Length Weight and Length-Length Relationships of Nine Native Fish Species from the Yichang Reach of the Middle Yangtze River, China
Length Weight and Length-Length Relationships of Nine Native Fish Species from the Yichang Reach of the Middle Yangtze River, China
Sha Li1,2, Yacheng Hu1,2, Wenjing Li3, Wei Su1,2 and Wei Jiang1,2*
1Chinese Sturgeon Research Institute, China Three Gorges Corporation, Yichang 443100, China
2Hubei Key Laboratory of Three Gorges Project for Conservation of Fishes, Yichang 443100, China
3Institute of Science and Technology, China Three Gorges Corporation, Beijing 100038, China
Sha Li and Yacheng Hu contributed equally to this study.
ABSTRACT
We determined the length-weight relationships (LWRs) and length-length relationships (LLRs) for nine fish species belonging to three families inhabiting the Yichang reach of the middle Yangtze River, China. The samples were collected with gill nets (2×50 m, mesh size: 40 and 60 mm) between November 5th, 2019, and December 31st, 2019. A total of 1252 specimens were used to estimate the related parameters. The LWRs parameters of all nine species were found to be significant (P <0.05). The values of b in LWRs ranged from 2.455 to 3.009. New maximum total length (TL) and standard length (SL) records for two of the nine species were reported, and the first report of LWRs of Xenocypris davidi was provided. The results of our study provided Fish Base with new data and basic biological information for research, management, and conservation of the middle Yangtze River ecosystem.
Article Information
Received 10 June 2022
Revised 15 August 2022
Accepted 14 September, 2022
Available online 01 December 2022
(early access)
Published 31 October 2023
Authors’ Contribution
SL, WJ and YH conceived and designed the research. SL wrote the manuscript. SL analyzed the data with WL. SL, WS and WL carried out the experiment.
Key words
The middle Yangtze River, Native fish, Length–weight relationships, Length–length relationships, Relative body weight
DOI: https://dx.doi.org/10.17582/journal.pjz/20220610080645
* Corresponding author: [email protected]
030-9923/2023/0006-2993 $ 9.00/0
Copyright 2023 by the authors. Licensee Zoological Society of Pakistan.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
With a total length of 6397 km, the Yangtze River is the longest river in China. As the main breeding sites and habitat of fishes, the middle reaches of Yangtze River have eleven spawning grounds for the four major Chinese carp and account for 42.7% of the total spawning scale of the mainstream of the Yangtze River. Determining the length-weight relationships (LWRs) is an effective approach for assessing fish biomass based on the conveniently obtained length data (Liu et al., 2018). A variety of information can be obtained from LWRs, including growth rate, age structure, age at first maturity, and segregation of stocks (Singh et al., 2017). Recently, it has been broadly used in the assessment of fish resources, conservation, and management of fish populations in combination with other environmental and population parameters (Fafioye and Oluajo, 2005; Froese, 2006; Pervin and Mortuza, 2008). Some studies reported on the association between the length and weight of fish in the Yangtze River. However, most of the earlier studies were conducted on the upper reaches or its tributaries, such as the research of 77 fish species in the Chishui River (Liu et al., 2014), 11 fish species in the Yibin River (Li et al., 2015), and two species of Jinshaia sinensis and Zacco platypus in the upper reaches (Wang et al., 2015). However, there is a lack of biological information for most of the freshwater fish species in the middle Yangtze River. The results of our study provided updates and data on nine native fish species for FishBase, as well as basic biological information for research, management, and conservation of the middle Yangtze River ecosystem.
Materials and methods
The fish specimens were collected from the Yichang reach (30°42’-30°24’ N; 111°16’-111°26’ E) of the middle Yangtze River, using a stationary gill net (2×50 m, mesh size: 40 and 60 mm) from November 5th, 2019 to December 31st, 2019. Species were identified in the field; each individual was measured for standard length (SL, mm), total length (TL, mm) to the nearest 1mm, and body weight (W, g) to the nearest 0.1g. FishBase was used to cross-reference all scientific names (Froese and Pauly, 2022). The experiments were approved by the Institutional Review Board on Bioethics and Biosafety of the Chinese Sturgeon Research Institute.
The relationship between length and weight was determined using the expression: W = a×Lb (Froese, 2006), where W represents the body weight (W, g), L is the standard length (SL, mm), a is the intercept of the regression and b is the slope or regression coefficient. A and B parameters of the weight–length relationship were calculated by linear regression analysis based on natural logarithms: ln W = ln a + b×ln L. The relationship between TL and SL was determined using linear regression analysis of TL =a + b×SL (Zhang et al., 2016). To remove outliers, log-log plots within species were performed using SPSS 17.0. The 95% confidence limits (Cl) of a and b parameters were estimated. The coefficient of determination (r2 ) was used to estimate the correlation between W and L. All statistical analyses were considered significant at 5% (P < 0.05).
Relative body weight (Wr) was estimated using the formula: Wr=W/(a*Lb)×100 (Froese, 2006), where W is the body weight (W, g), L is the total length (TL, mm), a and b are the parameters of LWRs.
Results
The present study reports LWRs and LLRs of nine species. LWR parameters, along with the descriptive statistics are given in Table I. LLR parameters along with TL (SL shown in Table I) and Wr are shown in Table II. All regressions were significant (P <0.05), with r2 ranging from 0.886 in Saurogobio dabryi to 0.982 in Xenocypris davidi for LWRs and from 0.956 in S. dabryi to 0.992 in Parabramis pekinensis for LLRs, respectively. For LWRs, the values of parameter b of the regression model varied from 2.455 in Culter alburnus to 3.009 in Pelteobagrus fulvidraco. For LLRs, it ranged from 1.087 to 1.183. The new maximum TL of S. dabryi is 35.9 cm, and new maximum SL is 30.5 cm. The new maximum TL of Rhinogobio typus is 47.0 cm, and new maximum SL is 41.2 cm. The relative Wr of nine species ranged from 59.02 to 67.18.
Discussion
A total of 1252 fish specimens were collected, representing nine species and three families (Tables I and II). The sample size ranged from 22 individuals of Culter alburnus to 473 individuals of Coreius heterodon. LWRs are one of the most commonly used formulas in Fishery Ecology Research (Anderson and Neuman, 1996). The parameter b of LWRs reflects the heterogeneity of growth and development (Froese, 2006). The b value is close to 3 indicated that the growth for length and body weight of fish was expressed as isauxesis (Huang and Chang, 1999; Froese, 2006). When b exceeds 3, it indicates positive allometric growth and stands for high productivity conditions, whereas low productivity areas such as deep water tended to stimulate negative allometric growth (b < 3) (Philip and Mathew, 1996). In this study, except for
Table I. Descriptive statistics and estimated parameters of LWRs (W = a×Lb) for nine fish species, Yichang reach in the middle reaches of the Yangtze River, China.
Family/ Species |
SL (mm) |
TW (g) |
Regression parameters |
|||||
N |
Range |
Range |
a |
aCI95% |
b |
bCI95% |
r2 |
|
Family: Cyprinidae |
||||||||
Coreius heterodon |
473 |
145.2-385.0 |
44-657.5 |
4.64E-05 |
2.92E-05~7.38E-05 |
2.761 |
2.678~2.843 |
0.902 |
Parabramis pekinensis |
76 |
140.4-438.2 |
47.9-1365 |
0.0001 |
4.43E-05~0.000286 |
2.644 |
2.475~2.814 |
0.929 |
Xenocypris davidi1 |
43 |
132.2-285.1 |
45.5-441.1 |
3.54E-05 |
1.82E-05~6.89E-05 |
2.869 |
2.746~2.992 |
0.982 |
Saurogobio dabryi2 |
136 |
155.0-305.6 |
47.1-283.2 |
4.12E-05 |
1.70E-05~0.000102 |
2.741 |
2.573~2.909 |
0.886 |
Rhinogobio typus2 |
100 |
152.4-412.1 |
41.1-577 |
3.96E-05 |
2.07E-05~7.59E-05 |
2.753 |
2.634~2.872 |
0.956 |
Culter alburnus |
22 |
220.0-560.3 |
122.7-1145.5 |
0.000241 |
8.47E-05~0.000687 |
2.455 |
2.273~2.638 |
0.975 |
Family: Bagridae |
||||||||
Pelteobagrus fulvidraco |
37 |
140.3-340.2 |
37.8-406.5 |
1.18E-05 |
3.29E-05~4.21E-05 |
3.009 |
2.769~3.249 |
0.949 |
Mystus macropterus |
32 |
173.4-415.0 |
45.4-562 |
2.89E-05 |
4.89E-05~0.000171 |
2.824 |
2.505~3.143 |
0.916 |
Family: Serranidae |
||||||||
Siniperca chuatsi |
333 |
90.0-410.0 |
26.6-1879 |
2.05E-05 |
1.33E-05~3.16E-05 |
2.997 |
2.914~3.081 |
0.938 |
Table II. TL, Wr and estimated total length-standard length relationships (TL = a + b×SL) parameters for nine fish species, Yichang reach in the middle reaches of the Yangtze River, China.
Family/ Species |
Wr (g) |
TL (mm) |
Regression parameters |
r2 |
||||
Mean |
Range |
Range |
a |
aCI95% |
b |
bCI95% |
||
Family: Cyprinidae |
||||||||
Coreius heterodon 1 |
65.88 |
43.4 -- 104.1 |
172.4-445.3 |
18.006 |
13.02~22.992 |
1.098 |
1.080~1.116 |
0.968 |
Parabramis pekinensis 1 |
64.01 |
35.7 -- 87.5 |
173.0-514.2 |
12.893 |
7.039~18.747 |
1.135 |
1.112~1.158 |
0.992 |
Xenocypris davidi 1 |
59.02 |
31.6 -- 72.2 |
160.3-357.5 |
4.858 |
-4.265~13.982 |
1.181 |
1.141~1.22 |
0.989 |
Saurogobio dabryi 1, 2 |
64.21 |
33.9 -- 81.4 |
195.5-358.9 |
5.72 |
-3.044~14.485 |
1.150 |
1.108~1.193 |
0.956 |
Rhinogobio typus 2 |
64.97 |
32.9 -- 88.6 |
175.2-470.0 |
11.784 |
5.845~17.723 |
1.122 |
1.098~1.146 |
0.989 |
Culter alburnus 1 |
66.00 |
52.3 -- 92.7 |
256.8-622.4 |
16.031 |
-4.737~36.799 |
1.116 |
1.053~1.179 |
0.985 |
Family: Bagridae |
||||||||
Pelteobagrus fulvidraco 1 |
62.48 |
30.1 -- 94.6 |
170.4-391.6 |
17.735 |
1.202~34.268 |
1.087 |
1.009~1.166 |
0.958 |
Mystus macropterus 1 |
67.18 |
43.2 --90.1 |
200.2-474.5 |
-6.358 |
-20.034~7.318 |
1.183 |
1.132~1.233 |
0.987 |
Family: Serranidae |
||||||||
Siniperca chuatsi 1 |
64.66 |
26.0--103.1 |
116.7-462.1 |
7.191 |
4.559~9.823 |
1.121 |
1.107~1.135 |
0.987 |
Wr, relative body weight; TL, total Length; a and b, the parameters for LLR; r2, coefficient of determination; CL, confidence limits. 1 First LLR information. 2 New TL max.
Culter alburnus (b = 2.455), all b values fell within Froese’s (2006) predicted range. In contrast, only Pelteobagrus fulvidraco (b= 3.009) was calculated as isauxesis; the other eight fish species showed negative allometric growth. Hence, the large specimens changed their body shape to become more elongated, or the small specimens were in a better nutritional state when they were sampled (Froese, 2006). Comparing this study to other studies (Ni et al., 2022; Dong et al., 2022), some deviations from parameter b for some species were identified. For example, the b values of Saurogobio dabryi were 3.017 and 2.96 stated by Ni et al. (2022) and Liu et al. (2013), respectively, whereas in this study, the b value is 2.741. This deviation may be because the samples we used to estimate LWRs were only collected in winter when fishes have low feeding activity and low energy. In other words, the fishes are in a basic metabolic condition. Although the collected specimens used to estimate LWRs should theoretically represent entire size classes of the population (Froese, 2006), due to the size-selective properties of nets types, very small individuals of any species rarely occurred in this study. For instance, the minimum SL and W of Saurogobio dabryi, reported by Ni et al. (2022), was 4.5 cm and 0.8 g, respectively, whereas, in this study the minimum SL and W were 15.5 cm and 47.1 g, respectively. The sampling methodology, sampling time, sampling location, and sampling size can all affect the estimation of LWRs values (Froese, 2006; Chen et al., 2017), thus, the LWRs presented in this paper should be limited to the observed length ranges. We need to expand the sampling season and strengthen the sample size collection in future studies.
The Wr of the nine species was significantly less than 100 in this study. In some studies, it was found that when the Wr of an individual or group of fish is less than 100, it might indicate problems like low food availability or high predation pressure (Rypel and Richte, 2008). In order to protect the fishery resources of the Yangtze River, the Chinese government imposed a ten-year ban on fishing in 2020. During our research in 2019, we found new maximum TL and SL records for two of the nine species and provided the first report of LWRs of Xenocypris davidi, which can be used as the background value for assessing the effect of the fishing ban. The findings provided new data for FishBase, and are valuable for further fisheries research, as well as helping to establish conservation and management measures of fish resources in the middle Yangtze River.
Acknowledgment
The authors would like to thank all fishers who collaborated with fish samplings acquisition during fieldwork.
Funding
This work was supported by the National Key R and D Program of China (2016YFC0502210), the Program of the Ministry of Agriculture and Rural Affairs (cjbzhc 2022007), and the Program of Three Gorges Corporation (XN270) .
Data availability statement
The data that support the findings of this study are available from the corresponding author upon reasonable request.
Ethics statement
The experiments were performed in accordance with the guidelines and regulations of the National Institute of Health Guide for the Care and Use of Laboratory Animals.
Statement of conflict of interest
The authors have declared no conflict of interest.
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