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Hydrobiologia (****) ***:*** ***

DOI **.****/s***50-011-0628-1

ZOOPLANKTON ECOLOGY

Zooplankton assemblages as indicators of seasonal changes

in water masses in the boundary waters between the East

China Sea and the Taiwan Strait

Shih-Hui Hsiao Samba Ka Tien-Hsi Fang

Jiang-Shiou Hwang

Published online: 3 March 2011

Springer Science+Business Media B.V. 2011

Abstract Hydrology and trophic relationships are indicating their association with the cold waters of

frequently reported for inducing changes in mesozoo- the East China Coastal Current. Appendicularians and

plankton communities. This study investigated the N. scintillans were mainly associated with the coastal

distribution and abundance of mesozooplankton in the waters of Taiwan; whereas C. sinicus was concen-

boundary waters between the East China Sea and trated in the offshore waters along the coast of

the Taiwan Strait. Samples were collected using a Mainland China. Chaetognaths, Temora turbinata,

NOR-PAC zooplankton net towed horizontally at a Acrocalanus spp., and radiolarians were dominant in

depth of 2 m, at eight stations along a transect, in autumn, showing their association with the warm

March (spring) and October (autumn) 2005. The waters of the Kuroshio Branch Current. Oncaea

abundance of mesozooplankton was signi cantly venusta was relatively abundant during both seasons.

higher during autumn than spring. Densities of many Our study shows that, in addition to the in uence of

groups (e.g., Noctiluca scintillans, pteropods, cope- seasonal changes in the water masses, the distribution

pods, mysids, euphausiids, and other larva) increased and composition of mesozooplankton are highly

in October. During both seasons, copepods repre- in uenced by trophic interactions between zooplank-

sented more than 50% of the total zooplankton ton taxa, in the boundary waters of the Taiwan Strait

abundance. Noctiluca scintillans, appendicularians, and the East China Sea.

and Calanus sinicus were dominant in spring,

Keywords Copepods Appendicularians

Noctiluca scintillans Hydrology Kuroshio Branch

Guest editors: J.-S. Hwang and K. Martens / Zooplankton Current East China Coastal Current

Behavior and Ecology

S.-H. Hsiao S. Ka J.-S. Hwang Introduction

Institute of Marine Biology, National Taiwan Ocean

University, Keelung 202, Taiwan

e-mail: *******@****.****.***.**

In marine ecosystems, mesozooplankton organisms

play an important role, as a link between the primary

S.-H. Hsiao T.-H. Fang

producers and higher consumers (Humes, 1994;

Department of Marine Environmental Informatics,

National Taiwan Ocean University, Keelung 202, Taiwan Naganuma, 1996). Mesozooplankton grazes on phy-

toplankton and are consumed by zooplanktivorous

S.-H. Hsiao

sh and other carnivorous organisms such as jelly sh.

Department of Science Education, National Taipei

In addition, mesozooplankton organisms are highly

University of Education, Taipei 106, Taiwan

123

318 Hydrobiologia (2011) 666:317 330

source of nutrients for the East China Sea (Chen

sensitive to environmental variations such as seasonal

et al., 1995, 1996; Lee et al., 2004), in uencing

changes in water masses, inducing seasonal succes-

biological productivity and sh catches (Wong et al.,

sions and uctuations in the abundance, and distri-

1991; Liu et al., 1992; Gong et al., 1995). The water

bution of various communities or species in aquatic

masses have high temperature and salinity in the

ecosystems (Uye et al., 2000; Tseng et al., 2008).

KBW and low temperature and salinity in the CCW,

Thus, several mesozooplankton organisms (copepods

due to the discharge of freshwater from a series of

or others groups) are commonly used as indicators for

rivers in Mainland China (Lee et al., 2004), and

water masses and oceanic currents (Grant, 1991;

intermediate temperature and salinity in the South

Hwang & Wong, 2005; Hwang et al., 2006; Tseng

China Sea Water (SCSW) (Chu, 1971). Although,

et al., 2008). Furthermore, in the context of climatic

these different oceanic waters have been proposed as

changes, drastic changes are anticipated in physical

the primary driving forces behind the enrichment of

parameters, such as temperature and salinity in many

marine biodiversity in Taiwan (Wong et al., 2000;

marine ecosystems (Chen & Folt, 2002). Thus,

Liu et al., 2003; Hwang et al. 2004a, b, c, 2006),

studying the seasonal dynamics of zooplankton and

the means by which it relates to variations in water seasonal changes in the relative in uence of these

masses could provide a deeper understanding of water masses may act as a contributing factor in the

marine ecosystems and help to ameliorate predictions temporal variations of marine organisms.

concerning such changes, in the local context as well The purpose of this study was to examine the

as the global. impact of changes in water masses in the boundary

The boundary waters between the Taiwan Strait waters of the Taiwan Strait and the East China Sea, as

and East China Sea are primarily in uenced by three they pertain to the composition and seasonal dynam-

currents: the East China Coastal Current (ECCC), the ics of the mesozooplankton; and to evaluate the group

Kuroshio Branch Current (KBC), and the South association among the taxa in relation to trophic

China Sea Surface Current (SCSSC) (Jan et al., interactions. Unlike the study of Hwang et al. (2006),

2002). The seasonal in uence of these currents is this present study was performed not only on

governed primarily by the monsoon system (Jan copepods, but also on other important mesozooplank-

et al., 2002; Liang et al., 2003; Tseng & Shen, 2003). ton taxa. This study represents an attempt to under-

During winter, the northeastern (NE) monsoon stand the main factors determining the distribution

induces a southward movement of the ECCC into and composition of the mesozooplankton in the study

the Taiwan Strait, while the KBC ows northward area.

along the west coast of Taiwan (Wang & Chern,

1988; Hu et al., 1999). However, the Kuroshio

Branch Water (KBW) which is blocked by ECCC Materials and methods

in the Changyun Ridge of the Penghu Channel covers

the entire eastern half of the Strait, while the China Samples were collected during two cruises in spring

Coastal Waters (CCWs) are con ned to the western (March, 2005) and in autumn (October, 2005) at eight

side (Liang et al., 2003; Hwang et al., 2006). During stations on a transect extending along the boundary

spring, the weakened NE monsoon leads to northward waters of the Taiwan Strait and the East China Sea

intrusion of the KBW into the Penghu Channel, (Fig. 1) aboard the R/V Ocean Research-II.

in uencing the northern part of the Taiwan Strait (Jan

et al., 2002; Hwang et al., 2006). During summer, the Environmental data

southwestern (SW) monsoon induces southward

movement of the SCSSC and KBC in the Taiwan Monthly averages for sea surface temperatures and

Strait; whereas in autumn, the beginning of the NE concentrations of chlorophyll a in seawater were

monsoon leads to the intrusion of the CCW in the collected from advanced very high resolution radi-

northwestern (NW) reaches. The in uence of the ometer (AVHRR) recordings in March and October

KBC into the Taiwan Strait is higher in the summer of 2005. At each station, temperature and salinity

than in winter. The subsurface Kuroshio waters in were simultaneously recorded using the on board

conjunction with the Yangtze River is the major SeaBird CTD instrument.

123

Hydrobiologia (2011) 666:317 330 319

Fig. 1 Schematic showing the Taiwan Strait circulation in waters between the Taiwan Strait and the East China Sea, in

a winter, b spring, c summer and d fall, after Jan et al. (2002); March and October 2005

and e location of our sampling stations (St) in the boundary

123

320 Hydrobiologia (2011) 666:317 330

Zooplankton sampling a are shown in Fig. 2. In March, temperatures showed

a highly marked gradient between the northern coast

Zooplankton samples were collected using a NOR-PAC of Taiwan and the coast of mainland China, decreas-

ing from 18 to 12 C. In October, the variation was not

net (diameter of 45 cm, mesh size of 333 lm). A ow

as high, with values ranging between 25 and 26 C.

meter (Hydro-Bios) was mounted at the center of the

mouth opening. The net was towed 2 m below the Concentrations of chlorophyll a ranged between 0.5

and 5.0 mg m-3, with the highest levels observed in

surface. Sampling time was approximately 100 min at a

vessel cruise speed of two knots. The samples of the waters off the coast of mainland China.

zooplankton were immediately preserved in 5 10% The TS diagram distinguishes two different water

buffered formalin seawater. At the laboratory, when masses in March (Fig. 3): waters with low tempera-

necessary, samples were split into subsamples using a ture and salinity (St7 and St8), and waters with high

Folsom splitter to count a maximum number of 500 temperature and salinity (St1 to St6). In October, only

individuals of dominant species. Rare taxa were counted a single water mass with elevated temperature, and

from the entire sample. All taxa were listed and their salinity similar to that of St1 to St6 of March was

abundances expressed in number of individuals per detected along the transect. The CTD vertical pro les

cubic meter (ind. m-3). Copepods were identi ed of temperature and salinity for each season are

following the methods of Chen & Zhang (1965), Chen presented in Fig. 4. In March, temperatures and

et al. (1974), and Huys & Boxshall (1991), whereas salinity decreased from the coastal waters of Taiwan

(St1, temperature 16.2 0.7 C, salinity 34.6 0.01)

others organisms were identi ed in accordance with the

studies of Mitsuo & Masaaki (1997). to the coastal waters of mainland China (St8,

temperature 10.4 0.7 C, salinity 31.1 1.0). In

Data analyses October, any gradient was observed in the tempera-

ture of the surface water along the transect. However,

Mann Whitney U test (non-parametric) and Spear- along the coast of Taiwan (St1 to St3) a marked

man correlation analyses were performed using SPSS vertical gradient was observed in the temperature,

13.0 for Windows to compare the taxa abundances with the lowest values measured below 60 m of depth.

between the two season and the taxa relationships, In October, the lowest salinity values were recorded in

respectively. the surface coastal waters all along the transect.

To reduce the elevated heteroscedasticity observed

in the original data on the abundance of species, a Zooplankton

transformation was generated using regression coef-

cients estimated by maximizing the log likelihood Mean mesozooplankton abundance increased signif-

icantly between March (132.9 114.9 ind. m-3) and

function (Box & Cox, 1964). Accordingly, the matrix

October (390.2 169.3 ind. m-3) (Table 1). The

of data related to the abundance of dominant

zooplankton taxa was used in conjunction with densities of dominant taxa comprising populations

Bray Curtis similarity indices following logarithmic such as Noctiluca scintillans, pteropods, copepods,

transformations log(X ? 1) using PRIMER 5 (Plym- amphipods, decapods, and chaetognaths increased

outh Routines in Multivariate Ecological Research) signi cantly between March and October (Mann

Whitney U test, P \ 0.05). Copepods dominated the

programme. Taxa characterizing each cluster were

further identi ed using the Indicator Value (IndVal) zooplankton population making up 60 and 58% of the

index proposed by Dufrene & Legendre (1997). mean abundance in March and October, respectively.

However, their proportion was lower in Sts 1 and 2

off the coast of Taiwan (Fig. 5). Depending on the

Results season, other holoplanktonic taxa, such as chaetog-

naths, appendicularians, N. scintillans, and radiolari-

Environmental data ans, made up a major proportion of the population.

Chaetognaths were observed in all stations, constitut-

Monthly average information derived from AVHRR ing 11 and 10% of the total mean abundance in

recordings of sea surface temperature and chlorophyll March and October, respectively. Appendicularians

123

Hydrobiologia (2011) 666:317 330 321

Fig. 2 Monthly average

sea surface chlorophyll

a and temperatures (SSTs)

derived from averaged

hourly recordings

(AVHRRs) in March 2005

and October 2005

28 March and October, respectively. Radiolarians con-

St5

St8 stituted 9% of the total mean abundance in October.

St7 St6

St3

St4

24 Copepods

St2

St1

Temperature ( C)

Altogether, 72 species of copepod were identi ed

20 during the two seasons. These belong to 32 genera: 46

calanoids, 3 cyclopoids, 2 harpacticoids, and 21

St2

poecilostomatoids (Table 2). Copepod diversity was

St3

St5

16

St6 St4 St1 high during both seasons (Fig. 5). The Shannon index

value decreased from the coastal waters of Taiwan (Sts

1 and 2) to those of mainland China in March. The

12 St7

highest diversity index was observed from St2 to St6 in

October. Oncaea venusta was present in all sample

St8

stations (100% of occurrence) both in March and

8

October. Calanus sinicus and Euchaeta rimana were

**-**-**-**-**-** 35

present at all sample stations in March, whereas

Salinity

Canthocalanus pauper, Undinula vulgaris, Subeucal-

Fig. 3 Temperature salinity diagram of the water masses anus subcrassus, and Temora turbinata were present at

along the transect in the boundary waters between the Taiwan all sample stations in October (Table 2). The most

Strait and the East China Sea, in March (solid curves) and in

abundant copepod species in decreasing order of mean

October (dotted curves)

density were C. sinicus (46%), E. concinna (13%),

constituted 10% of the total mean abundance in March O. venusta (8%), and E. rimana (5%) in March;

and Acrocalanus gracilis (19%), T. turbinata (18%),

(Fig. 5). Noctiluca scintillans accounted 6 and 8% on

A. gibber (11%), O. venusta (8%), Paracalanus parvus

the total mean abundance of the mesozooplankton in

123

322 Hydrobiologia (2011) 666:317 330

March

Temperature Salinity

34.5

17.5

20 34

16.5

33.5

15.5

40 33

32.5

14.5

60 32

13.5

31.5

80 12.5 31

30.5

11.5

100 30

10.5

29.5

120 9.5 29

October

Temperature Salinity

27.5

20 26.5

25.5 35

40 24.5

23.5

60 22.5 34.5

21.5

80 20.5

19.5 34

100 18.5

17.5

120 16.5 33.5

St1 St2 St3 St4 St5 St6 St7 St8

St1 St2 St3 St4 St5 St6 St7 St8

Fig. 4 Vertical and horizontal pro les of temperature and salinity along the transect in the boundary waters between Taiwan Strait

and East China Sea in March and October 2005

Hierarchical classi cation and identi cation

(7%), P. aculeatus (5%), E. concinna (5%), Can.

of dominant zooplankton taxa assemblages

pauper (4%), T. discaudata (4%), and S. subcrassus

(4%) in October (Table 2).

Cluster analysis of zooplankton taxa indicated six

The mean abundance of copepods was signi -

cantly higher in October (237.5 163.2 ind. m-3) principal groups (Fig. 7). The rst hierarchical level

than in March (88.5 98.6 ind. m-3). In March, the of the cluster analysis separated the coastal waters of

density of copepods was lower than 100 ind. m-3 at Taiwan (St1 and St2) in March assemblage (cluster

IA) from all the remaining stations in any season

all stations, except at St8 where a peak of 325.1 ind.

m-3 was reached (Fig. 5). In contrast, in October, (cluster IB). The second hierarchical level distin-

guished the assemblage of St3 to St8 in March

the density of copepods was higher than 100 ind.

m-3 at all sample stations with two peaks at St3 (cluster IIA) from other assemblages of St1 to St8 in

(368.0 ind. m-3) and St5 (588.2 ind. m-3) (Fig. 5). October (cluster IIB). The next hierarchical level

distinguished four different clusters, representing St1

The density of C. sinicus was signi cantly higher in

(IIIA), St2 (IIIB), St3 to St7 (IIIC), and St8 (IIID) in

March than in October, whereas most of the other

March; and St1 to St3 (IIIE) and St4 to St8 (IIIF) in

dominant copepods were signi cantly more abun-

October. Clusters IA, IIIA, and IIIB (St1 and St2

dant in October than in March (Fig. 6). However,

in March) were characterized by low temperature

the density of Paracandacia bispinosa, Par. trun-

(17.5 17.6 C), high salinity (34.3 34.6) surface

cata, E. concinna, E. rimana, and P. parvus did not

waters (0 10 m of depth), with the highest densities

vary signi cantly between March and October

of appendicularians (33 41% of total zooplankton

(Fig. 6).

123

Hydrobiologia (2011) 666:317 330 323

sampled stations in October) were characterized by

Table 1 Total zooplankton abundance (mean SD, in ind.

m-3), relative abundance and occurrence (in %) of the main warm waters (27.2), high salinity (33.9 34.2), and the

groups found along the transect, in the boundary waters

highest densities of chaetognaths (8 10%), T. turbi-

between the Taiwan Strait and the East China Sea, during

nata (12 17%), A. gracilis (7 13%), A. gibber

March and October 2005

(5 8%), N. scintillans (7 13%), and radiolarians

Taxa March October

(9 22%) (Table 3).

Mean SD Occ. Mean SD Occ.

Total 132.9 114.9 390.2 169.3

Discussion

zooplankton

Noctiluca 6.0 11.5 63 7.6 5.5 100

In March (end of winter), a high-temperature gradient

scintillans

in the water and salinity along the transect between

Radiolaria 0.5 0.8 38 8.9 15.9 63

the coasts of Taiwan and mainland China showed

Foraminifera 0.0 0 0.5 0.9 25

differences between the two water masses, corre-

Medusa 5.1 4.5 88 1.6 1.0 100

sponding to waters associated with the ECCC (St7

Pteropoda 0.2 0.6 25 1.9 2.6 88

and St8, low salinity and temperature), and waters

Polychaeta 0.1 0.1 25 0.3 0.5 38

associated with the KBC (St1 to St6, high temper-

Bivalve molluscs 0.2 0.4 25 0.0 0

ature and salinity). In October (autumn), the water

larva

mass at all stations of the transect were characterized

\0.1 0.1

Cladocera 13 0.0 0

by high temperature and salinity, corresponding to

Ostracoda 1.2 1.1 75 2.1 3.4 63

the waters of KBC. Our results correspond with the

Copepoda 59.5 20.6 100 57.7 14.9 100

studies of Lan et al. (2004) and Hwang et al. (2006),

Cirripedia 0.1 0.3 13 0.1 0.2 13

which reported that during the spring, the water

Mysidacea 0.4 0.9 25 0.5 0.8 38

masses of the eastern side of the northern Taiwan

\0.1 \0.1

Amphipoda 13 2.3 3.6 75

Strait are in uenced mainly by the KBC, while the

Euphausiacea 0.2 0.4 25 0.8 1.2 50

western side is in uenced by the ECCC. In addition,

Decapoda 0.4 0.5 50 4.3 2.7 100

it was reported that the KBC introduced water masses

Heteropoda 0.0 0 0.0 0.1 13

with higher temperatures and salinity; whereas the

Chaetognatha 11.4 12.2 100 9.8 6.7 100

ECCC was associated with lower temperatures and

Echinodermata 1.1 1.7 50 0.2 0.5 13

salinity (Hsieh et al., 2004; Li et al., 2006).

larva

Our results illustrate the considerable impact of

Appendicularia 9.9 16.8 63 0.2 0.3 50

seasonal variations in water masses on the diversity,

Others (larva) 0.4 0.5 38 1.2 1.1 63

composition, and abundance of mesozooplankton.

Fish eggs 3.0 2.8 75 0.1 0.1 38

Between March and October, the abundance of the

most important taxa increased signi cantly with

abundance, indicator species with IndVal [25%) and changes in water mass. This change in the water

N. scintillans (12 32% of total zooplankton abun- mass was accompanied by an increase in temperature,

dance, indicator species for IIIA with IndVal [25%) suggesting that this last parameter is a major factor

(Table 3). Clusters IIA, IIIC, and IIID (St3 to St8 in in uencing seasonal changes in the community of

March) were characterized by the lowest temperature mesozooplankton. Previously, Hsieh & Chiu (2002)

(9.9 15.5 C) and salinity (29.7 33.4) surface waters reported that the abundance of copepods was posi-

(0 10 m of depth), with high densities of C. sinicus tively related to water temperature in the northern

(33 41% of total zooplankton abundance, indicator Taiwan Strait. This observation was reinforced by a

species with IndVal [25%) and chaetognaths (7 17% reduction in the abundance of copepods observed in

of total zooplankton abundance) (Table 3). Medusae the northwest of the Japan Sea during the winter

and E. concinna were also abundant at these stations (Dolganova & Zuenko, 2004). The dominance of

contributing 5 7% and 6 13% of total zooplankton copepods in mesozooplankton is commonly observed

abundance, respectively (Table 3). The remaining in marine ecosystems (Rakhesh et al., 2006; Eskinazi-

clusters (IIB, IIIE, and IIIF corresponding to the

Sant Anna & Bjornberg, 2006; Tse et al., 2007).

123

324 Hydrobiologia (2011) 666:317 330

Fig. 5 Station wise March October

variations in abundance 150 300 Noctiluca scintillans

dominant zooplankters and Radiolarians

Chaetognatha

diversity of copepods along 250 Appendicularians

120

Density (ind. m-3)

Density (ind. m-3)

Decapods

the transect in the boundary

Other groups

200

waters between the Taiwan 90

Strait and the East China

150

Sea, in March and October

60

2005. Note: the scales for 100

Y-axis for zooplankton

30

density in October differ by 50

factor 2 March

0 0

350 4.5 700 4.5

Copepods

Shannon index

4.0 4.0

300 600

3.5 3.5

Density (ind. m-3)

Density (ind. m-3)

Shannon index

250 500

Shannon index

3.0 3.0

200 400

2.5 2.5

150 300

2.0 2.0

100 200

1.5 1.5

50 100

1.0 1.0

0 0.5 0 0.5

St1 St2 St3 St4 St5 St6 St7 St8 St1 St2 St3 St4 St5 St6 St7 St8

Stations Stations

Many studies have reported the importance of This study basically noted that copepods are less

environmental factors (salinity, temperature, and abundant in the coastal waters of Taiwan (St1 and

primary production) on the abundance and distribu- St2) characterized by the highest abundances of

tion of zooplankton (e.g., Tan et al., 2004; Reese N. scintillans and appendicularians. Many studies

et al., 2005; Champalbert et al., 2007). In Dabob Bay have reported the predation of copepod eggs by

(Washington), Fulmer & Bollens (2005) reported that Noctiluca spp. (Daan, 1987; Quevedo et al., 1999).

chaetognaths, which are highly abundant in summer On the other hand, it has also been reported that

and spring, consume mostly copepods, thus their calanoid copepods are capable of ingesting appendi-

abundance is correlated to that of copepodites. Thus, cularians (Lopez-Urrutia et al., 2004; Stibor et al.,

in the present study, an increase in the abundance of 2004), which can explain the low densities of this

many predator groups such as chaetognaths may also taxa in offshore waters and the coastal waters of

be linked to an increase in the abundance of copepods Mainland China. Thus, predation of appendicularians

in autumn (Spearman correlation, q = 0.002). On the by copepods and the predation of copepod eggs by N.

other hand, in the coastal waters of Gulf of Maine scintillans (Spearman, signi cant negative correla-

(North America), Sherman & Shaner (1968) reported tion values with most of the dominant copepods)

high density of Saggita elegans (stage 1) resulting could explain the reverse distribution of copepods

from breeding in summer and autumn. This can and these other two taxa along the transect. The

support also the highest density of chaetognaths we present study shows that appendicularians and N.

observed in our study during autumn. Tse et al. scintillans are associated mainly with the coastal

(2007) reported that the currents from the South waters of Taiwan (St1 and St2) in March, a period for

China Sea carry various species of chaetognaths into which they could act as good indicators (IndVal

[25%). N. scintillans is particularly known for its

the coastal waters of Hong Kong. This phenomenon

may also be applicable to the KBC, owing from the association with coastal waters (Ka & Hwang, 2011)

southern side of Taiwan. However, the suggested and upwelling areas (Dela-Cruz et al., 2008).

hypothesis about reproduction may be an interesting Basically, our results show a higher degree of

one. species diversity at the stations in uenced by the

123

Hydrobiologia (2011) 666:317 330 325

Table 2 List and occurrence of the copepods species in the boundary waters between the Taiwan Strait and East China Sea in

March and October 2005

Taxa/species Taxa/species Taxa/species Taxa/species

Calanoida Clausocalanus farrani (25, 0) Delius nudus (0, 25) Corycaeidae

Paracalanus aculeatus

Acartiidae Clau. furcatus (38, 0) Corycaeus (Agetus) limbatus

(38, 88) (13, 38)

P. parvus (75, 50)

Acartia danae (0, 13) Clau. lividus (38, 0) C. (Agetus) typicus (13, 13)

A. erythraea (0, 13) Clau. mastigophorus (38, 25) Parvocalanus crassirostris C. (Corycaeus)

(0, 13) crassiusculus (50, 13)

A. paci ca (25, 0) Clau. minor (38, 0) Pontellidae C. (Corycaeus) speciosus (50, 63)

Calanidae Eucalanidae Calanopia minor (38, 0) C. (Ditrichocorycaeus)

andrewsi (38, 13)

Calanoides carinatus Rhincalanus Scolecithricidae C. (Ditrichocorycaeus) asiaticus

(13, 13) rostrifrons (25, 0) (38, 38)

Calanus sinicus (100, 38) Subeucalanus Scolecithricella minor C. (Ditrichocorycaeus) dahli

crassus (0, 50) (50, 38) (38, 13)

Canthocalanus pauper S. mucronatus (0, 25) Scolecithrix bradyi (13, 13) C. (Ditrichocorycaeus)

(75, 100) erythraeus (0, 13)

S. subcrassus (75, 100)

Cosmocalanus darwini Temoridae C. (Onychocorycaeus)

(63, 63) agilis (38, 13)

Temora discaudata (25, 75)

Nannocalanus minor (38, 63) Euchaetidae C. (Onychocorycaeus) catus (0, 63)

Undinula vulgaris (38, 100) Euchaeta concinna (88, 75) T. turbinata (88, 100) C. (Onychocorycaeus)

giesbrechti (25, 0)

Calocalanus gracilis (25, 0) E. indica (75, 50) Farranula carinata (0, 25)

Cal. pavo (38, 0) E. longicornis (25, 25) Cyclopoida F. gibbula (25, 63)

E. rimana (100, 88)

Candaciidae Oithonidae Unidenti ed species (0, 25)

Candacia ethiopica (50, 0) Lucicutiidae Oithona plumifera (25, 0) Oncaeidae

Paracandacia bispinosa Lucicutia avicornis (38, 0) O. rigida (38, 0) Oncaea clevei (0, 13)

(25, 38)

Par. simplex (0, 38) Metridinidae O. setigera (38, 38) O. conifera (0, 13)

Par. truncata (38, 38) Pleuromamma abdominalis Harpacticoida O. media (13, 25)

(13, 0)

Centropagidae P. gracilis (25, 13) Ectinosomatidae O. mediterranea (38, 50)

Centropages calaninus Paracalanidae Microsetella norvegica O. minuta (25, 25)

(0, 25) (13, 0)

O. venusta (100, 100)

Cen. furcatus (0, 63) Acrocalanus gibber (38, 88) Miraciidae

Cen. tenuiremis (90, 13) A. gracilis (88, 88) Macrosetella gracilis Sapphirinidae

(25, 13)

Clausocalanidae A. monachus (38, 0) Poecilostomatoida Sapphirina stellata (0, 13)

Bold characters represent the most abundant species; and numbers in brackets the occurrence of species in March and October,

respectively

KBC (Fig. 5). These ndings correspond to those of zooplankton differed among water masses in the

reported in previous studies (e.g., Shih & Chiu, 1998; boundary waters between the Taiwan Strait and the

Hsieh et al., 2004; Lan et al., 2004). Hsieh et al. East China Sea. In fact, we observed a shift in

(2004) have suggested that this is a result of the more the composition of species between March and

stable environment of the Kuroshio waters. However, October. C. sinicus and E. concinna were largely

in our study the lowest diversity observed in March the dominant species in March, whereas A. gracilis,

was caused primarily by the high abundance of A. gibber, T. turbinata, and O. venusta co-dominated

C. sinicus during the same period. The composition in October. The number of copepod species found in

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326 Hydrobiologia (2011) 666:317 330

Fig. 6 Variations in the 100

most abundant copepod

species (mean SE) along

Log abundance (ind. m )

ns ns

the transect in the boundary ns

-3

*** *** ns

waters between the Taiwan 10

Strait and the East China

Sea in March and October

2005 (Mann Whitney

U test, sig. ***P \ 0.001, 1

**P \ 0.01, *P \ 0.05, ns

P [ 0.05)

0.1

0.01

C. sinicus Cant. U. vulgaris E. rimana

Par. Par. S. E.

pauper bispinosa truncata subcrassus concinna

100

March

October

ns

Log abundance (ind. m )

*

-3

10

1

0.1

0.01

O. venusta

P. P. T. T.

A. gibber A. gracilis

aculeatus parvus discaudata turbinata

Fig. 7 Dendrogram

showing similarities in the

most abundant zooplankton

taxa in the boundary waters

between the Taiwan Strait

and the East China Sea in

March and October 2005,

based on the Bray Curtis

index

123

Hydrobiologia (2011) 666:317 330 327

Table 3 Dominant species, contributing [50% to the relative abundance of each cluster during the two sampling seasons, calculated

using Bray Curtis cluster analysis (see Fig. 7)

Dominant taxa Cluster level

Group Group Group Group Group Group Group Group Group Group

IA IB IIA IIB IIIA IIIB IIIC IIID IIIE IIIF

Noctiluca scintillans 22 4 7 12 13

32

Radiolarians 5 9 22

Medusae 7 7 5

Decapods 5

Chaetognaths **-**-**-**-*-*-**

Appendicularians 37 41 33

Fish eggs 5 7

Calanus sinicus 5 17 7

40 33 72

Acrocalanus gibber 6 8 5

Acr. gracilis 5 9 13 7

Paracalanus aculeatus 9

P. parvus 6

Euchaeta concinna 6 11 13

Temora turbinata 7 12 17

Oncaea venusta 5 7

Cumulative contribution **-**-**-**-**-** 70 84 72 51

Bold values represent indicator taxa with a IndVal [ 25%

presence of this copepod in warmer waters of 27.2 C

our study was lower than that of Hwang et al. (2006).

This can be explained by the fact that the study by (Lan et al., 2004). In autumn, C. sinicus is still the

Hwang et al. (2006) was performed over a longer most abundant of the large copepod species in the

period (5 years), covering more stations in the coastal Yellow Sea and East China Sea (Zuo et al., 2006).

waters of Taiwan and in the vicinity of the Danshui However, Zhang et al. (2007) reported that higher

estuary, which introduced typical estuarine copepod temperatures have a deleterious effect on both the

species such as Pseudodiaptomus annandalei. fecundity and hatching of C. sinicus, which could

A high degree of correlation between water masses explain the low abundance of this copepod in the

and the assemblage and distribution zooplankton was boundary waters of the Taiwan Strait and the East

recorded in our study, and in previous studies (Hsieh China Sea in autumn, in this study. However, in our

et al., 2004; Hwang et al., 2006; Zuo et al., 2006; Lan study, C. sinicus was present in very low densities

(0.1 0.3 ind. m-3) in autumn only from St6 to St7

et al., 2009). C. sinicus is known for its preference of

cold water masses (Uye, 1988; Lan et al., 2004; located near the coast of Mainland China, where

surface temperatures were lower (26.8 C) during this

Hwang et al., 2006), explaining the introduction of

this species to the Taiwan Strait from the East China period. This means that during autumn, the main

Sea, Yellow Sea, and Bohai Sea by the ECCC during population of C. sinicus is distributed on the northern

the NE monsoon in winter and spring (Zheng et al., side of the boundary waters between the Taiwan

1992; Hwang & Wong, 2005). Our study con rms Strait and the East China Sea. The other copepod

that C. sinicus is a good indicator of the intrusion of species present along our entire transect in October

waters into the Taiwan Strait from the East China Sea and along the western part during winter are domi-

in winter, as suggested by several other studies (e.g., nant in the South China Sea (Lo et al., 2001; Dur

Hwang & Wong, 2005; Hwang et al., 2006; Dur et al., 2007; Hwang et al., 2007). Euchaeta concinna,

et al., 2007). Recently, studies have reported the P. aculeatus, and A. gracilis, are the most abundant

123

328 Hydrobiologia (2011) 666:317 330

communities and hydrology in the Senegal River Estuary.

species among those observed in this study during

Estuarine Coastal and Shelf Science 74: 381 394.

autumn, and have been associated with the Kuroshio

Chen, C.-Y. & C. L. Folt, 2002. Ecophysiological responses to

waters of northern Taiwan (Hsieh et al., 2004; Zuo warming events by two sympatric zooplankton species.

et al., 2006; Lan et al., 2009; Lee et al., 2009).



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