Giménez & Dick; Shore crab settlement and transport mechanisms
161
Bft 1 = 0.3 to 1.5 ms 2 = 1.6 to3.3 ms' 1 ,3 =3,4 to 5.4 m
s’ 1 , 4 = 5.5 to 7.9 m s’ 1 , 5 = 8.0 to 10.7 m s’ 1 , 6 = 10.8 to
13.8 m s’ 1 , 7 = 13.9 to 17.1 m s’ 1 , and 8 = 17.2 to 20.7 m
s’ 1 : World Meteorological Organization 1970). The N-S
and W-E components were regarded as positive when
the wind was from the north or east, respectively.
Daily residual surface currents (0 to 8 m), predicted
from an operational circulation model developed by
Federal Maritime and Hydrographic Agency for the
(a)
German Bight (Dick et al. 2001), were used to explore
potential effects of current patterns on colonisation of
megalopae. The model simulates tidal-, density- and
wind-driven motion. Based on meteorological forecasts
supplied by the DWD, the hydrodynamical model pre
dicts currents in a nested grid system. The model had
been previously validated in the North Sea with good
agreement between data and predictions (Klein & Dick
1999, Dick et al. 2001), and has been successfully used
to predict and combat marine pollu
tion (e.g. Dahlmann & Miiller-
Navarra 1997). Current components
were calculated from predicted sur
face current fields in the German
Bight with 1.8 km grid spacing. The
data covering 50 km around Helgo
land were coded in an 8-sector
rosette. Current components are pos
itive if currents are moving east
wards or northwards.
Data analysis. Time series analysis
followed the protocol shown in
Fig. 2a (after Chatfield 2004) using
Statistica®. For abundance data, colo
nisation rate of all collectors were
pooled each day. Visual inspection of
the time series showed trends and
considerable variability, which in
creased with increasing abundance.
Therefore, colonisation data were
log(x+l)-transformed, the trend re
moved, and the data smoothed by a 3
points moving-average. The function
used for trend extraction depended
on the year: for 2003 and 2004 data
showed either an increasing or a
decreasing trend, so a linear function
was used; in 2005 data showed a
humped pattern, and the trend was
extracted using a log-normal function
adjusted by non-linear regression
(Fig. 2b).
Spectral analysis of the de-trended
time series of abundance was used to
explore temporal patterns of varia
tion. Relationships between abun
dance, wind and predicted currents
were explored using cross-correlation
analysis after smoothing all series. Po
tential relationships between abun-
240 dance and tidal cycles were also
explored with cross-correlation ana
lysis, using the days since spring tide
as variable. All cross-correlations
were done by lagging the predictor
Pooling colonisation
X(f> = x, (í) + Xj (0 +x,(()
Transformation
V*{i) = log 1)
I
Trend subtraction
Z{t) = Y(t)~Y(t)
L
Spectral analysis
Wind or current components
C(t)
I
Trend subtraction
S (() = C (0 - C (f)
Smoothing
Cross-
Smoothing
¿(0
correlation
S(f)
Spectral analysis
(b)
£Z
o
to
(O
c
o
o
o
<31
o
JO
(0
3
•g
m
ai
CT
jo
(0
3
■o
(0
01
t_
to
01
■C
5
4
3
2
1
0
2
1
0
-1
-2
2
O -1
£
(O
-2
Ÿ (t) = 0.2598 it ■' e “ 27 - 5S72 (Log < - s.2430|<
170
180
190
200
210
220
230
Day
Fig. 2. Procedure for time series analysis, (a) Flow diagram showing data trans
formation for spectral analysis and cross-correlation; (b) example of data trans
formation for colonisation by Carcinus maenas megalopae in 2005 (data from Fig. 6)