摘 要:【目的】研究特克斯河新疆高原鳅系统生物学特性,为其种质资源开发利用奠定基础,夯实新疆特有鱼类基础生物学数据。【方法】2022~2023年在特克斯河采集新疆高原鳅488尾样本,运用经典生物学方法鉴定其形态特征,分析其年龄、生长等生物学特性。【结果】新疆高原鳅体延长,头略扁平,头后稍隆起,吻钝、口下位较宽,背廓呈弧状,前躯粗圆,呈纺锤形,尾柄起点处的宽度明显大于尾柄高,皮肤光滑,无鳞,侧线完全。体长和体重均不符合正态分布,年龄均值为(1.74±0.77)+,最大年龄为4+,最小年龄为0+,其中优势年龄个体为2+,占46.80%。体长和体重相关方程为:W = 1.15 × 10-5L2.968(R2 = 0.92);生长方程为:Lt = 161.13 (1-e-0.32 (t + 0.20) )和Wt = 40.82 (1-e-0.32 (t + 0.20) )2.968,渐近体长L∞ = 161.13 mm,渐近体重W∞ = 40.82 g,t0 = -0.20,k = 0.32,ti = 3.23;丰满系数为k = 1.21。【结论】新疆高原鳅为高原冷水性鱼类,体形呈纺锤形,特克斯河中处于匀速生长,年龄组成小,适应性强,生长性状稳定,数量多,极为适口的肉食性鱼类饵料生物,具有较大的开发利用价值和生态意义,特克斯河优势土著鱼类。
关键词:特克斯河;新疆高原鳅;形态特征;年龄与生长
中图分类号:S9 文献标志码:A 文章编号:1001-4330(2024)10-2576-07
收稿日期(Received):2024-04-07
基金项目:农业农村部财政专项“西北地区重点水域渔业资源与环境调查”
作者简介:古丽旦·赛力克波勒(2000-),女,新疆昭苏人,硕士研究生,研究方向为渔业生态学,(E-mail)17797894248@163.com
通讯作者:陈生熬(1980-),男,青海西宁人,教授,博士,硕士生/博士生导师,研究方向为渔业资源与环境,(E-mail)chenshengao@163.com
0 引 言
【研究意义】新疆高原鳅Triplophysa strauchii(Kessler 1874)属高原鳅属(Triplophysa),是新疆高原山区分布最多的冷水性小型鱼类之一,分布范围广,资源量丰富,为该水域内肉食性鱼类极为适口的饵料生物,具有一定的开发利用价值和生态意义[1-2]。【前人研究进展】关于特克斯河相关文献主要集中在特克斯河山口引水枢纽的引水防沙设计及试验[3]、水质特点[4-6]和水能开发利用等相关研究[7-8],特克斯河中仅有对伊犁裂腹鱼生物学特性[9]和斑重唇鱼生态学特征[10]等鱼类研究,但对新疆高原鳅研究仅有郭焱等[11-12]的赛里木湖和柴窝堡湖的生物学特性研究。【本研究切入点】近年来生物安全和种质保护研究极为重要,尤其对于新疆跨境河流鱼类多样性的研究亟待开展调查保护,鉴于对伊犁河水系高原鳅属鱼类研究文献较少,尤其是特克斯河新疆高原鳅系统生物学的研究未见报道。需研究特克斯河新疆高原鳅系统生物学特性。【拟解决的关键问题】2022~2023年采集特克斯河新疆高原鳅,鉴定分析特克斯河新疆高原鳅形态特征及其年龄与生长等生物学特性,研究该鱼在特克斯河的适应行为,为保护其种质资源、高原鳅属鱼类的分类及其生物学研究积累理论数据。
1 材料与方法
1.1 材 料
2022~2023年,在新疆伊犁河水系特克斯河(80°96′E,42°95′N,海拔1 746.88 m)使用流刺网和地笼(网目2a = 2 cm)等工具按4季采集新疆高原鳅样本488尾。
1.2 方 法
依据殷名称[13]现场对新疆高原鳅的14个可量性状和21个框架距离指标进行测量(长度精确至0.01 mm,质量精确至0.01 g),并解剖采集微耳石,清洗后用离心管固定,带回实验室处理。
依据殷名称[13],利用体长和体重关系式W = aLb(a和b是常数)拟合生长类型。
利用公式K=(W/L3)×100,W为体重(g),L为体长(mm),求丰满度。
采用Von Bertalanffy(1938)方程[13]Lt=Lt(1-e-k(t-t0)),Wt=Wt(1-e-k(t-t0))。
1.3 数据处理
采用Spss18.0和Origin9.0,并用均值和标准差(Mean±S.D.)表示。
2 结果与分析
2.1 新疆高原鳅外形特征
研究表明,新疆高原鳅外形纺锤形,身体呈淡棕色,背侧为灰褐色,并布有不规则的小黑斑。背鳍和尾鳍有较整齐的小斑纹。头部较小,口裂小而圆;体延长,头后稍隆起,背廓呈圆弧状,前躯粗圆,尾柄较细;皮肤光滑,没有鳞片;眼睛也相对较大。在14个可量性状中体高大于体宽,头长大于吻长,标准差中仅全长和体长较大,其他均较小。图1,表1
在其他可量性状的比值中,该鱼头部较小、眼睛较大、尾柄又细又长。表2
2.2 新疆高原鳅可量性状指标测定
研究表明,新疆高原鳅体长范围为(51.63~137.09) mm,均值为(88.69±15.65) mm(图2a);体重为(1.18~22.99) g,均值为(7.69±4.58) g(图2b),体高为(5.30~21.50) mm,均值为(13.63±3.01) mm(图2c);体宽为(5.30~21.50) mm,均值为(10.85±2.31) mm(图2d);头长为(9.97~28.82) mm,均值为(19.36±3.37) mm(图2e);年龄为0+~4+,均值为1.74±0.77+,其中2+为优势年龄个体,占46.80%;0+占2.40%;1+占36.60%;3+占12.60%;4+仅1.60%(图2f)。图2
2.3 新疆高原鳅体长-体重关系
研究表明,采用W=aLb拟合新疆高原鳅体重与体长的关系式,新疆高原鳅的体长-体重关系方程为W = 1.148 × 10-5L2.968(R2 = 0.917),b值与3差异不显著(P gt; 0.05),属匀速生长类型。图3
2.4 新疆高原鳅肥满度
研究表明,利用公式K=(W/L3)×100统计,分析新疆高原鳅肥满度,波动范围在0.12~1.89,均值为1.21。
2.5 新疆高原鳅生长方程
研究表明,得新疆高原鳅L∞ = 161.13 mm,W∞ = 40.82 g,t0 = -0.20,k = 0.32,ti = 3.23。
求得渐近方程:
Lt = 161.13 (1-e-0.32 (t + 0.20) ).
Wt = 40.82 (1-e-0.32 (t + 0.20) )2.968.
对生长方程一阶求导,得到生长速度方程:
dl/dt = 51.08e-0.32 (t + 0.20).
dW/dt = 121.15e-0.32 (t + 0.20) (1-e-0.32 (t + 0.20))1.968.
对生长方程进行二阶求导,得到生长加速度方程:
d2l/dt2 = -16.19e-0.32 (t + 0.20).
d2W/dt2 = 12.18e-0.32 (t + 0.20) (1-e-0.32 (t + 0.20) )0.968 (2.968e-0.32 (t + 0.20) - 1).
新疆高原鳅体长与体重生长曲线均随年龄增长呈上升趋势;体长生长速度随年龄呈下降趋势,体重生长速度3龄前随年龄呈上升趋势,而后呈下降趋势;体长生长加速度随年龄呈现上升趋势,体重生长加速度随年龄呈现下降趋势,体长生长加速度与体重生长加速度在2.5龄处相交。新疆高原鳅ti为3.23,所对应的体长和体重分别为106.89 mm和12.07 g。图4
3 讨 论
3.1 鱼类形态学研究是反映鱼类形态和生长的重要指标,同时也是其分类的重要依据之一[14-16]。研究中新疆高原鳅呈纺锤形,躯体呈淡棕色,背侧为灰褐色,并布有不规则的小黑斑,与赛里木湖新疆高原鳅[11]外形特征上基本一致,无显著差异;但生长性状上最大体长137.09 mm,与赛里木湖群体最大体长161 mm差异极显著(P lt; 0.05);最大体重22.99 g,与赛里木湖群体最大体重59 g差异极显著(P lt; 0.05)。特克斯河是海拔3 000 m的寒冷水系,而赛里木湖是海拔2 073 m的内陆高盐湖泊,2个水系明显相差较大,且特克斯河年均径流量80×108 m3随季节变化较大[9],而赛里木湖是封闭的高山湖类型,水位相对稳定[11],不同水域中饵料生物组成也不同,因此导致2个不同地理群体生长有差异。刘璐等[17]对不同地理群体的褐菖鲉形态学进行比较,发现不同生境差异下群体间存在分化;张永杰等[18]对新疆裸重唇鱼不同地理种群形态研究,不同生境差异导致群体形态差异显著,与不同地理群体的新疆高原鳅形态存在显著差异结果一致,因此不同栖息水域环境会导致鱼类形态学性状的差异。
3.2 鱼类在生长过程中体长和体重的生长极其重要,对于鱼类生态学基础理论研究、鱼类生长的表达和发展渔业生产中其相关系数有重要意义[19-21]。在W = a × Lb中,a值为条件因子,可用来判断饵料基础、水文等环境因子[22],在一定条件下可以表示肥满度[23];b值通常在2.5~4.0之间[24-25],越接近于3,鱼类在整个生长过程中,其体长与体重的生长均匀且较为理想。试验研究中特克斯河新疆高原鳅W = 1.148 × 10-5L2.968,赛里木湖新疆高原鳅[11]W = 8.225×10-3L3.112,对比2个群体a值,发现特克斯河群体a值显著低于赛里木湖群体(P lt; 0.05),则赛里木湖群体丰满度较特克斯河好,与试验研究当中的肥满度研究比值发现,特克斯河群体肥满度1.21也低于赛里木湖群体肥满度1.26,与a值的结论相一致,可能与赛里木湖钩虾饵料丰富,食物保障较好,水生生物组成单一有关[26];对于b值而言,两者均为匀速生长,但赛里木湖群体生长匀速度更优,与赛里木湖是封闭的高山盐碱湖水,水域中无凶猛鱼类有关。塔里木河叶尔羌高原鳅[27]W = 4×10-6L3.333 1,肥满度为1.48,对比发现叶尔羌高原鳅丰满度以及生长匀速均较新疆高原鳅好,可能是种类和生境差异引起的,如特克斯河地处高海拔(3 000 m)冰雪融水补给型河流,年均水温不超过15℃[6],而塔里木河为低海拔(800~1 000 m),年均水温19℃[28],2个水域明显差异较大,饵料系数组成不同等导致2种高原鳅生长差异明显。
Von Bertalanffy生长方程可准确地描述种群的生长特性,被广泛地用于描述鱼类的生长特征[29-31]。比较新疆高原鳅Von Bertalanffy方程,其L∞ = 161.13 mm、W∞ = 40.82 g、t0 = -0.20、ti = 3.23,均显著高于叶尔羌高原鳅[27]L∞ = 108.71 mm、W∞ = 24.49 g、t0= -1.72、ti = 1.83,叶尔羌高原鳅种群趋于小型化,存在早熟现象,而新疆高原鳅生长较为缓慢,与2个水体的温度、海拔以及饵料丰度差异有关[6,28,32]。与西藏哲古措异尾高原鳅[33]相比较,其L∞ = 138.91 mm、W∞ = 28.18 g、t0 = -2.89显著小于新疆高原鳅,而ti = 3.67显著大于特克斯河群体(ti = 3.23)(P lt; 0.05),是由于西藏哲古措平均水温4℃显著低于特克斯河水温15℃,且西藏地处高海拔高寒地区,低水温和冰冻时间较长[33],导致其生长缓慢,性成熟较晚。
4 结 论
特克斯河是伊犁河的主流,典型的高海拔冰雪融水补给型河流,新疆高原鳅是特克斯河主要冷水性土著鱼类,其体延长,头后稍隆起,背廓呈弧状,前躯粗圆,身体呈淡棕色,背侧为灰褐色,并布有不规则的小黑斑,与其他群体差异不显著(P gt; 0.05),体长均值为(88.69±15.65) mm,体重均值为(7.69±4.58) g,与其他群体差异显著(P lt; 0.05)。年龄结构中,其年龄范围在0+ ~ 4+,其中优势年龄个体为2+。体长和体重拟合回归方程W = 1.148 × 10-5L2.968(R2 = 0.917),体长和体重相关性较大,匀速生长,肥满度一般。特克斯河地处海拔高,水温低,生物量随季节性变化比较大,使得新疆高原鳅拐点年龄偏大,生长缓慢,成熟晚。新疆高原鳅在该水域分布广泛,数量较多,成为肉食性鱼类的适口性饵料,并表现出较强的高寒水系适应性,具有较大的开发利用价值。
参考文献(References)
[1]武云飞,吴翠珍. 青藏高原鱼类[M].成都: 四川科学技术出版社, 1982.
WU Yunfei, WU Cuizhen. The fishes of the Qinghai-Xizang Plateau[M].Chengdu: Sichuan Scientific amp; Technical Publishers, 1982.
[2] 郭焱. 新疆鱼类志[M].乌鲁木齐: 新疆科学技术出版社, 2012: 24-213.
GUO Yan. Xinjiang ichthyology[M].Urumqi: Xinjiang Science and Technology Press, 2012: 24-213.
[3] 侯杰, 周著, 邱秀云. 特克斯河山口引水枢纽的引水防沙设计及试验研究[J].水力发电, 2001, 27(2): 31-34.
HOU Jie, ZHOU Zhu, QIU Xiuyun. Dynamic test and study on the integral body and model with transverse joint of Xiaowan High Arch Dam[J].Water Power, 2001, 27(2): 31-34.
[4] 陈峰, 袁玉江, 魏文寿, 等. 特克斯河流域近236a降水变化及其趋势预测[J].山地学报, 2010, 28(5): 545-551.
CHEN Feng, YUAN Yujiang, WEI Wenshou, et al. Variation and prediction trend of precipitation series for the tekes river basin during the last 236 years[J].Journal of Mountain Science, 2010, 28(5): 545-551.
[5] 曾昭品, 王成雄. 特克斯河流域径流洪水特性分析[J].东北水利水电, 2004, 22(12): 42-43.
ZENG Zhaopin, WANG Chengxiong. Analysis of runoff flood characteristics in Tekes River Basin[J].Water Resource amp; Hydropower of Northeast China, 2004, 22(12): 42-43.
[6] 江敏, 张岩, 阎新书, 等. 伊犁地区部分河流的水质标识指数[J].干旱环境监测, 2007, 21(4): 199-204.
JIANG Min, ZHANG Yan, YAN Xinshu, et al. Water quality identification index in some rivers of Yili district[J].Arid Environmental Monitoring, 2007, 21(4): 199-204.
[7] 袁国映. 托木尔峰地区人类活动对环境的影响[J].地理学报, 1981, 36(4): 413-422.
YUAN Guoying. Influences of human activities on the environmentin the tuomul area[J].Acta Geographica Sinica, 1981, 36(4): 413-422.
[8] 赵玉, 董芳慧, 刘影, 等. 特克斯河上游湿地镰叶锦鸡儿群落植物多样性及区系分析[J].伊犁师范学院学报(自然科学版), 2017, 11(1): 44-49, 84.
ZHAO Yu, DONG Fanghui, LIU Ying, et al. Species diversity and flora components of the Caragana aurantiaca community in the upstream of tekes river, xinjaing[J].Journal of Yili Normal University (Natural Science Edition), 2017, 11(1): 44-49, 84.
[9] 王程欣, 刘斐, 陈生熬, 等. 伊犁裂腹鱼生物学特性[J].新疆农业科学, 2022, 59(8): 2065-2072.
WANG Chengxin, LIU Fei, CHEN Shengao, et al. Biological characteristics of Schizothorax pseudaksaiensis[J].Xinjiang Agricultural Sciences, 2022, 59(8): 2065-2072.
[10] 姚娜, 葛建民, 王程欣, 等. 特克斯河斑重唇鱼生态学特征[J].新疆农业科学, 2023, 60(7): 1798-1805.
YAO Na, GE Jianmin, WANG Chengxin, et al. Ecological characteristics of Diptychus maculates in Turks River[J].Xinjiang Agricultural Sciences, 2023, 60(7): 1798-1805.
[11] 郭焱, 蔡林钢, 吐尔逊, 等. 赛里木湖新疆高原鳅生物学研究[J].水产学杂志, 2002, 15(2): 6-11.
GUO Yan, CAI Lingang, Tuerxun, et al. The study on the biology of T.strauchii (Kessler) in the lake of sailimu[J].Chinese Journal of Fisheries, 2002, 15(2): 6-11.
[12] 郭焱, 蔡林钢, 阿达可白克, 等. 柴窝堡湖新疆高原鳅生物学特性研究[J].水利渔业, 2008, 29(3): 49-50, 79.
GUO Yan, CAI Lingang, Adakebaike, et al. Study on biological characteristics of Xinjiang Plateau loach in Chaiwobao Lake[J].Reservoir Fisheries, 2008, 29(3): 49-50, 79.
[13] 殷名称. 鱼类生态学[M].北京: 中国农业出版社, 1995.
YIN Mingcheng. Fish ecology[M].Beijing: China Agriculture Press, 1995.
[14] Chizinski C J, Pope K L, Wilde G R, et al. Implications of stunting on morphology of freshwater fishes[J].Journal of Fish Biology, 2010, 76(3): 564-579.
[15] Tokaç A, Herrmann B, Gökçe G, et al. Understanding the size selectivity of red mullet (Mullus barbatus) in Mediterranean trawl codends: a study based on fish morphology[J].Fisheries Research, 2016, 174: 81-93.
[16] Petrtỷl M, Kalous L, MemĪş D. Comparison of manual measurements and computer-assisted image analysis in fish morphometry[J].Turkish Journal of Veterinary and Animal Sciences, 2014, 38: 88-94.
[17] 刘璐, 周永东, 高天翔. 褐菖鲉不同地理群体的形态学比较研究[J].水生态学杂志, 2023, 44(2): 81-88.
LIU Lu, ZHOU Yongdong, GAO Tianxiang. Comparison of morphological characteristics of marbled rockfish (Sebastiscus marmoratus) among different geographic populations[J].Journal of Hydroecology, 2023, 44(2): 81-88.
[18] 张永杰, 陈生熬, 王程欣, 等. 新疆裸重唇鱼不同地理种群形态差异[J].新疆农业科学, 2023, 60(2): 511-520.
ZHANG Yongjie, CHEN Shengao, WANG Chengxin, et al. Morphological differentiation of Gymnodiptychus dybowskii kessler among different geographical populations[J].Xinjiang Agricultural Sciences, 2023, 60(2): 511-520.
[19] Kim J, Lee S, Nguyen P T, et al. Length–weight relationships and condition factors of six notothenioid fish species occurring off King George Island and Northern Victoria Land (Antarctica)[J].Polar Biology, 2023, 46(10): 1145-1150.
[20] Bhattacharya P, Banik S. Length-weight relationship and condition factor of the pabo catfish Ompok pabo (Hamilton, 1822) from Tripura, India[J]. Indian Journal of Fisheries, 2012, 59(4): 141-146.
[21] zcan G, Altun A. Length-Weight Relationship and Condition Factor of Three Endemic and Threatened Freshwater Fishes from Orontes River[J].Pakistan Journal of Zoology, 2015, 47(6): 1637-1643.
[22] Ricker W E. Computation and interpretation of biological statistics of fish populations [J]. Bulletin of the Fisheries Research Board of Canada, 1975(191): 382-385.
[23] 杨丽亚, 吕红健, 付梅, 等. 三峡库区短颌鲚年龄和生长特性的研究[J].水生生物学报, 2022, 46(1): 17-28.
YANG Liya, LYU Hongjian, FU Mei, et al. Age and growth characteristics of coilia nasus in the Three Gorges Reservoir Region[J].Acta Hydrobiologica Sinica, 2022, 46(1): 17-28.
[24] 曾霖, 唐文乔. 两种无鳞高原鳅年龄鉴定方法探讨[J].动物学杂志, 2010, 45(1): 94-103.
ZENG Lin, TANG Wenqiao. Discussion on age determination methods for two esquamate Triplophysa fishes[J].Chinese Journal of Zoology, 2010, 45(1): 94-103.
[25] Russell D J, Thomson F E, Thuesen P A. Age and growth of two newly established invasive populations of Tilapiamariae in northern Australia[J].Journal of Fish Biology, 2013, 82(4): 1211-1225.
[26] 杨文荣, 郭焱, 蔡林钢, 等. 赛里木湖饵料生物及渔业现状的研究[J].水产学杂志, 2000, 13(1): 1-10.
YANG Wenrong, GUO Yan, CAI Lingang, et al. Research of Fishery sttuation and Feed creature of Sailimu Lake[J].Chinese Journal of Fisheries, 2000, 13(1): 1-10.
[27] 王新月. 叶尔羌高原鳅年龄、生长、繁殖和种群判别的研究[D].阿拉尔:塔里木大学, 2023.
WANG Xinyue. Research on the age, growth, reproduction and population discrimination of Triplophysa Yarkandensis [D].Aral: Tarim University, 2023.
[28] 陈生熬, 姚娜. 塔里木河流域叶尔羌高原鳅的生物学调查[J].水生态学杂志, 2008, 29(5): 100-102.
CHEN Shengao, YAO Na. Research on biological characteristic of the Triplophysa (Hedinichthys)yarkandensis(day)in Tarim River[J].Journal of Hydroecology, 2008, 29(5): 100-102.
[29] Lester N P, Shuter B J, Abrams P A. Interpreting the von Bertalanffy model of somatic growth in fishes: the cost of reproduction[J].Proceedings Biological Sciences, 2004, 271(1548): 1625-1631.
[30] Katsanevakis S, Maravelias C D. Modelling fish growth: multi-model inference as a better alternative to a priori using von Bertalanffy equation[J].Fish and Fisheries, 2008, 9(2): 178-187.
[31] Schofield M R, Barker R J, Taylor P. Modeling individual specific fish length from capture-recapture data using the von Bertalanffy growth curve[J].Biometrics, 2013, 69(4): 1012-1021.
[32] 陈生熬, 程勇, 范镇明, 等. 塔里木河上游阿拉尔段水质的时空特征[J].水生态学杂志, 2014, 35(5): 15-21.
CHEN Shengao, CHENG Yong, FAN Zhenming, et al. Spatial-temporal characteristics of water quality in the upper reaches of the Tarim River in alar[J].Journal of Hydroecology, 2014, 35(5): 15-21.
[33] 田娜娜, 杨瑞斌, 谭博真, 等. 西藏哲古措异尾高原鳅年龄、生长及繁殖特性[J].中国水产科学, 2022, 29(7): 1013-1021.
TIAN Nana, YANG Ruibin, TAN Bozhen, et al. Age, growth, and reproductive characteristics of Triplophysa stewarti in Lake Chugutso, Tibet[J].Journal of Fishery Sciences of China, 2022, 29(7): 1013-1021.
Research on the biology of Triplophysa strauchiiin Turks River
Gulidan Sailikebole1, WANG Chengxin1, XU Hao1, HU Bolin2,
YANG Haoke3, WEI Qi4, CHEN Shengao1
(1. College of Animal Science and Technology, Tarim University/Tarim Rare Fish Research Center, Aral Xinjiang 843300, China; 2. Aquatic Technology Promotion Station of Xinjiang Production and construction Corps, Urumqi 830000, China; 3. Agriculture and Rural Affairs Bureau of Cocodala City, the Fourth Division of Xinjiang Production and Construction Corps, Cocodala Xinjiang 835219, China; 4 Xinjiang Zhaosu Shanshui Agricultural Technology Co.,Ltd., Zhaosu Xinjiang 835600, China)
Abstract:【Objective】 To study the systematic biology characteristics of Triplophysa strauchii in Turks River, lay a foundation for the development and utilization of its germplasm resources, and consolidate the basic biological data of fish endemic to Xinjiang. 【Methods】 From 2022 to 2023, 488 samples of T. strauchii were collected in the Turks River, and their morphological characteristics were identified by classical biological methods, and their biological characteristics such as age and growth were analyzed. 【Results】 T. strauchii had elongated body, slightly flattened head, slightly raised head, blunt snout, wider lower mouth, curved back outline, thick round forebody, fusiform, width of caudal stalk starting point was obviously larger than caudal stalk height, smooth skin, no scale, and complete lateral line.. The mean age of T. strauchii was (1.74±0.77)+, the maximum age was 4+, the minimum age 0+. Among them, the dominant age was 2+, accounting for 46.80%. The correlation equation between standard length and body weight was as follows: W = 1.15 × 10-5L2.968(R2 = 0.92); The growth equations was: Lt = 161.13 (1-e-0.32 (t + 0.20) ) and Wt = 40.82 (1-e-0.32 (t + 0.20) )2.968, asymptotic standard length was: L∞ = 161.13 mm, asymptotic body weight W∞ = 40.82 g, t0 = -0.20, k = 0.32, ti = 3.23; The fullness coefficient was: k = 1.21. 【Conclusion】 Triplophysa strauchii, a cold water fish with a body shape of spindle, is a carnivorous fish feed organism with uniform growth rate, small age composition, strong adaptability, stable growth characteristics, large number and extremely palatability in the Turks River, which has great development and utilization value and ecological significance. As the dominant indigenous fish in the Turks River.
Key words:Turks River; Triplophysa strauchii; morphology characteristic; age and growth
Fund projects:Special Financial Project of Ministry of Agriculture and Rural Affairs \"Fishery Resources and Environment Survey in Key Waters of Northwest China\"
Correspondence author: CHEN Shengao (1980-), male, from Xining, Qinghai, professor, master and doctorals supervisor, research direction is fishery resources and environment, (E-mail) chenshengao@163.com