田间小棚繁殖烟蚜茧蜂的繁蜂效果研究

研究了田间小棚繁殖烟蚜茧蜂的繁蜂效果,比较了在不同接蜂量和蚜量范围条件下的僵蚜数量及其羽化情况。接蜂量和接蜂时的蚜量是影响僵蚜数量的2个重要因素,以接蜂时的蚜量对繁蜂效果的影响更为明显。在接蜂量为蜂(♀)蚜比1∶100、蚜量范围2 000~3 000头/株的条件下,可获得较好的繁蜂效果,僵蚜的数量可达到8 000个/株以上。在繁蜂前期僵蚜的质量较高,僵蚜的羽化率可保持在90%以上,在繁蜂后期受重寄生蜂的影响,僵蚜的质量明显下降。应用田间小棚繁殖烟蚜茧蜂时,重寄生蜂是影响后期繁蜂质量的重要因素。     

13～18周龄笼养蛋鸭适宜蛋白质和蛋氨酸水平的研究

用 32 4羽满 1 2周龄的金定鸭 ,通过饲养试验、代谢试验、屠宰试验和对试鸭产蛋期 (1 9～ 2 8周龄 )产蛋性能的观察 ,研究了在等能条件下(ME :1 1 51MJ/kg) ,不同蛋白质水平 (CP :1 3 %、 1 5 %、 1 7% )和蛋氨酸水平 (Met/CP :0 0 1 7、 0 0 2 2、 0 0 2 7)组成的 9种饲粮对 1 3～ 1 8周龄笼养蛋鸭的生长性能、养分利用、体成分沉积和产蛋期产蛋性能的影响。结果表明 :该阶段饲粮粗蛋白、蛋氨酸水平对体增重影响不显著 (P >0 0 5) ;体增重与蛋氨酸 (% )呈一定的正相关 (r=0 4574) ;CP为 1 3%、Met/CP为 0 0 2 7组采食量一直较稳定、较高 ,且饲料效率又好。代谢试验 :不同粗蛋白、蛋氨酸水平饲粮对试鸭氮存留率和能量的利用率影响显著(P <0 0 5或P<0 0 1 ) ,且它们随饲粮CP水平的升高而降低 ,随蛋氨酸水平升高而升高 ;磷的利用率也分别以CP为 1 3%的水平和Met/CP为 0 0 2 7的水平极显著地高于其他水平对磷利用率 (P <0 0 1 )。屠宰试验 :当Met/CP为 0 0 2 7时 ,体氮沉积量和体磷沉积量最佳。产蛋性能 :开产日龄和高峰日龄与 1 3～ 1 8周龄CP食入量呈弱的负相关 (r=- 0 1 83 3和r=- 0 0 984) ,与蛋氨酸食入量呈正相关 (r =0 5780和r =0 435 0 )。饲粮粗蛋白、蛋氨酸水平对 1 9～ 2 8周龄     

磷化铝间歇熏蒸防治鱼粉螨类的研究

本研究介绍了饲料鱼粉螨类的有效防治方法．采用11．5g／m2的磷化铝片剂，分两次间歇熏蒸大量孳生螨类和昆虫的棉纱布袋和编织袋包装的鱼粉，达到了有效杀灭鱼粉中大量孳生的粉尘螨、跗蠊螨、齿蠊螨、河野脂螨、食根嗜木螨、马六甲肉食螨、转开肉食螨、特氏肉食螨等8种螨类和烟草甲、白腹皮蠹、拟白腹皮蠹、赤颈郭公虫、赤足郭公虫、黑菌虫的效果。     

海洋养殖柔性网衣结构水动力特性研究进展

发展深水网箱养殖是保障我国粮食及食品安全的长远战略,也是缓解近海网箱养殖环境胁迫力、拓展食物生产空间的必然选择。发展深水网箱养殖首先需要面对的突出挑战是养殖设施在外海恶劣海况下的安全性问题。网衣是深水网箱的主体结构,由于其自身具有高柔性、小尺度的特点,在波浪和水流作用下易出现大位移和大变形的极端响应。当前,网衣结构分析技术已成为我国深水网箱养殖工程技术的薄弱环节,一定程度上制约当前海上养殖网箱向大型化和深水化发展。因此,网衣水动力特性研究对于深远海网箱养殖的发展具有重要意义。本研究系统介绍了计算网衣水动力荷载的主要方法及其适用范围。同时,对网衣动态响应数值计算中的主流建模技术进行了总结和分析。最后,根据目前网衣水动力特性研究中存在的热点问题,提出了网衣流固耦合分析、生物污损分析、数字孪生技术等前沿发展方向,为网衣水动力学分析向数字化、精准化发展提供参考。     

不同声音对草鱼幼鱼负趋音性行为反应影响研究

声驱鱼技术作为辅助过鱼措施之一,承担着保证鱼类洄游顺利通过过鱼设施,继而保护鱼类资源和恢复河流连通性的重要作用。本研究采用交替播音的形式,以草鱼(Ctenopharyngodon idellus)幼鱼为研究对象进行负趋音性实验,旨在探究草鱼幼鱼面对不同声音的行为反应。实验水槽(3.6 m×1.1 m×1.0 m)布置于下牢溪周围水域,平均水深为0.5 m,平均流速为0.06 m/s。实验使用1种单频音(1 000 Hz)和5种复杂音(鱼游动声、引擎声、短吻鳄叫声、打桩声和游艇声),声压级(sound pressure level)为(117.69±2.77) dB re 1 μPa,对照组为未播放声音时草鱼的行为反应数据。结果显示,播放复杂音时,草鱼的反应次数、趋音速度、运动时间比均显著高于单频音和对照组(P<0.001),草鱼的初次反应时间、平均反应时间均显著低于单频音和对照组(P<0.001);复杂音中,受到游艇声刺激的草鱼反应次数和趋音速度最大,受到鱼游动声刺激的草鱼反应次数、趋音速度最小;复杂音中,受到游艇声刺激的草鱼初次反应时间最短,为(23.40±5.13) s;受到引擎声刺激的草鱼初次反应时间最长,为(146.00±7.82) s,显著低于其他复杂音(P<0.05);受到游艇声和打桩声刺激的草鱼平均反应时间最短,分别为(26.52±3.01) s和(28.76±4.07) s;受到鱼游动声刺激的草鱼平均反应时间最长,为(64.76±17.82) s;复杂音中,受到鱼游动声刺激的草鱼运动时间比最高,为(98.47±0.48)%;受到引擎声刺激的草鱼运动时间比最低,为(94.58±0.54)%;播放单频音时,草鱼的反应次数、初次反应时间、平均反应时间、运动时间比均与对照组无显著差异(P>0.05)。本研究表明,5种复杂音(鱼游动声、引擎声、短吻鳄叫声、打桩声和游艇声)对草鱼幼鱼具有驱赶效果。本研究在丰富鱼类负趋音性研究的同时,为实际工程中声驱鱼辅助过鱼设施的设计和优化提供了科学依据。     

进水流速对圆形循环水养殖池流场特性影响的数值模拟

通过对工厂化循环水养殖进水流速的智能调控,可降低饵料残留,避免水质恶化。为此,本研究采用数值模拟方法探究了进水流速对工厂化循环水养殖池流场特性的影响,并基于该研究设计出一套确定进水流速调控的实验方法。首先,通过对比Standard k-ε、RNG k-ε和Realizable k-ε 3种湍流模型及多种壁面函数的仿真效果,确定RNG k-ε模型和标准壁面函数作为仿真配置。同时,针对多相流模型,对欧拉多相流模型和DPM离散相模型进行对比,为提高计算准确性选用DPM离散相模型,并基于上述模型进行网格无关性验证、制定网格划分方案。其次,以大菱鲆(Scophthalmus maximus)养殖为例,模拟不同进水流速下养殖池流场、排污和水温调节的效果。最后,针对仿真结果提出进水流速调控方案。结果显示,日常采用1.0 m/s的进水流速,可有效提高适宜流速区面积并控制水处理成本;投饵前,采用0.2 m/s的进水流速可以解决循环水养殖中存在的饵料浪费问题;进食结束后,采用1.2 m/s的进水流速可快速排出残饵避免水质恶化;水温异常时,采用15 ℃的水、以1.2 m/s的进水流速注水230 s,可使20 ℃的水下降到正常水平,精准化控制水温。采用本研究提出的方法,可针对不同养殖生物和养殖环境设计进水流速智能调控策略,可用于解决循环水养殖过程中饵料浪费、水质变差和水温异常等问题。     

基于水声学方法的嘉陵江中游蓬安段鱼类资源研究

研究嘉陵江中游鱼类资源时空动态特征,了解变化过程及影响因素,提出嘉陵江鱼类资源保护的建议和措施,同时为长江上游及其支流的鱼类资源保护提供基础数据。2018年7月（夏）、10月（秋）以及2019年1月（冬）、4月（春）,运用Biosonics DT-X分裂波束科学回声探测仪对嘉陵江中游蓬安段金溪航电工程干流江段进行了水声学探测,并辅以常规渔获物调查。共采集到鱼类6科38种,其中蛇鮈、鲫、银飘鱼、黄尾鲴等中小型鱼类在数量上占优;鱼类密度分别为春季（0.8296±0.43）、夏季（0.8705±0.38）、秋季（0.5082±0.25）、冬季（0.3939±0.13）尾/m3;鱼体平均目标强度分别为春季（-63.15±5.03）、夏季（-52.85±14.45）、秋季（-46.42±15.85）、冬季（-44.77±15.28）dB;鱼体平均重量分别为春季0.03、夏季1.08、秋季11.19、冬季20.40 g/尾;鱼类资源量分别为春季0.4096、夏季0.2907、秋季0.3919、冬季0.5622 kg/m3;坝下鱼类密度显著高于坝上（F=12.67,P<0.05）;坝上（F=7...     

Therapeutic Intervention with Dietary Chitosan Nanoparticles Alleviates Fish Pathological and Molecular Systemic Inflammatory Responses against Infections

Marine bio-sourced chitosan nanoparticles (CSNP) are antimicrobial and immunomodulatory agents beneficial for fish medicine. Herein, dietary CSNP was investigated for the amelioration of the systemic inflammatory responses of an induced fish model. One hundred and forty-four rainbow trout were assigned to one pathogen-free and non-supplemented group (negative control), and three challenged groups: non-supplemented (positive control), CSNP-preventive, and CSNP-therapeutic. After a feeding experiment extended for 21 days, the organosomatic indices (OSI) and molecular aspects were assessed. After a challenge experiment extended for further 28 days, CSNP-therapeutic intervention was assessed on fish survival and systemic inflammatory responses on pathology, histo-morphology, and molecular aspects. With CSNP administration, OSI nonsignificantly decreased and the relative expression of targeted inflammatory-mediator genes was significantly increased. The CSNP-therapeutic fish showed an RPS of 80% as compared to the positive control group, and CSNP-therapeutic administration retained the highest gene expression augmentation up to 28 days after the challenge. Notably, the splenic reticulin fibers framework of the CSNP-therapeutic group retained the highest integrity among the groups during the infection. After recovery, reticulin fibers density in the CSNP-therapeutic samples was significantly higher than in the negative control group, which indicates high innate immunity. Thus, CSNP showed promising biotherapeutic features enhancing fish resistance against infections.     

The pathogenic helminth parasites of eels

Although 63 and 55 species of helminths have been reported from each species of Atlantic eel and from 29 to 19 for each species of Pacific eel only the monogeneans Pseudodactylogyrus bini and P. anguillae and the nematode Anguillicola crassus, originally specific to species of Pacific eels, can be considered serious pathogens. None of the three are normally pathogenic to their preferred natural eel host species in the wild. Pseudodactylogyrus spp. only cause serious local gill damage when present on a host in large numbers under optimal conditions that facilitate transmission. This is the case in eel aquaculture, where infections can be controlled by drugs. Anguillicola crassus is only pathogenic to Anguilla anguilla and A. rostrata when Atlantic eels are introduced to the far east or when the parasites have been introduced to Europe. Here the parasite life cycle differs in that A. crassus can infect a wide range of intermediate hosts, employ paratenic hosts and survive as larvae for months in the swimbladder wall. This makes it an excellent colonizer. Its major pathogenic effects on eels result from haemorrhaging in, and thickening of, the swimbladder wall. It reduces the oxygen concentration in the swimbladder, reducing its ability to function as a hydrostatic organ, and increases the stress response of eels. In shallow lakes at warm temperatures this can result in mass mortalities. It is also feared that the parasite affects the ability of eels to migrate to the Sargasso Sea and so contributes to the decline in eel populations. Control by drug treatment is possible in culture, but not in the wild.     

Priority habitats for the conservation of large river fish in the Ganges river basin

• 1. Three classes of habitat used by groups of fish species classified as conservation and management priorities were developed for the Gerua River (also known as the Girwa River, Karnali River) in the Ganges river basin. This river is large (mean annual discharge ca 1500 m³ s^?1, up to 900 m wide), surrounded by protected lands of India and Nepal, and upstream of major diversions and river alterations.
• 2. Fish and habitat sampling was conducted at 45 sites from 2000 to 2003. Data were analysed for 2172 fish of 14 species. Species and life stages found occupying a statistically distinct subset of the river habitats were grouped to identify classes of river habitat for conservation.
• 3. Most species and life‐stage groups specialized on specific habitat conditions revealed by multivariate analyses of variance and a principal component analysis. The most numerous and diverse group (six species, 15 life stages) was associated with deep depositional habitats with sandy substrate. Two species covering three life stages were primarily oriented to erosional habitat marked by fast current velocity with pebble and cobble substrate. A third group of three species of adults and juveniles were intermediate in habitat use.
• 4. River conservation for fish faunas should maintain both erosional and depositional channel habitats with depths, substrates, and current velocity inclusive of the ranges reported. The erosional and depositional nature of the key habitats requires that rivers be maintained with flows capable of channel‐forming functions.

Copyright © 2006 John Wiley & Sons, Ltd.