生物多样性 ›› 2016, Vol. 24 ›› Issue (3): 304-312. DOI: 10.17520/biods.2015268
熊飞1,*(), 刘红艳1, 段辛斌2,*(), 刘绍平2, 陈大庆2
收稿日期:
2015-10-09
接受日期:
2015-12-11
出版日期:
2016-03-20
发布日期:
2016-04-05
通讯作者:
熊飞,段辛斌
基金资助:
Fei Xiong1,*(), Hongyan Liu1, Xinbin Duan2,*(), Shaoping Liu2, Daqing Chen2
Received:
2015-10-09
Accepted:
2015-12-11
Online:
2016-03-20
Published:
2016-04-05
Contact:
Xiong Fei,Duan Xinbin
摘要:
长鳍吻鮈(Rhinogobio ventralis)为长江上游特有种, 由于过度捕捞和大坝建设, 其种群生存受到极大威胁。为了解三峡工程蓄水后、金沙江一期工程蓄水前该物种的种群动态, 作者利用2007-2009年长江上游江津和宜宾江段调查获取的体长频率数据, 评估了其生长和死亡参数、种群数量及资源利用情况。结果表明, 长江上游长鳍吻鮈渔获群体体长范围为52-250 mm, 体重范围为2.7-307.2 g, 平均体长为150.8 ± 40.7 mm, 平均体重为72.3 ± 49.7 g。江津江段长鳍吻鮈平均体长(168.6 ± 29.5 mm)显著大于宜宾江段(125.6 ± 41.2 mm)。长鳍吻鮈体长-体重关系为: W = 6.06 × 10-6L3.20 (R2 = 0.98, P < 0.01, n = 436)。由体长频率法拟合出渐近体长(L∞)为338 mm, 生长系数(k)为0.24/yr。由Pauly公式、Gunderson和Dygert公式、Jensen公式等3种方法估算出其平均自然死亡系数为0.43。由长度转渔获物曲线估算出江津和宜宾江段长鳍吻鮈的总死亡系数分别为2.26和2.09。江津和宜宾江段长鳍吻鮈资源开发率分别为0.81和0.79, 已超过由Beverton-Holt动态综合模型估算出的最大开发率0.57和0.62。由体长实际种群分析估算出2007、2008和2009年江津江段长鳍吻鮈种群数量分别为68,247、67,432和176,266尾, 平均为103,982尾; 宜宾江段种群数量分别为22,953尾、46,340尾和34,021尾, 平均为34,438尾, 表明江津江段种群数量高于宜宾江段。长鳍吻鮈资源已被过度开发, 建议加强种群动态监测, 延长禁渔期及开展栖息地修复等措施保护这一特有物种。
熊飞, 刘红艳, 段辛斌, 刘绍平, 陈大庆 (2016) 长江上游特有种长鳍吻鮈种群数量和资源利用评估. 生物多样性, 24, 304-312. DOI: 10.17520/biods.2015268.
Fei Xiong, Hongyan Liu, Xinbin Duan, Shaoping Liu, Daqing Chen (2016) Estimating population abundance and utilization of Rhinogobio ventralis, an endemic fish species in the upper Yangtze River. Biodiversity Science, 24, 304-312. DOI: 10.17520/biods.2015268.
江段 Section | 年份 Year | Z | M | F | E |
---|---|---|---|---|---|
江津 Jiangjin | 2007 | 3.01 | 0.43 | 2.58 | 0.86 |
2008 | 1.90 | 0.43 | 1.47 | 0.77 | |
2009 | 2.53 | 0.43 | 2.10 | 0.83 | |
总体 Total | 2.26 | 0.43 | 1.83 | 0.81 | |
宜宾 Yibin | 2007 | 2.41 | 0.43 | 1.98 | 0.82 |
2008 | 1.81 | 0.43 | 1.38 | 0.76 | |
2009 | 1.61 | 0.43 | 1.18 | 0.73 | |
总体 Total | 2.09 | 0.43 | 1.66 | 0.79 |
表1 2007-2009年长江上游长鳍吻鮈的死亡系数和开发率
Table 1 Mortalities and exploitation rates of Rhinogobio ventralis in the Jiangjin and Yibin sections from 2007-2009
江段 Section | 年份 Year | Z | M | F | E |
---|---|---|---|---|---|
江津 Jiangjin | 2007 | 3.01 | 0.43 | 2.58 | 0.86 |
2008 | 1.90 | 0.43 | 1.47 | 0.77 | |
2009 | 2.53 | 0.43 | 2.10 | 0.83 | |
总体 Total | 2.26 | 0.43 | 1.83 | 0.81 | |
宜宾 Yibin | 2007 | 2.41 | 0.43 | 1.98 | 0.82 |
2008 | 1.81 | 0.43 | 1.38 | 0.76 | |
2009 | 1.61 | 0.43 | 1.18 | 0.73 | |
总体 Total | 2.09 | 0.43 | 1.66 | 0.79 |
图4 江津(a)和宜宾(b)江段长鳍吻鮈的相对单位补充量产量(Y′/R)和生物量(B′/R)曲线
Fig. 4 Relative yield per recruit (Y′/R) and biomass per recruit (B′/R) curves of Rhinogobio ventralis in the Jiangjin (a) and Yibin (b) sections
图5 2007-2009年江津(a)和宜宾(b)江段长鳍吻鮈的体长结构实际种群分析
Fig. 5 Length-structured virtual population analyses for Rhinogobio ventralis in the Jiangjin (a) and Yibin (b) sections from 2007-2009
江段 Sections | 年份 Year | 数量 Individuals (尾) | 生物量 Biomass (t) | |||||
---|---|---|---|---|---|---|---|---|
迭代法 Iteration method | Et = 0.5 | Et = 0.8 | 迭代法 Iteration method | Et = 0.5 | Et = 0.8 | |||
江津 Jiangjin | 2007 | 68,247 | 67,447 | 63,097 | 14.17 | 13.70 | 11.13 | |
2008 | 67,432 | 66,719 | 64,478 | 15.55 | 15.04 | 13.46 | ||
2009 | 176,266 | 174,952 | 171,938 | 29.36 | 28.62 | 26.92 | ||
宜宾 Yibin | 2007 | 22,953 | 24,881 | 22,613 | 2.58 | 3.46 | 2.44 | |
2008 | 46,340 | 44,744 | 40,832 | 5.15 | 4.62 | 3.37 | ||
2009 | 34,021 | 37,503 | 32,412 | 6.37 | 8.37 | 5.44 |
表2 不同资源开发率(Et)取值确定最大体长组捕捞死亡系数(Ft)值时长鳍吻鮈的种群数量和生物量估算结果
Table 2 Estimate results of population abundance and biomass of Rhinogobio ventralis based on terminal fishing mortalities (Ft) determined by different exploitation rates (Et)
江段 Sections | 年份 Year | 数量 Individuals (尾) | 生物量 Biomass (t) | |||||
---|---|---|---|---|---|---|---|---|
迭代法 Iteration method | Et = 0.5 | Et = 0.8 | 迭代法 Iteration method | Et = 0.5 | Et = 0.8 | |||
江津 Jiangjin | 2007 | 68,247 | 67,447 | 63,097 | 14.17 | 13.70 | 11.13 | |
2008 | 67,432 | 66,719 | 64,478 | 15.55 | 15.04 | 13.46 | ||
2009 | 176,266 | 174,952 | 171,938 | 29.36 | 28.62 | 26.92 | ||
宜宾 Yibin | 2007 | 22,953 | 24,881 | 22,613 | 2.58 | 3.46 | 2.44 | |
2008 | 46,340 | 44,744 | 40,832 | 5.15 | 4.62 | 3.37 | ||
2009 | 34,021 | 37,503 | 32,412 | 6.37 | 8.37 | 5.44 |
群体 Stock | 体长 Length (mm) | L∞ (mm) | k(/yr) | b | 样本数 Number | 估算方法 Method | 文献 Reference |
---|---|---|---|---|---|---|---|
乌江 Wujiang (1981-1983) | 81-260 | - | - | 2.96 | 112 | 年龄-体长法 Age-length | Zhou & He, 1992 |
江津 | 100-280 | 269 | 0.48 | 3.03 | 443 | 年龄-体长法 Age-length | Duan et al, 1991 |
长江上游 Upper Yangtze River (2005-2007) | 75-236 | 299 | 0.24 | 3.21 | 546 | 年龄-体长法 Age-length | 辛建峰, 2010 |
合江 Hejiang (1998-2001) | 81-240 | 316 | 0.30 | 3.15 | 445 | 年龄-体长法 Age-length | 张松, 2003 |
木洞 Mudong (1998-1999) | - | 305 | 0.31 | 3.07 | 570 | 年龄-体长法 Age-length | Deng & He, 2005 |
丽江 | 101-263 | 279 | 0.33 | 3.01 | 161 | 年龄-体长法 Age-length | Bao et al, 2009 |
江津和宜宾 Jiangjin and Yibin (2007-2009) | 52-250 | 338 | 0.24 | 3.20 | 436 | ELEFANⅠ | This study |
表3 长鳍吻鮈种群参数估算结果比较
Table 3 Comparison of estimated population parameters of Rhinogobio ventralis
群体 Stock | 体长 Length (mm) | L∞ (mm) | k(/yr) | b | 样本数 Number | 估算方法 Method | 文献 Reference |
---|---|---|---|---|---|---|---|
乌江 Wujiang (1981-1983) | 81-260 | - | - | 2.96 | 112 | 年龄-体长法 Age-length | Zhou & He, 1992 |
江津 | 100-280 | 269 | 0.48 | 3.03 | 443 | 年龄-体长法 Age-length | Duan et al, 1991 |
长江上游 Upper Yangtze River (2005-2007) | 75-236 | 299 | 0.24 | 3.21 | 546 | 年龄-体长法 Age-length | 辛建峰, 2010 |
合江 Hejiang (1998-2001) | 81-240 | 316 | 0.30 | 3.15 | 445 | 年龄-体长法 Age-length | 张松, 2003 |
木洞 Mudong (1998-1999) | - | 305 | 0.31 | 3.07 | 570 | 年龄-体长法 Age-length | Deng & He, 2005 |
丽江 | 101-263 | 279 | 0.33 | 3.01 | 161 | 年龄-体长法 Age-length | Bao et al, 2009 |
江津和宜宾 Jiangjin and Yibin (2007-2009) | 52-250 | 338 | 0.24 | 3.20 | 436 | ELEFANⅠ | This study |
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