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Mar Ecol Prog Ser 338: 159-168, 2007
2004, the year with higher variations in winds and pre
dicted current, we found a significant negative correla
tion with northward currents and a positive correlation
with the easterly winds. Therefore, correlations de
pend on the range in variation and strong SW winds,
and an anticlockwise circulation pattern reduces
colonisation. (4) Spectral analysis of the northerly wind
and eastward current of 2005 revealed a peak at a
period of nearly 15 d (data not shown). Thus, both var
ied at approximately the same frequency as the spring-
neap cycle. Colonisation peaks occurred after rela
xation of the predicted eastward residual currents
(Days 200 to 210, Fig. 6). Either these correlations
arose from coincidental variation between tidal cycles
and winds, or they indicate that colonisation increases
after current relaxation. It is thus clear that strong and
persistent (>5 d long) periods of SW winds and east
ward currents lead to low colonisation rates, while
under other wind or current conditions, e,g. current
relaxation or westward currents, colonisation appar
ently varies as a function of tide.
Our hypothesis is consistent with a 2-step model of
larval supply formulated for coastal marine species in
general (see Miller & Shanks 2004 for discussion) and
supported by Carcinus maenas data from Portugal
(Queiroga et al. 2006). In addition, the influence of
local movements of megalopae on colonisation pat
terns may be contingent on the overall number of
larvae reaching the benthic habitats.
As an initial step in larval transport, wind-driven
currents are thought to transport larvae across the
continental shelf towards the coast (Shanks 1995, Wing
et al. 2003); in Portugal, the supply of Carcinus maenas
megalopae to estuaries may be related to upwelling
fronts reaching the coast after wind relaxation (Al
meida & Queiroga 2003, Queiroga et. al. 2006). In the
North Sea, variations in westward wind-driven trans
port may move larvae away or towards Helgoland.
Near the coast in mesotidal systems, selective tidal
stream transport (STST, Forward & Tankersley 2001)
or some form of tidally mediated water flow may trans
port larvae shorewards in pulses of about 2 wk, at or a
few days after spring tides; this may be the second step
in transport, as observed for Carcinus maenas in Portu
gal (Queiroga et al, 2006). This second step is contin
gent on the first step, since 2 wk pulses were observed
in the absence of strong SW winds or eastward cur
rents. In the estuaries along the Portuguese coasts,
zero time lags suggest STST, although the influence of
internal waves cannot be disregarded (Queiroga et al.
2006). Following Miller & Shanks (2004) and Queiroga
et al. (2006), the time lags of 1 to 5 d for Helgoland sug
gest a combined effect of STST and internal waves on
larval colonisation. The STST has been invoked for
megalopae invading estuaries: here cues associated
with estuarine water (e.g. low salinity) may entrain the
appropriate swimming behaviour of megalopae. Data
for coastal zones are sparse (Necora puber. Lee et al.
2005; C. maenas in mesotidal coastal zone of Wales:
Zeng & Naylor 1996, Queiroga 1998), but those that
are available for C. maenas show that larvae are more
abundant near the surface water at flood tide, espe
cially at night. This pattern would predict maximum
larval supply to the intertidal of Helgoland during
spring tides, since at this time at least 1 high tide
occurs al night. According to Zeng & Naylor (1996) this
pattern is not endogenous, but due to some exogenous
factor, perhaps related to the intertidal proximity (e.g.
turbulence),
Tidally mediated flow may be related to internal
waves through at least 3 different transport mecha
nisms, involving shoreward movements of (1) conver
gence zones, (2) upwelling fronts, and (3) cold bores
(Pineda 1999, Shanks 2006). River plumes, such as
those of the Elbe and Wesser, may be a source of large-
amplitude internal waves (Nash & Mourn 2005);
however, according to W. Alpers (www.internal-
waveatlas.com) internal waves are present only spo
radically in the North Sea, mainly in the summer
months. An analysis of density fronts and residual cir
culation of the German Bight, under minimal wind
effects (Luyten et al. 2003) suggest that a southward
flow can be expected at neap tide, while a northward
flow can be expected at spring tide. This pattern
should result in peaks of Carcinus maenas settlement
on Helgoland around spring tides. In summary, several
mechanisms may explain the abundance peaks around
spring tides; however, the fact that spectral analysis
shows a periodicity of 10 d, instead of 14 to 15 d, sug
gests that further studies are necessary to elucidate the
tidal mechanisms operating in the German Bight.
Finally, the influence of emigration-immigration
cycles of megalopae on colonisation rates should also
be contingent on the absence of strong SW winds. This
was the case in the 2005 and part of the 2003
settlement period, with marked short-period (ca. 5 d)
variability in colonisation rate. SW winds or eastward
currents should lead to low settlement rates and a low
number of megalopae colonising the sediment.
In summary, variability in intertidal colonisation by
megalopae of the shore crab Carcinus maenas in the
North Sea may be related to wind-driven current and
tidal conditions. Colonisation is low under strong and
persistent eastward currents, whereas under other
conditions (westward currents or during relaxation
events), colonisation may be high and related to sping-
neap tidal cycles. Future work should elucidate the
mechanisms of larval transport in the North Sea and
relationships between larval supply, colonisation and
juvenile recruitment in the intertidal.