Spatial Niche Breadth and Overlap of Main Nekton Species in
Autumn Near Dongtou Island
Dongrong Zhang
1,2*
, Lihong Chen
1
, Hengtao Xu
1
, Weihua Feng
1
, Zhifu Wang
1
, Ling Peng
1
and Jian Qian
1
1
Key Laboratory of Engineering Oceanography, Second Institute of Oceanography, MNR, Hangzhou, China
2
State Key Laboratory of Marine Geology, Tongji University, Shanghai, China
Keywords:
Spatial Niche Breadth, Niche Overlap, Nekton Species, Dongtou Island.
Abstract: As the basic theory in community ecology, research on the niche breadth and niche overlap is of great
significance to understand the position, function of various species and explain the mechanism of interspecific
coexistence and competition. We found the main nekton were 5 species of fish, 5 species of shrimp and 2
species of crab in autumn in the sea area near Dongtou Island (DTI). The dominant species are mainly
Harpodon nehereus, Portunus trituberculatus and Oratosquilla oratoria, in which the Harpodon nehereus
and Portunus trituberculatus had the high degree of aggregation phenomenon in DTI. The niche breadth of
main nekton ranged from 1.08-2.06, and the broad niche species were shrimp Solenocera crassicornis (2.06)
and fish Harpodon nehereus (2.03), which is negative correlated with the index of aggregation intensity. The
niche overlap index (Q
ik
) of main nekton were 66 pairs of species, in which, 32 pairs whose overlap indices
were Q
ik
> 0.6 and 23 pairs whose overlap indices were 0.6 Q
ik
0.3. The niche breadth and overlap of main
nekton communities were highly positive correlated. The niche overlap may be a necessary factor for
interspecific competition between the nekton species. The competition among species may also be affected
by the distribution and supply of resources in the coexistence area. The habitat homogenization of nekton
community should be considered in studying the niche and ecological restoration.
1 INTRODUCTION
The niche theory was first proposed and defined by
Grinnell (1917; 1924), and then Elton (1927) and
Hutchinson (1991) successively put forward
nutrition niche, multi-dimensional super volume
niche and other theories, which improved and
developed the niche theory. The niche theory has
been widely used in the study of species community
structure and function, community interspecific
relationship, biodiversity and other aspects. The
division of trophic level, functional group and niche
has been highly applied to the study of aquatic
ecosystem (especially in marine ecosystems) in
recent years. Yu et al. (2010) showed that niche
breadth could more comprehensively reflect the
evenness and change of species biomass at different
scales in the central and southern Yellow Sea; Li et
al. (2013) believed that the niche of dominant fish
species in the Yangtze River Estuary and adjacent
waters had obvious seasonal variation and spatial
movement trend. Li et al. (2017) found that the niche
overlap is different among species and has the
relatively independent distribution characteristics in
Wenzhou Bay.
Dongtou Island (DTI) is rich in islands and
marine resources, which is located in the estuarine
area (Oujiang) in the southeastern part of the East
China Sea. The sufficient baiting food brought by
river runoff supply for nekton to feed, spawn, breed
here (Day et al., 2012). There may be overlap and
interspecific competition in the niche of main nekton
species. Therefore, it is necessary to study the niche
of main nekton in estuarine waters. The research on
the nekton in Oujiang Estuary (near DTI) and its
adjacent waters mainly focused on the community
composition, community structure and its
relationship with environmental factors (Xu, 2008,
2009; Yan et al., 2018, 2019). And, Li et al. (2013)
studied the niche and interspecific association and
functional group of major nekton in the spring of
Wenzhou Bay. Zhang et al. (2019) found the niche
breadth values differed greatly and showed
1268
Zhang, D., Chen, L., Xu, H., Feng, W., Wang, Z., Peng, L. and Qian, J.
Spatial Niche Breadth and Overlap of Main Nekton Species in Autumn Near Dongtou Island.
DOI: 10.5220/0011508000003443
In Proceedings of the 4th International Conference on Biomedical Engineering and Bioinformatics (ICBEB 2022), pages 1268-1272
ISBN: 978-989-758-595-1
Copyright
c
2022 by SCITEPRESS Science and Technology Publications, Lda. All rights reserved
significant positive correlation with IRI in Yueqing
Bay. However, there is no relevant report on the
niche breadth and overlap of main zooplankton
species in autumn in the sea area around DTI.
This paper studied the niche breadth and
overlapping characteristics of the main nekton
communities in the coastal waters of DTI in autumn,
which can objectively reflect the interspecific
relationship and community structure characteristics
of the main nekton communities in the coastal
waters, reveal the ecological relationship between
different species, avoid interspecific competition due
to lack of common resources, and maintain
ecological balance. The purpose is to provide
scientific basis for the research and sustainable
utilization of the marine ecosystem.
2 MATERIALS AND METHODS
2.1 Study Area
DTI is located in the southeast coast of the East
China Sea, whch is rich in marine resources and has
many bay shorelines, and is the second largest fishing
ground in Zhejiang (Fig. 1). As the second largest
river in Zhejiang Province, the Oujiang River feeds
fresh water into the sea near DTI all year round,
making the sea rich in bait organisms, which is
favorable for fish and other nekton to feed and spawn
here.
Figure 1: Study area and sampling stations in DTI, China.
2.2 Sample Collection and Data
Analysis
The research data was collected through the survey
cruise with 10 sampling sites in Autumn (October) of
2019 in the waters around DTI (Fig. 1) (Zhang et al.,
2021). We employed an 8-m wide, mouth-opening
bottom trawl, with 20 mm cod-end mesh, was towed
in mean speed of 3.7 kn for 25 min on average in
stepped tows to collect samples. And, we
standardized the original survey data of nekton
before data analysis.
The dominant species was determined by the
Index of Relative Importance (IRI): IRI = (W + N) ×
F (1) (Pinkas et al., 1971). W is the percentage of a
species' biomass in the total biomass, N is the
percentage of a species' abundance in the total
abundance, F is the frequency of a species'
occurrence in all stations. The species with IRI
1000 were the dominant species; The species with
IRI value of 100-1000 were important species. We
selected the species with IRI100 and the frequency
of occurrence higher than 50% as the main nekton of
the study.
The aggregation intensity of main nekton species
was determined by the clumping index : I = S
2
/x 1
(2); and mean crowding index : x* = (S
2
x + x
2
)/ x
(3) (x is the mean of the total number of species, S
2
is
the variance) (Lloyd, 1967).
The niche breadth was calculated by Shannon
Wiener index (Shannon and Wiener, 1963):
𝐵
=
𝑃

𝑙𝑛𝑃


(4). According to the value of
B
i
, species can be divided into broad niche species
(B
i
≥2.0), medium niche species (2.0>B
i
≥1.0) and
narrow niche species (1.0>B
i
>0) (Doledec et al.,
2000). The niche overlap index was calculated by
Pianka index (Pianka, 1973):
𝑄

=
𝑃

𝑃

/
𝑃


𝑃



(5). r is the
number in all sampling station; P
ij
and P
kj
represent
the proportion of individual number of species i and
species k in station j to the total number of species. B
i
is the niche breadth with the value range in r. The
peak B
i
value means the high niche breadth. Q
ik
represents the niche overlap value with the range in
0˗1. Q
ik
> 0.3 is regarded as significant overlap, and
Q
ik
> 0.6 is regarded as highly significant overlap
(Krebs, 1999).
3 RESULTS & DISCUSSION
Our results showed that the main nekton in the sea
area near DTI included 5 species of fish (Harpodon
nehereus, Coilia nasus, Takifugu xanthopterus,
Chrysochir aureus, Collichthys lucidus), 5 species of
shrimp (Solenocera crassicornis, Palaemon gravieri,
Exopalaemon carinicauda, Oratosquilla oratoria,
Exopalaemon annandalei) and 2 species of crab
(Charybdis japonica, Portunus trituberculatus) in
Spatial Niche Breadth and Overlap of Main Nekton Species in Autumn Near Dongtou Island
1269
autumn (Table 1). The dominant species are mainly
Harpodon nehereus, Portunus trituberculatus and
Oratosquilla oratoria. As the aggregation intensity
of dominant species is an indicator reflecting the
spatial distribution of nekton. When it is positive, it
means that the spatial pattern of the species is non-
random to a greater extent, i.e. there is a certain
aggregation, and the high positive value means the
high aggregation intensity. We found that the
Harpodon nehereus and Portunus trituberculatus
were captured in the all sampling stations, implied
that there is a large number of aggregation
phenomenon of these two species in the sea area,
which also can be reflected from the aggregation
intensity index (Table 1).
Comparison with the aggregation intensity index,
the spatial niche reflects the evenness of species
spatial distribution (Yu et al., 2010), and it is a
negative correlated with the index of aggregation
intensity (I, x*). For instance, Portunus
trituberculatus and Oratosquilla oratoria were the
relatively low niche species, while their indices of
aggregation intensity (I=15342.02, 15771.32;
x*=20701.22, 20763.66) were extremely high (Table
1, Fig. 2). As the niche theory is one of the basic
theories to explain the mechanism of interspecific
coexistence and competition in communities. The
calculation of niche breadth and niche overlap is of
great significance to understand the position and
function of various species in the community and the
relationship among species (Yu et al., 2010; Zhang et
al., 2019). Niche breadth is an important index to
evaluate the environmental adaptability and resource
utilization of species, and its value depends on the
ecological adaptability, interspecific competitiveness
and distribution range of species (Soberon and
Peterson, 2005). We found that the niche breadth of
main nekton ranged from 1.08-2.06 in DTI (Fig. 2).
The broad niche species were shrimp Solenocera
crassicornis (2.06) and fish Harpodon nehereus
(2.03), while other species were the medium niche
species. The niche breadth segmentation is not
obvious, contrary to Zhang et al (2020). The larger
the value of niche breadth, the higher the ability of
the species to use its resources, and the species could
more easily adapt to environmental changes and
broadened the scope of activities (Liu et al., 2018).
The niche breadth of Harpodon nehereus was
relatively high (2.03) with the high proportion of
quantity (Table 1), indicated the species has the
widest distribution and is more adaptable to
environmental changes, able to make better use of
environmental resources and at an absolute
advantage in the competition in the investigated sea
area.
The overlap value of ecological niches reflects
the similarity and competition between species for
the utilization of same resource (Liu et al., 2018;
Wathne et al., 2000). When the overlap value was
greater than 0.6, the overlap between species pairs
was significant, and the overlap between species
pairs and stations was high (Wathne et al., 2000). In
the sea area near DTI, the results indicated the niche
overlap index (Q
ik
) of main nekton were 66 pairs of
species, in which, 32 pairs whose overlap indices
were Q
ik
> 0.6 (accounting for 48.48% of the total
species pairs) and 23 pairs whose overlap indices
were 0.6 Q
ik
≥0.3 (accounting for 34.85% of the
total species pairs), and only 11 pairs whose overlap
indices were < 0.3
(accounting for 16.67% of the total
species pairs) (Table 2). The niche breadth and
overlap of the main nekton communities were highly
positive correlated (Fig. 2, Table 2). For example, the
broad niche species shrimp Solenocera crassicornis
and fish Harpodon nehereus were significantly
overlapped with most species. Actually, niche
overlap may be a necessary factor for interspecific
competition between the nekton species. For
instance, the niche overlap of crab Portunus
trituberculatus and fish Collichthys lucidus is
significant (Q
ik
= 0.99) (Wathne et al., 2000),
although there are some differences in the habitats
between sub-benthic Collichthys lucidus and benthic
Portunus trituberculatus, their competition in food
resources is fierce as they both feed on benthos.
Nevertheless, the niche overlap of Solenocera
crassicornis and Exopalaemon annandalei is not
significant (Q
ik
= 0.18), due to the fact that the
feeding spectrum of Solenocera crassicornis are
more than that of Exopalaemon annandale. As a
result, we believed the overlap value and competition
degree of interspecific pairs are not necessarily
positive correlated. The competition among species
may also be affected by the distribution and supply
of resources in the coexistence area. Furthermore, the
high spatial niche overlap in this study also reflects
the reality of the high degree of habitat homogeneity
in the nekton community in DTI, which should be
considered in ecological restoration.
ICBEB 2022 - The International Conference on Biomedical Engineering and Bioinformatics
1270
Table 1: The Index of Relative Importance (IRI), index of aggregation intensity of main nekton species in DTI.
Nekton species Code N W F IRI I x*
Solenocera crassicornis SC 3.75 0.24 90.00 359.25 365.82 1438.97
Harpodon nehereus HN 29.77 19.93 100.00 4970.16 4918.26 13432.16
Charybdis japonica CJ 2.01 2.52 90.00 407.29 900.78 1474.41
Coilia nasus CN 1.36 4.19 80.00 443.99 480.45 869.97
Palaemon gravieri PG 1.93 0.14 70.00 145.01 784.42 1336.05
Takifugu xanthopterus TX 0.95 1.46 70.00 169.37 436.10 709.15
Exopalaemon
ca
r
inicauda
EC 1.87 0.38 70.00 157.84 1065.73 1601.38
Chrysochir aureus CA 1.34 1.35 60.00 161.66 1001.63 1384.85
Portunus trituberculatus PT 18.74 19.29 100.00 3803.04 15342.02 20701.22
Oratosquilla oratoria OO 17.46 7.34 80.00 1984.02 15771.32 20763.66
Collichthys lucidus CL 4.45 4.72 60.00 550.33 5586.78 6858.89
Exopalaemon
annandalei
EA 2.17 0.07 70.00 156.53 3191.12 3810.50
Figure 2: Variation of niche breadth of main nekton species in DTI. The codes are same to Table 1.
Table 2: Niche overlap index of main nekton species in DTI. The codes are same to Table 1.
Q
ik
H
N
C
N
T
X
CA CL S
C
PG E
C
OO EA CJ P
T
H
N
1.00
C
0.88 1.00
T
X
0.52 0.54 1.00
CA 0.56 0.34 0.24 1.00
CL 0.82 0.73 0.37 0.46 1.00
S
C
0.83 0.78 0.70 0.45 0.46 1.00
PG 0.76 0.75 0.62 0.20 0.81 0.64 1.00
E
C
0.75 0.70 0.40 0.34 0.68 0.75 0.85 1.00
OO 0.82 0.66 0.39 0.60 0.96 0.52 0.78 0.74 1.00
EA 0.27 0.40 0.08 0.54 0.25 0.18 0.18 0.14 0.20 1.00
CJ 0.68 0.35 0.41 0.85 0.57 0.61 0.44 0.56 0.75 0.12 1.00
P
T
0.83 0.70 0.38 0.52 0.99 0.48 0.78 0.66 0.98 0.22 0.65 1.00
4
CONCLUSIONS
The main nekton in the sea area near DTI included 5
species of fish, 5 species of shrimp and 2 species of
crab in autumn. The dominant species are mainly
Harpodon nehereus, Portunus trituberculatus and
Oratosquilla oratoria, in which the Harpodon
nehereus and Portunus trituberculatus had the high
degree of aggregation phenomenon in the sea area.
The niche breadth of main nekton ranged from 1.08-
2.06, and the broad niche species were shrimp
Solenocera crassicornis (2.06) and fish Harpodon
2,06
2,03
1,73
1,72
1,64
1,63
1,45
1,37
1,28
1,21
1,17
1,08
0,00
0,50
1,00
1,50
2,00
2,50
SC
HN
CJ
C
N
PG
TX
EC
CA
PT
OO
CL
EA
Niche breadth
Main nekton species
Spatial Niche Breadth and Overlap of Main Nekton Species in Autumn Near Dongtou Island
1271
nehereus (2.03), which is negative correlated with
the index of aggregation intensity. The niche overlap
index (Q
ik
) of main nekton were 66 pairs of species,
in which, 32 pairs whose overlap indices were Q
ik
>
0.6 and 23 pairs whose overlap indices were 0.6 Q
ik
≥0.3. The niche breadth and overlap of the main
nekton communities were highly positive correlated.
The niche overlap may be a necessary factor for
interspecific competition between the nekton
species. The competition among species may also be
affected by the distribution and supply of resources
in the coexistence area. Next, we should consider the
habitat homogenization of nekton community in
studying the niche and ecological restoration.
ACKNOWLEDGMENTS
The authors are grateful to National Natural Science
Foundation of China (Grant number 41776119) for
the financial support.
REFERENCES
Day, J. W., Crump, B. C., Kemp, W. M., et al. (2012)
Estuarine ecology. Wiley-Blackwell, New Jersey.
Doledec S, Chessel D, Gimaret-Carpenentier C. (2000)
Niche separation in community analysis: A new
method. Ecology, 81(10): 2914-2927.
Elton C S. (1927) Animal Ecology. London: Sedgwick &
Jackson.
Grinnell J. (1917) The niche-relationships of the California
thrasher. The Auk, 34(4): 427-433.
Grinnell J. (1924) Geography and evolution. Ecology,
5(3): 225-229.
Hutchinson G E. (1991) Population studies: Animal
ecology and demography. Bulletin of Mathematical
Biology, 53(1-2): 193-213.
Krebs C J. (1999) Ecological Methodology. New York:
Harper Collins Publishers.
Li C N, Shui Y Y, Tian K, et al. (2017) A study of niche
and interspecific association and functional group of
major nekton in the spring of Wenzhou Bay. Acta
Ecologica Sinica, 37(16): 5522-5530. (in Chinese)
Li X S, Yu Z H, Sun S, et al. (2013) Ecological niche
breadth and niche overlap of dominant species of fish
assemblage in Yangtze River estuary and its adjacent
waters. Chinese Journal of Applied Ecology, 24(8):
2353-2359. (in Chinese)
Liu R H, Chang B, Rong C Y, et al. (2018) Niche of main
woody plant populations of Pterocarya stenoptera
community in riparian zone of Lijiang River, China.
Chinese Journal of Applied Ecology, 29 (12) : 3917-
3926. (in Chinese)
Lloyd. (1967) Improvements in or relating to fuel element
end closure. Journal of Environmental Health, 70(10):
40-46.
Pianka E R. (1973) The structure of lizard communities.
Annual Review of Ecology and Systematics, 4: 53-74.
Pinkas, L., Oliphant, M. S., Iverson, I. L. K. (1971) Food
habits of albacore, bluefin tuna, and bonito in
California waters. Fish Bulletin, 152: 1-105.
Shannon C E, Wiener W. (1963) The Mathematical Theory
of Communication. Chicago, IL, USA: University of
Illinois Press.
Soberon J, Peterson A T. (2005) Interpretation of models
of fundamental ecological niches and speciesʹ
distributional areas. Biodiversity Informatics, 2: 1-10.
Wathne J A, Haug T, Lydersen C. (2000) Prey preference
and niche overlap of ringed seals Phoca hispida and
harp seals P. groenlandica in the Barents Sea. Marine
Ecology Progress Series, 194: 233-239.
Xu, Z. L. (2008) Spatial-temporal distribution of fish
density in the Oujiang estuary during summer and
autumn. Acta Zoologica Sinica, 54(6): 981-987. (in
Chinese)
Xu, Z. L. (2009) Relationship of crab density distribution
with environment in the Oujiang Estuary during
summer and autumn. Journal of Fisheries of China,
33(2): 237-244. (in Chinese)
Yan, W. C., Song, W. H., Yu, C. G., et al. (2018) Studies on
fish diversity and community structure in spring and
autumn in Oujiang Estuary. Transactions of
Oceanology and Limnology,
6: 132-141. (in Chinese)
Yan, W. C., Song, W. H., Yu, C. G., et al. (2019)
Community structure of shrimps and crabs in spring
and autumn in Oujiang River Estuary. Journal of
Shanghai Ocean University, 28(1): 134-144. (in
Chinese)
Yu Z H, Jin X S, Li X S. (2010) Analysis of ecological
niche for major fish species in the central and southern
Yellow Sea. Progress in Fishery Sciences, 31(6): 1-8.
(in Chinese)
Zhang Dongrong, Xu Hengtao, Wang Zhifu, et al. (2021)
Community structure of nekton in the waters around
Dongtou Island in Autumn of 2019. IOP Conf. Series:
Earth and Environmental Science, 734: 012001.
Zhang L L, Jiang R J, Yin R, et al. (2019) Spatial niche and
differentiation of major nekton species in Yueqing
Bay, Zhejiang, China. Chinese Journal of Applied
Ecology, 30(11): 3911-3920. (in Chinese)
Zhang L L, Zhou Y D, Jiang R J, et al. (2020) Spatial niche
of major fish species in spring in the coastal waters of
central and southern Zhejiang Province, China.
Chinese Journal of Applied Ecology, 31(2) : 659-666.
(in Chinese)
ICBEB 2022 - The International Conference on Biomedical Engineering and Bioinformatics
1272