of either the slack high or slack low tide after sunset and the overall sampling time (6 h) covered the entire interval of flood or ebb. Sample transects were established along the course of the wrack line. Quadrats of 0.5 x 0.5 m 2 were placed on the wrack line a n d all H. nudus within the quadrat were counted. Transect distance of 0 m was defined as the p o i n t where the beach wrack line m e t the b o r d e r i n g rock field. T h e first quadrat (-- 1 m) was randomly placed between 0.B and 1.5 m distance f~om ~he rock field; all s~bsequent quadrats were placed evmT 3 m along the wrack 1inc. Since an u n d i s t u r b e d wrack line was essential for additional studies in a n o t h e r context, we were unable to d e t e r m i n e the wrack by means of mass p e r area; p e r c e n t cover of ~-ack within qnadrat a n d minim u m distance of rock shelter was r e c o r d e d for each quadrat. T h e wrack within the rock field, where it is deposited more patchily a n d in larger amounts, was also sampled by means o f 5 quadrats that were r a n d o m l y placed within the area of wrack deposition in the rock field. Percent cover of x.~ack and n u m b e r of crabs were r e c o r d e d for each qnadrat. M i n i m u m distance to potential shelter within the rock field was defined as 0 m. Da), Trar~sects Materials and Methods FIELD SAMPLING Study Site Field studies were c o n d u c t e d on a small, protected sand ~ d gravel b e a c h on the northeast c o r n e r of Edward King Island (48~ 125017 , 18.86"W), Barkley Sound, off ~he west coast of Vancouver Island (British Columbia, Canada). T h e study beach is approximately 75 m long and f}inged o n each side by large rock fields c o m p o s e d of cobbles mad boulders. Dense populations of H. Daytime sampling ~bllowed the m e t h o d s used tbr nocturnal sampling, A total of 4 diurnal transects were sampled o n August 13 (9 d after n e a p tide) a n d 19 (8 d before spring tide), 2003. Because shore crabs are typically m o r e active during diurnal high tides (Williams 1991; Marsdon a n d Dewa 1994), diurnal sampling was p e r f o r m e d at high tides to maximize likelihood of finding H. ,mtd~s within wrack. This p r o c e d u r e biased our results towards higher crab densities during da}r so that lower diurnal crab densities, relative to night, can be considered conservative. Intertidal Crabs in Supratidal Subsidy LABORATORY EXPERIMENTS Predators Laborato~ T experiments were c o n d u c t e d at the nearby Bamfield Marine Sciences Centre. H. nudus of various size classes were collected by hand from u n d e r n e a t h cobbles near the study site on Edward King Island. Crabs were held in seawater tanks with a constant flow of fresh seawater and a b u n d a n t macroalgae ( F u ~ s spp). Only crabs that had spent at least 24 h in the laboratory were used in experiments. Randomly chosen crabs were sexed, and the carapace width and the height of the p r o p o d i t e os the right chela were measured to the nearest millimeter (cf., Buck et al. 2003) betore they were used in the experiments. Since claw size is related to fbod choice, we aimed at c o m p a r i n g H. ~udus, which we c o n s i d e r an omnivore, with a n o t h e r grapsid crab, A r~ases cinereum, which has recently been shown to exhibit omnivorous feeding beha~4or (Buck et al. 2003). Predation Trials Predation trials with H. nudus were c o n d u c t e d in dry plastic tanks (30 • 17 cm~). One randomly selected crab was placed in the tank along with 10 talitrid amphipods and 10 individuals of one of three littorine snails: Littorina sitka~'~a, L. scutulata, or L, subrotundata. Each Littorb~a sp. was used in separate experiments, and a total of five trials were pe~Ibrmed per species; no sheker was offered to prey organisms. Crabs and prey were lett in darkness for 12 h per predation trial, and r e m N n i n g prey items were c o u n t e d at the conclusion of each trial. Dry- tanks mimicked emersion at low tide and prevented Littorina spp. ti-om climbing out of reach of crabs. Littorina spp. differ in shell thickness, with L. sitkana and L. subrotundata being lighter shelled (Dalziel personal c o m m u n i c a t i o n ) . Only small Littorina (< 7 ram) were used to f~acilitate handling and crushing. Previous feeding eN)eriments have d o c u m e n t e d H. nudus predation on L. sitkana (Behrens Yamada and Boulding 1998). Additional teeding experiments were c o n d u c t e d with L. sitkana as the only prey item. O n e randomly selected crab was placed in a tank with 10 L. sitkana. Five trials were c o n d u c t e d for this experiment, using the same m e t h o d as for the prey preference experiments. Simultaneously, teeding trials (n - 10) in waterfilled, lid-sealed plastic tanks (30 • 17 cm c) with a continuous flow of fiesh seawater yielded comparative data o n overnight c o n s u m p t i o n of different subtidal and intertidal tbod items that enabled us to decide whether 14. nudus acts as a detritivore, an herbivore, a carnivore, or an o m n i v o r e when submerged. For this, cobbles with kno+t~+, numbers 453 of barnacles (mixed genera), 10 snails (L. sitkana), and knowa amounts of fresh and detrital Fucus cf, gardneri were placed in the tank betore a randomly chosen crab was added. Aficer 12 h, the numbers of barnacles m)d snails were counted, and algae were oven dried (24 h, 60~ and weighed. The dry mass of the initial a m o u n t of algae was determined on the basis o f a fl-esh mass:dry mass ratio fbr fi-esh and detrital Fucus (n - 15, each), ~Nhen several types of t o o d are offered silr, ultaneously, c o n s u m p t i o n of one cannot be assumed to be i n d e p e n d e n t of c o n s u m p t i o n of the others. To avoid f~dlacies in statistical analyses of preference tests (cf,, Peterson and Renaud 1989; Roa 1992; Manly 1993), all preference tests were statistically analyzed t h r o u g h randomization of data by using resampling statistics with 9999 iterations as implem e n t e d in the sottware poptools ( h t t p : / / w ~ . c s e . c s i r o . a u / p o p t o o l s / ) , since this approach incorporates such interdependencies. Fisher (1951) introd u c e d permutation tests as a theoretical a r g u m e n t supporting Student's t-test, but this approach is also valuable fbr statistical tests in its o ~ l right (Bfirlocher 1999). The repeated resampling of experimental data gen.erates sets of artificial data. Instead of listing all possible arrangements, r a n d o m arrangements of the original data are generated. By increasing the n u m b e r of iterations, it can be decided whether the original experimental data deviate f)om a r a n d o m distribution that would t?e expected if no preference was observed. Protection Jko~n Predatio~ Eftects of potential shelter on supratidal predatorprey interactions were tested in trials with H. nudus and a m p h i p o d prey overnight (n - 10, each). A single randomly chosen crab was placed in a plastic tank (30 • 17 cm 2) that was either bare, filled with 4 cm of moist sand, or filled with sand and a small patch of wrack that covered approximately 50% of the sand surfkce area. Prior to introducing the crab, 10 m e d i u m sized taiitrid amphipods were given time to acclimatize in the tank for 1 h. At the end of the experiment, crabs were removed, and the remaining amphipods were counted. To compare nocturnal versus diurnal supratidal predation, plastic tanks (30 X 17 cm ~) were filled with 4 cm of moist sand. A circular bowl (10 cm diameter) containing seawater was sunk into the sand and a small rock shelter was constructed within the water bowl. Crabs were aisle to move fleely between the water bowl and sand. A small pile of wrack was placed in the tank opposite the water bowl. Ten mediuln-sized talitrid amphipods were placed into the wrack pile. O n e randomly selected H. nudus (n - 5) was placed in the water bowl and either studied during daytime at 12 h of light or 454 T.L. Lewis et al. 14 100 - 140 120 80- r 10~ oo 60- 8 ,.,., !~ 40 "ID 20- 0 100 females 8O ~2r e'~ 6 c~ 4 ,~ 2 B ._~ "10 13 "16 "19 22 25 28 31 34 37 40 43 46 D i s t a n c e f r o m r o c k field (m) Fig. 1. Wrack cover (bars) and density of He~nig~apsus~*udizs (dots) underneath wrack along transects with increasing distance from shelter in an adjacent rock field. Crab density is not correlated with percent cover of wrack, but with distance from the rock shelter. Data are median -- median absolute deviation (n 9 3 transects at 3 dates, each). o v e r n i g h t at 12 h o f dark. A m p h i p o d s r e m a i n i n g in t h e t a n k a f t e r 12 h w e r e c o u n t e d . 6O E 4O 20 .__. o_ m 0 3 E 120 t- T o c o m p a r e t h e t i m e n e e d e d to h a n d l e a caugh~ a m p h i p o d with t h e t i m e n e e d e d for a h a r d - s h e l l e d snail ( B e h r e n s 'l<~mada a n d B o u l d i n g 1998), we measured handling time of medium-sized amphip o d s f o r H. nudus. O n e r a n d o m l y s e l e c t e d c r a b (n - 10) was p l a c e d in a dry, plastic tank with 10 a m p h i p o d s . Crabs were w a t c h e d by an o b s e r v e r u n d e r r e d l i g h t to m i n i m i z e o b s e r v e r d i s t u r b a n c e o n c r a b b e h a v i o r . H a n d l i n g t i m e was m e a s u r e d f o r o n l y tire first a m p h i p o d c a p t u r e d , b e g i n n i n g w h e n the crab caught the amphipod and ending when the entire amphipod had been consumed. Results Daytime transects revealed an almost complete a b s e n c e o f H. nudus f r o m b e a c h wrack; in 80 d i u r n a l q u a d r a t s s a m p l e d , o n l y f o u r indix4duals were f o u n d (0.05 c r a b s p e r q u a d r a t ) versus 97 indit4duals ~ b u n d at n i g h t ( n - 189 q u a d r a t s : 0.5 crabs p e r q u a d r a t ) . T h e d i s t r i b u t i o n o f H- ~z~d'~t,sat n i g h t l y h i g h tides was o n l y mm-ginalIy i n f l u e n c e d by t h e p e r c e n t c o v e r o f u a a c k (Fig. 1; S p e a r m a n rs 0.409, n - 17, p > 0.06), b u t was s t r o n g l y i n f l u e n c e d b y b o t h t h e d i s t a n c e iS'ore t h e r o c k s h e l t e r (rs - 0.803, n - 17, p < 0.001) a n d tidal h e i g h t ( l i n e a r r e g r e s s i o n : r 2 - 0.47, n - 9, p < 0.05). O b s e r v a t i o n s in t h e field, b o t h p r i o r to a n d b e t w e e n t r a n s e c t s a m p l i n g s , i n d i c a t e d t h a t initial m o v e m e n t o f H. nz~dus i n t o t h e w r a c k line c o i n c i d e d with t h e t i m e s o f h i g h t i d e m a x i m a . A t h i g h tide, t h e water comes into close contact or even resnspends a~ males 100 t~ r 8O 4O 20 0 Seaweed Prey Handling Time . r 0 Wrack Barnacles Snails Fig. 2. Feeding preferences of submerged H,'mi~z*psus ,~tudus when 9 offered different food items simuhaneousl), indicating Jmt shor'e crabs may act as ornnivores. Females and males differ in fl:eh" rates of barnacle consmnption. Data are median + median absoktte deviation (n 9), p r e v i o u s l y d e p o s i t e d xwack ( O r r et al, 2005). T h e density- o f H. nudus within t h e v a a c k d e c r e a s e d s i g n i f i c a n t l y with t i m e since p r e v i o u s h i g h t i d e m a x i m a (i.e., t i m e since tide last t r a n s p o r t e d crabs to w r a c k d e p o s i t s ; l i n e a r r e g r e s s i o n : r 2 - 0.71, n 9, p < 0.005). D u r i n g l a b o r a t o r y p r e d a t i o n trials, s u b m e r g e d H. nudus f e d o n s i m i l a r a m o u n t s o f f r e s h a n d b e a c h t o s s e d (wrack) Fucussp. (Fig. 9; Utest: p > 0.8), a n d p r e t e r r e d p r e y i n g o n b a r n a c l e s (mLxed g e n e r a ) o v e r p r e y i n g o n snails (L. sitkana; U test: p < 0.001). T h e absence of a preference between flesh and wracked s e a w e e d suggests t h a t t h e p r e s e n c e o f d e c o m p o s i n g s e a w e e d a l o n e d o e s n o t e x p l a i n H. ,,t;~dus p r e s e n c e in b e a c h - c a s t wrack; b o t h f i e s h a n d w r a c k e d m a c r o a l g a e are a b u n d a n t h~ t h e i n t e r t i d a l zone. The consumption of both seaweed and barnacles c o n f i r m s a n o m n i v o r o u s diet {0r H. ~udus, W h e n g i v e n a c h o i c e b e t w e e n a m p h i p o d s a n d snails (Littorina s p p . ) , e m e r g e d H. nudus always s t r o n g l y p r e f e r r e d a m p h i p o d s , i r r e s p e c t i v e o f Littorina species (Fig. 3; Utest: p < 0.001). I n f e e d i n g trials with L. sitkana as t h e sole p r e y c h o i c e , no snails were c o n s u m e d at all ( d a t a n o t s h o w n ) . I n b o t h sexes o f H. ~udus; claw size i n c r e a s e d l i n e a r l y with c a r a p a c e w i d t h (males: r 2 - 0.749, s l o p e - 0.37 + 0.04, n - 24, p < 0.0001; females: r 2 - 0.664, s l o p e - 0.25 -+ 0.04, n - 25, p < 0.0001), Intertidal Crabs in Supratidal Subsidy 455 100 10 80 02 Q) 4,-* 9 o~ 6 03 "13 O 60 C1. >., n 40 4 E < 20 2 0 0 ,T, M p L. sit. I~ p L scut. M p. L, sub. Fig. 3. Feeditag p r e f e r e n c e o f e m e r g e d Hemig'~ap~u~ ~ d ~ s w h e n offered talitrid a m p h i p o d s ([vL p. lgieg~o';~,/~esti~ p~g~te~sis) a n d different species o f Iittorine snails (L. sit = 5it~o~r*{z sit!{ana, L. scut - L. scutugata, L. sub - L. su&otundata) simultaneously, indicating that s o f t b o d i e d a m p h i p o d s are preferred over hard-shelled snails. Data are m e d i a n • m e d i a n absol~tte deviatiol-~ (~s - 9). but males had bigger claws than females of the same size (ANCO\:%: p < 0.00I). T h e difference increased ~dth increasing body size, i.e., the regression coefficients were signilicantly different (p < 0.01}, indicating that with increasing size tomes develop disproportionately larger claws than do females. Males differed froln females in that thev consnmed fewer barnacles than females, perhaps because the smaller female claws facilitate pulling out the barnacle soft body from the hard carapace (Mews and Zimmer personal obselwation). Females (9 -+ 1) and males (9 _+ 1) did not differ from each other in how many amphipods (M. p~,~r were consumed within the time provided during feeding tests (U test: p > 0.%. 100 q- t'- 80 o~ 60 O Q.. '- 40 E 20 0 w/o shelter w/sand w/sand 9 wrack Fig. 4. Effect of s a n d ( w / s a n d ) a n d additional wrack (~v..~ sated + wrack) o n c o n s u m p t i o n of a m p h i p o d s (Megalor~hes~a p'ug~t~e*zs/s) by Hemigrapsus mzdus in c o m p a r i s o n to shelter free trials (w/'o shelter), indicating that sand, b u t n o t wrack, provides protection f r o m p r e d a t i o n by f o r a g i n g crabs. Data are m e d i a n -- mediat~ absolute deviation (n - 9). Fig~ 5. I I Day Night Daytime a n d o v e r n i g h t c o n s u m p t i o n of a m p h i p o d s ( 3,'Iegzzl~rches*ia pzzg'eih'~is) by Hemig'mps.us ,~zv,d,us, indicating Iligher consumptiolz rates d u r i n g night. Data a,'e m e d i a n + ntedian absolute de~{atiola (n - 9). Con:pared wifl~ sheher-free conn-ols, s.'.md significantly (,~NO\,q~k: p < 0.001) reduced predation on Meg~go~chestia by H. ~z~,d.~s (Fig. 4). Adding wrack only marginally resulted in a ch.'.~nged 5reqneilc.y of predation (ANOVA: p > 0.07), suggesting tl:at. wTack does not provide an effective sheher ii'om predation. H. nudus consumed significantly more talitrid amphipods at night than during day (Fig. 5; U test: p < 0.05), consistent with the observation of higher H. ~zudus abundance in the nocturnal field transects. From time of a m p h i p o d capture m complete consumption, H. nudus required 118 + 8 s. This handling time tbr amphipods is approximately five times faster than values reported for Littorina snails (Behrens Yamada and Boulding 1998}. Discussion T h e significant nunlbers of H. nudes within beach-cast wrack deposits during nightly high tides support our hypotheses that this intertidal crab may act as an omnivore and exits the water and travels up the beach gradient platform to forage underneath supratidal wrack patches rich in prey. Clear diel patterns of H. nudus accessing wrack were observed. Observations at night revealed obvious crab movements out o f the water and up tile exposed beach towards tile wrack line, while no crabs were observed moving or foraging out of the ,~vtter during the day. O f the four diurnal transects, only four H. nudus were f o u n d in tile wrack, indicating a 10-times lower density of e m e r g e d H. n.udus during the day than during night. These few H..nudus were buried u n d e r a deep pile o f wrack (ca. 25 cm) a m o n g tile rock field, quite possibly using the wrack primarily as shelter. A complete diurnal data set with regards m tidal level would be 45G T.L. Lewis et al. necessary- to draw m o r e firm conclusions, but o u r present data conservatively confirm the essential absence of H. n u d u s fl-om the supratidal wrack line during the day. Day and night simulated laboratory e x p e r i m e n t s p r o v i d e d g o o d evidence regarding diel activity patterns. H. ~ u d u s c o n s u m e d significantly m o r e a m p h i p o d s during simulated night than day-, a h h o u g h they were still active and foraging during simulated day, Although these e x p e r i m e n t s may indicate increased n o c t u r n a l activity, laboratory conditions are admittedly limited. Foraging crabs only had t o move short distances (ca, 15 cm) f r o m water to ~.~-ack and had no tid~ or crep~scwlar signals to cue movement. N o c t m n a l activity in b e a c h x~ack confers potential major advantages to H. ~ud~s, Nocturnally foraging crabs are hidden in darkness ~}om visually oriented terrestrial predators, and nighttime foraging coincides with maximal activity of talitrid arnphipods that s p e n d days mostly buried in sand (Richards 1983). W h e n given a choice, H. mtd,ts foraging o n land clearly p r e t e r r e d a m p h i p o d s over littorine snails, which are highly a b u n d a n t at the study site. Igittori,~a spp, occupy the intertidal z o n e a n d could b e e~t5ciently p r e y e d u p o n by crabs during times of tidal submersion, eliminating potentially dangerous foraging trips onto exposed flats. T h e handling time for an individual a I n p h i p o d (ca. 2 Inin) was m o r e t h a n 6 rain lower t h a n the h a n d l i n g time t o t littorine snails (ca. 500 s) as r e p o r t e d by Behrens Yamada a n d Boulding (1998). This time-energetic benefit may b e a major driving torce p r o m p t i n g H. ~ a d u s m o v e m e n t s to wrack deposits. W h e n submerged, ILl. ~zud*ts p r e f e r r e d feeding on barnacles or F u ~ s wrack, and to some extent on t}esh Fucus, rather than on littorine snails. :Mmther factor Mtiecting teeding behavior of crabs may be claw size (Behrens Yamada a n d Boulding 1998). Males of the grapsid crab, A. d,~ereum, have bi,,,,er claws than females (Buck et al. 2003). Male A. cb~er~,.u.m eat more snails than temales do, likely o~fing to their improved ability to crush shelled prey items. Both A. ~d~e~ez~zsexes .prefer amphi.pods and isopods over snails (Buck et al. 2003). Although male H. '~v~,.d,~,.shave biooer claws than females of the same size, feeding on talitrid a m p h i p o d s did not differ between sexes; preying ~ p o n barnacles even appears to be fi~cilitated by small claws. Allomet.ric differences between sexes likely have other reasons than sex-specific prey selection in ILl. *~udus and may simply be an evolutionary heritage rather than an adaptation to teeding habits. In addition to an a p p a r e n t day-night rhythm, tidal height and time elapsed since previous slack high tide a p p e a r to have the most significant it~luences o n crab density- within the wrack. T h e strong relationship between H. ~ u d u s density- a n d time elapsed since previous high tide suggests that H. nud,~s ride the high tide into the wrack line. We p r o p o s e that high tides contacting the wrack line may carry aqueous chemical signals ti-om decomposing wrack to s u b m e r g e d H. nudus, providing a chemical cue that initiates travel to the wrack, b u t this hypothesis awaits e x p e r i m e n t a l testing. Waiting for the slack high tide to access wrack would entirelyminimize the travel distance between wrack a n d water. Concerning which portion of the wrack line will be used, the distance t-ore rock shelter strongly dictates H. nud.~ts distribution. T h e propensity of H, ~x~.dus to remain close to s h e h e r in rock fields adjacent to the Beach could preclude t h e m f r o m wrack access at larger beaches or areas lacking p r o p e r rock shelter. This observauon could be an artit~ct of the study site, since a b u n d a n t wrack deposits abutted rock fields at the study site, potentially eliminating the n e e d for ILl. ~*tdus to stray tar li-om their daytime habitat. It is unlikely that the m o v e m e n t of ILl. ~zudus to wrack patches is fi)r shelter purposes alone, since adequate shelter is available u n d e r rocks in the intertidal zone, and reaching the wrack line might require m o v e m e n t over exposed areas of the beach. T h e presence of H, ~ u d u s within the wrack does not necessarily m e a n that a m p h i p o d s are being used as a t b o d source. The wrack itself may b e fed u p o n (Griffiths et at. 1983), possibly being the main attractant for ~oraging crabs, while the occasional capture a n d ingestion of a m p h i p o d s within wrack may- b e a secondary reason for m o v e m e n t into the wrack. We tilled this out, since H. n u d u s did not show any p r e f e r e n c e for f e e d i n g o n wrack in laboratory trials, but did exhibit a cleat- p r e f e r e n c e for feeding on a m p h i p o d s rather than other available prey. Owing to substantial a m p h i p o d densities (Griftiths et at. 198a; McLachlan 1985), shore crabs are likely e n c o u n t e r i n g n u m e r o u s a m p h i p o d s when in the wrack, These e n c o u n t e r s are potentially profitable feeding opportunities that may influence the decision of an indi~r H. ,~z~.~.&~.sto access the wrack, and we hold that high densities of amphipods in supratidal ~.~.~ack patches render t h e m an attractive prey fbr H. ~xt~d-u.s.T h e feeding habitat of talitrid a m p h i p o d s is also a feeding hN~itat for their potential predators such as shore crabs (this study), rove beetles (Neame, Zimmer, Jelinksi, and Mews u n p u b l i s h e d data), frogs (Orr personal c o m m u n i cation), m iJ:tks, and bears (Mews, Zimmer, a n d Jelinski personal observations), The predators' eftect o n wrack d e c o m p o s i t i o n by a m p h i p o d s (Mews et al. 2006) may be substantial, b u t n u m e r o u s studies indicate that increasing environmeJ~tal structure r e d u c e s the ability of predators to capture prey (Gotceitas a n d Colgan 1989; Lewis m~d Eby 2002; Buck et al. 2003). While Interlidal Crabs i~] Supratidal Subsidy bmying in the sand obviously provides some prot e r t i a n ticom p r e d a t i o n b y H. n u d u s t o t a l i t r i d amphipods, foraging underneath wrack does not. W r a c k d i d n o t s i g n i f i c a n t l y attiect c a p t u r e t i m e o f amphipods by the beach-dwelling rove beetle, Thinopinus .pictus ( N e a m e , Z i m m e r , J e l i n s k i , a n d Mews unpublished data). Spending a significant a m o u n t o~ t i m e w i t h i n ~ a c k patches appears to i n c r e a s e ~he risk o f p r e d a t i o n b y p r e d a t o r s ~hat actively seek those wrack patches for foraging. We conclude that freshly deposited wrack, which becomes densely colonized by talitrid amphipods w i t h i n less t h a n o n e h o u r ( P e l l e t i e r , M e w s , J e l i n s k i , a n d Z i m m e r p e r s o n a l o b s e r v a t i o n ) , is m o r e i m p o r t a n t t o a m p h i p o d s as a t b o d s o u r c e w i t h s u i t a b l e temperature and moisture conditions t h a n as a s h e l t e r fi'orn p r e d a t o r s . C o n s i d e r i n g t h e a v a i l a b l e e v i d e n c e , we d e d u c e o l n n i v o r o u s f e e d i n g b e h a v i o r o f H. n u d u s t h a t u s e s t a l i t r i d m n p h i p o d s as a v a l u a b l e f b o d s o u r c e . T h e abundant availability of these detritivores in wrack lines renders this supratidal subsidy a habitat worthy o f i n t r u s i o l ~ f o r f o r a g i n g . T h e risk o f h a v i n g t o l e a v e s h e l t e r , b e it s u b t i d a l l y o r u n d e r n e a t h intertidal r o c k s a n d b o u l d e r s , is m i n i m i z e d by nocturnal f b r a g f n g at h i g h t i d e s . B e c a u s e w r a c k l i n e s a r e deposited at the previous high water mark, delaying f o r a g i n g u n t i l h i g h t i d e a l l o w s H. n u d u s t o r i d e t h e tide into the wrack lines without having to pass e x p o s e d b e a c h a r e a s . As a n e x t s t e p , r e m o v a l a n d addition of natural and artificial wrack in field e x p e r i m e n t s , as well as g u t a n a l y s e s o f f i e l d c o l l e c t e d c r a b s , m a y r e v e a l d i r e c t e v i d e n c e 1o c o r r o b o r a t e o r question our conchtsions based on tield observations and laboratory experiments~ ACK.NOWLEDGME N'I-S We are grateful to the former Director, Andy Spencer, and staff of the Bamtie/d Manne Sciences Centre, especially Jean Paul Danko, Andrea Hunter, and James Mortimer, for their support. This is contribution SIRG/03-04 of the Supratidal Interface Research Group. The experiments herein comply with the laws of Canada and British Columbia. LITERATURE CrTED BKPmoCa~v~, F 1999. Biostatisik. Thieme, Stuttgart, Germany. BEHRENS YAt~t~.~A,S. AND E. G. BOUI~INO. 1996. The role of highly mobile crab predators in the intertidal zonation of their gastropod prey. Journal oj EaqoerimentalMarine Biology and Ecology 204:59-83~ BEHRENS YitCa,~A, S. AND E. G. BOUI~ING. 1998. Claw morphology, prey size selection and foraging efficiency in generalist and specialist shell-breaking crabs. Journal oJ Evperig~ental Ma.~ine ~-,%7o~ a'nd s 220:191-211 BUCK, T. L., G. A. g,va~r), S. C. PENNINGS, ~r E. CH~SE, M. ZIMNIER., AND T. H. CAe~FOOT. 2003. Diet choice in an omnivorous salt marsh ceab: Different food types, body size and habitat complexity. Journal of E@erimental Marine Biology and Ecology 292:103-116 4.57 CORONA, A., L. A. SOTO, AND A. j. Sayca~Ez~ 2000. Epibenthic arnphipod abundance and predation efficiency of the pink shrimp Farjantepenaeas duorar, m (Burkenroad, 19391 in habitats with different physical complexity in a tropical esmarine system. Journal ojExperimental Marine Biology and Ecology 253:33-48. Cm~SWV~L, P. J. 1994. Age dependent choice of redshank (Tringa tetanus) feeding location: Profitability or risk? ]omnal of Animal Ecology 63:589-600~ DALNKL, B. AND E. G. BO1JLDING. 2005. Water-borne cues from a sheiI-crc~shing predator induce a more massive shell in experimeuta[ populations of an intertidal snail. Marine ~,io&gy 31'7:25-35. D ~ , P. J. AND D. B. Er~wam~s. 1981. Undec~vatec television observations on the iotertidal movements of shore crabs, Cardnw- meanas, across a mndflat. Journal oj the Ma~dne Biological Association of Ne United 7iTngrJom61:107--116. DUGAN,J. E., D. M. H l m ~ i L M. D. MCCRARu AND M O. PIERSON. 2003. The response of macrofauna communities and shorebirds to macrophyte wrack subsidies on exposed sand), beaches of somhem Califbmia~ Esau~rine (~a.*tal and Shd] Sc~enee 58S:133I48. FISHLa, R. A~ 1951. The Design of Experiments, 6th edition. Oliver and Boyd, Edinburgh, Scotland. GOTC%ITAS,V. AND E COLGAN. 1989. Predator foraging mccess and habitat complexity: Quantitative test of the threshold hypothesis. Oecologia 80:158-166. GmFFITHS, C. L.,J. M. E. S"rENTON-DozEY,AND K. KooP. 1983. Kelp wrack and the flow of energy through a sandy beach ecosystem, p. 547-556. In A McLachlan and T. Erasmus (eds.), Sandy Beaches as Ecosystems. J'unk, The Hague, The Netherlands. Lm~ls, D. B. aND L. A EBY. 2002. Spatially heterogeneo'us refilgia and predation risk in intertidal salt marshes. Oikos 96:I I9-I 29 MANLY, 23. 1993. Comments on design and analysis of multiplechoice feeding~preference experiments. Oeeulo~a 93:149-152. MARSDEN, I. D. aND R S. DEWA. 1994. Diel and tidal activity patterns of the smooth shore crab @dograpsus laz,auxi.~oumal of the Royal Sodet~ ojNew Zealand 24:429-438. McLaC~LAN, A. 1985. The btomass of macro- and interstitial fauna on clean and wrack~covered beaches in western Australia. Estuarine, Coastal and She{f Science 21:587-599. MEWS, M., M. Z I M ~ , AND D, E, JEtaNSm. 2006. Species-specific decomposition rates of beach-cast wrack in Barkley So'un d, British Columbia., Canada t~4arineEco{vgyProg~s 5%n~.'.~328:155-I60. NOKKIiO, A. 1998. Ti~e impact of loose-lying algal mats and predation by the beown shrimp Crangon crang0n (L.) on infaunal prey dispeE*a[ and survival. Journal of Experimental Marine Biology and Ecology 221:99-116. Ore% M., M. Z~aE~, D E J'~taNSm, AND M. MxWS. 20(~5. Wrack deposition on different beach types: Spatial and temporal variation in the pattern of subsidy. Ecology 86:1496-1507. PENN1NGS, S. C., T. H. C*2-.~FOOT, M. Z~MM~,J. P DaNxo, .aND A. Z~EGta~R.2000. Feeding preferences of supralittoral isopods and amphipods. Cana&an Jourm~l o/ Zoology 78:1918-1929. PL'r~aSON~ C. H. A~D P. E. I~NAVr 198q Analysis of feeding preference experiments. Oecologia 80:82-8& DOLLS, G. A., W. B~ ANDERSON, AND R. D. HOLT. 1997. Toward an integration of landscape and food web ecology-: The dynamics of spatially subsidized food webs. Annual Review of Ecology and Systematics 28:289-316. PdCa~Am~S,L.J. 1983. Feeding and activity patterns of an intertidal beetle. Journal of Experimental Marine Biology and Eeol%7 73:213-224. ROA, R. 1992. Design and analysis of multiple-choice feedingpreference expmirnents O~c0logia89:509-515. ROBLES~ C~ ]-). _A. S%~W-ETNAM,AND D DITT~,,~aN. ~989. Diet ,*adatiuu of intertidal • by Cancerproductus L~ io British Columbia. Journal of Natural HistaU 23:1041-1049. VETZXR, E. W. 1998. Population dynamics of a dense assemblage of marine detritivores. JoumaI of Experimental Manne Biology and Ecology 226:131-161. 458 T.L. Lewis et al. WILLIAMS,B. G. 1991. Comparative studies of ddat rhythms - V. Individual variation in the rilythm/c beha~ouc of C'am'~*us mae~*as (L.). Marine Behaviou,~ a*ed Physmlo~ 19:97-112, SOURCES OF UNPUBLISHED [k:L~TERIALS DALZIEL, B. personal communication. Depactment of Zoology, University of Guelph, Guelph, ON NIG ~W1, Carta.da. NEAME, L. A. V. unpublished data. Biologlcat Soences, Plant Evolutionary Ecology, Simon Fraser Univers{cy, 8888 University Drive, Burnaby, BC V5A 1S6. OPa, M. personal communication. Department of Biotogy, University of Victoria, STN, CSC, Victoria, British Columbia VSW 3N5. PELLETIER, A. personal observation. Centre for Biodiversity Research, Department of Zoology, University of British Columbia #2370-6270 University Blvd., Vancouver, B.C., Canada V6T 1Z4. Received, lane 30, 2006 Revised, February 28, 2007 Accepted, March 22, 2007