克氏原螯虾对盐度适应性试验

对克氏原螯虾仔虾采用6个不同的盐度进行了盐度突变试验,2个试验组的初始盐度为2,探讨克氏原螯虾仔虾对盐度适应性。盐度突变试验结果显示,克氏螯虾仔虾对盐度为10以下具有较强的适应性。渐变试验显示,克氏螯虾仔虾的存活率与盐度调整周期有关,3d为1次的调整周期优于2d调整周期。因此,在低盐度水平开展克氏螯虾盐度驯养是可行的。     

盐度对克氏原螯虾幼虾生长的影响

研究了不同盐度对克氏原螯虾幼虾生长的影响.试验于水族箱内进行,试验幼虾的初始体质量(1.82±0.21)g,体长(3.13±0.30)cm.在25 ℃条件下,试验设置0、2、4、6、8、10、12、14计8个盐度梯度,试验结果表明,盐度为0～14时,克氏原螯虾的幼体均能存活与生长.盐度为0～6,成活率较高,生长较快,饵料系数较低,各项指标与对照组差异不显著(P>0.05).当盐度超过此范围时,随着盐度增加,幼虾的成活率下降,生长变慢,饵料系数增大,与对照组差异显著(P<0.05).     

盐度对克氏原螯虾幼虾耗氧率和排氨率的影响

研究了不同盐度对克氏原螯虾幼虾耗氧率和排氨率的影响.试验用虾体长(3.13±0.30) cm,体质量(1.82±0.21) g.25 ℃条件下,试验设置盐度0、2、4、6、8、10、12七个梯度.结果表明,试验范围内,盐度为2时,克氏原螯虾幼虾的耗氧率与排氨率最低,表明幼虾对盐度调节的等渗点约为2.随着盐度升高,幼虾的耗氧率和排氨率上升,Tukey HSD test发现,对照组、2、4、6盐度组的耗氧率、排氨率差异不明显.盐度超过0～6时,幼虾的耗氧率、排氨率影响与对照组相比差异显著.     

亚硝酸盐和硫化物对克氏原螯虾幼虾的毒性效应研究

采用静水法生物测试,研究了亚硝酸盐(NO2--N)和硫化物(S2-)对克氏原螯虾(Procambarus clarkii)幼虾急性毒性效应。实验结果表明,克氏原螯虾幼虾的死亡率随着NO2--N和S2-浓度的升高和暴露时间的延长而显著上升。NO2--N对克氏原螯虾幼虾24、48、72、96h的半致死浓度(LC50)分别为108.09、90.08、73.02、69.74mg/L。S2-对克氏原螯虾幼虾24、48、72、96h的半致死浓度(LC50)分别为12.96、9.57、7.62、4.63mg/L。克氏原螯虾幼虾对NO2--N和S2-的安全浓度(SC)分别为6.97mg/L和0.46mg/L,为相应渔业水质标准的35倍和2.3倍,说明克氏原螯虾对NO2--N和S2-的毒性具有一定的耐受力,且对NO2--N的耐受能力强于S2-。     

亚硝酸盐和硫化物对克氏原螯虾幼虾的毒性效应研究

采用静水法生物测试,研究了亚硝酸盐(NO2--N)和硫化物(S2-)对克氏原螯虾(Procambarus clarkii)幼虾急性毒性效应。实验结果表明,克氏原螯虾幼虾的死亡率随着NO2--N和S2-浓度的升高和暴露时间的延长而显著上升。NO2--N对克氏原螯虾幼虾24、48、72、96h的半致死浓度(LC50)分别为108.09、90.08、73.02、69.74mg/L。S2-对克氏原螯虾幼虾24、48、72、96h的半致死浓度(LC50)分别为12.96、9.57、7.62、4.63mg/L。克氏原螯虾幼虾对NO2--N和S2-的安全浓度(SC)分别为6.97mg/L和0.46mg/L,为相应渔业水质标准的35倍和2.3倍,说明克氏原螯虾对NO2--N和S2-的毒性具有一定的耐受力,且对NO2--N的耐受能力强于S2-。     

不同遮蔽物对克氏原鳌虾幼虾成活率的影响

选择向阳面的6个水泥池，利用茶树枝、稻草、枯树叶、棕榈皮、泥巴为遮蔽物，从池塘捕捉克氏原螯虾抱卵亲虾。在不同的遮蔽物下孵化以及苗种培育，研究不同遮蔽物对克氏原螯虾幼虾成活率的影响。结果表明：在不同遮蔽物条件下，幼虾成活率具有显著差异。以茶树枝和棕榈皮为遮蔽物的幼虾成活率极显著高于以稻草、枯树叶、泥巴为遮蔽物的幼虾成活率。其中不设遮蔽物的水泥池中，克氏原螯虾幼虾的存活率最低。在所收获的幼虾个体中，以棕榈皮为遮蔽物的幼虾平均个体重量显著高于以茶树枝、泥巴为遮蔽物的幼虾。     

克氏原螯虾幼虾培育技术研究

对克氏原螯虾幼虾进行培育,即克氏原螯虾从破膜再经3次蜕皮体长到0.9～1.0cm后(即仔虾离开母体后)进行培育,经22d培育试验,幼虾体长平均从1.0 cm增长到3.0 cm,体重平均从0.012 g增重到1.64g.采取两种培育方式(即繁殖池原池培育和幼虾池培育),其成活率平均分别为75.6%和71.2%.     

Cu2+和Cd2+对克氏原螯虾幼虾的毒性效应研究

采用静水法生物测试,研究了Cu2+和Cd2+对克氏原螯虾幼虾(体重0 0142～0 0308 g)的急性毒性作用.试验结果表明,克氏原螯虾对Cu2+、Cd2+均会产生较强的毒性效应,其对Cu2+、Cd2+的耐受性随接触时间延长而明显降低.Cu2+对克氏原螯虾幼虾24 h、48 h半致死浓度(LC50)分别为30.854 mg/L、10.595 mg/L;Cd2+对克氏原螯虾幼虾24 h、48 h、72 h半致死浓度(LC50)分别为5.315 mg/L、1.371 mg/L和0.414 mg/L.Cu2+、Cd2+对其的安全浓度(SC)分别为0.375 mg/L、0.027 mg/L,为相应渔业水质标准的3.8倍和 5.5倍,表明克氏原螯虾具有较强耐受Cu2+和Cd2+污染的能力.     

Cu~(2+)和Cd~(2+)对克氏原螯虾幼虾的毒性效应研究

采用静水法生物测试,研究了Cu2+和Cd2+对克氏原螯虾幼虾(体重0.0142～0.0308g)的急性毒性作用。试验结果表明,克氏原螯虾对Cu2+、Cd2+均会产生较强的毒性效应,其对Cu2+、Cd2+的耐受性随接触时间延长而明显降低。Cu2+对克氏原螯虾幼虾24h、48h半致死浓度(LC50)分别为30.854mg/L、10.595mg/L;Cd2+对克氏原螯虾幼虾24h、48h、72h半致死浓度(LC50)分别为5.315mg/L、1.371mg/L和0.414mg/L。Cu2+、Cd2+对其的安全浓度(SC)分别为0.375mg/L、0.027mg/L,为相应渔业水质标准的3.8倍和5.5倍,表明克氏原螯虾具有较强耐受Cu2+和Cd2+污染的能力。     

湖北地区温棚养殖与稻田养殖克氏原螯虾生长特性研究

2018年12月—2019年3月间,定期从温棚养殖和稻田养殖的克氏原螯虾中采集599尾样本,测量克氏原螯虾的体质量(y)、全长(x1)、头胸甲长(x2)、头胸甲宽(x3)、腹节总长(x4)、第一腹节长(x5)、第一腹节宽(x6)、尾节长(x7)、第六腹节长(x8)、第六腹节宽(x9)和螯长(x10),探明温棚养殖幼虾与稻田养殖幼虾以及温棚养殖雌雄幼虾的生长特性,以期为克氏原螯虾温棚养殖及单性养殖提供参考。试验结果表明,克氏原螯虾全长(L)和体质量(m)呈幂函数,回归方程为:m=0.0209L3.1132;温棚养殖和稻田养殖克氏原螯虾幼虾均在2—3月生长最快,1月生长最慢;克氏原螯虾幼虾各时期各生长指标温棚养殖幼虾均大于稻田养殖幼虾,至3月,温棚养殖的克氏原螯虾体质量接近稻田养殖的2倍;在温度较低的12月—翌年2月期间,温棚养殖的克氏原螯虾幼虾的平均体质量增加率比稻田养殖的克氏原螯虾幼虾的平均体质量增加率高14.00%,温棚养殖的克氏原螯虾幼虾全长平均增长率比稻田养殖的高3.96%。温棚养殖的各时期雄虾体质量均略高于雌虾,但差异不显著(P>0.05);在所有生长指标中,只有雄性克氏原螯虾螯长一直大于雌性,且自12月后,雌、雄虾螯长间一直存在极显著差异(P<0.01)。     

Effects of Salinity on Hatching and Post-Hatch Survival of the Australian Red Claw Crayfish Cherax quadricarinatus

Hatching rate and post-hatch survival of Australian red claw crayfish Cherax quadricarinatus decreased with an increase in seawater salinity. An LC₅₀ of approximately 11 g/L was determined for juvenile survival in seawater through 15 d. Sodium chloride salinity levels as low as 1 g/L killed all crayfish within 15 d. Tolerance of young red claw to higher levels of seawater salinity than sodium chloride salinity may he due to the concentration of other ions in seawater.     

盐度与体重对克氏原螯虾代谢的影响

在水温为20.0±0.5℃条件下,研究了不同盐度(0、3.0、6.0、9.0、12.0)和不同体重(平均体重为7~8 g、19~20 g两种规格)对克氏原螯虾的耗氧率、CO2排出率以及NH3-N排泄率的影响。结果表明,低盐度条件下(0~6.0),两种规格克氏原螯虾的耗氧率、CO2排出率和NH3-N排泄率均随着盐度的升高而显著上升(P<0.05),盐度为6的条件下代谢水平达最高值,此后随着盐度的升高耗氧率、CO2排出率和NH3-N排泄率显著下降(P<0.05);相同盐度下,小规格(平均体重为7~8 g)克氏原螯虾的耗氧率、CO2和NH3-N排泄率显著高于大规格虾(平均体重为19~20 g)。相同规格的克氏原螯虾在不同盐度条件下呼吸商、氧氮比均无显著差异(P>0.05),但是大规格的克氏原螯虾呼吸商和氧氮比显著大于小规格的虾(P<0.05),前者的代谢率极显著低于后者(P<0.01)。     

Acute Toxicity of 5% Non-Synergized Emulsifiable Rotenone to White River Crayfish Procambarus acutus acutus and White Perch Morone americana

Annual drawdown of crayfish culture ponds to plant forage crops also serves to eradicate most predaceous finfish. Without annual drawdown predaceous fish populations may reach numbers that can significantly reduce the crayfish crop. Frequent drawdown may not be feasible or desirable in some management schemes. Evidence in the literature suggests that differential toxicity of rotenone would allow removal of fish without harming crayfish in the same pond. In the current study, laboratory and in situ acute toxicity bioassays (96 h) were conducted with 5% non-synergized emulsifiable rotenone to define the maximum non-lethal concentration (LC₁₀₀) for white river crayfish Procambarus acutus acutus and the minimum lethal concentration (LC₁₀₀) for white perch Morone americana . Six concentration levels of rotenone formulation were tested in each of six toxicity trials with crayfish using dechlorinated tap water at 21–25 C. LC₀ (compensated for control mortality) was determined to be 3.0 mg/L. Significant crayfish mortality began at 4.0 mg/L. Acute toxicity to white perch was anticipated to be within recommended concentration levels on product label for similar fish, and was corroborated by laboratory bioassay (LC₁₀₀ of 0.15 mg/L). Both species were then tested together in laboratory aquaria utilizing pond water at room temperature. Concentration levels of 0.05–2.5 mg/L killed all white perch with no crayfish mortality. In the final phase of the study a 1.0 mg/L concentration of rotenone was applied to a pond containing both species held in cages. All white perch were dead within 24 h; no crayfish mortality was observed for the 96-h duration of the trial. It may therefore be possible to use this rotenone formulation to control white perch and other finfish in active crayfish culture ponds.     

盐度对克氏原螯虾孵化率的影响

研究了不同盐度对克氏原螯虾受精卵孵化的影响.水温25 ℃条件下,盐度0～8时克氏原螯虾的受精卵均可孵出幼体.但以盐度0～4时孵化率较高,每个亲体平均孵出的幼体数量较多,高出此盐度范围时孵化率明显降低,且随着盐度升高,孵化时间延长.试验表明,0～4的盐度为克氏原螯虾孵化的适宜盐度,孵化率较高,孵化时间较短.     

Freshwater crayfish farming technology in the 1990s: a European and global perspective

This paper aims to describe the state of crayfish farming technology in the USA, Australia and Europe, and to discuss some of the prerequisites for this industry. Data from Europe are partly based on replies from a questionnaire sent out to scientists in all European countries. For other parts of the world, the crayfish literature has been reviewed and data from the August 2000 meeting of the International Association of Astacology are also included. Issues addressed in this review are cultivated species, production and productivity figures, production technique with regard to enclosures, reproduction and feed items, disease problems, predators, pond vegetation and water quality. Fewer than a dozen crayfish species are cultivated. The most attractive ones for culture and stocking in natural waters have been transferred to more than one continent. Pond rearing techniques predominate in all countries, and the technology required to achieve the spawning and rearing of juveniles is relatively simple. Pieces of fish, carrots and potatoes are frequent supplementary feed items; plants, cereals, pieces of meat, zooplankton and pellets are also common. Diseases are not usually a major concern, except in Europe where the American plague fungus, Aphanomyces astaci, has eradicated many European crayfish populations. Predators identified as common include insects and amphibians, as well as fishes, birds and mammals. Many water macrophytes are common in crayfish farms. These may either serve a useful function or cause problems for the crayfish farmer. Water temperature is the crucial factor for crayfish production. Water parameters such as pH and certain inorganic ion concentrations may also be of concern. Acidic waters that occur in some areas are generally detrimental to crayfish. The total yield from crayfish production from farming and fishery is in the order of 120 000–150 000 tonnes, more than four times the quantity given by FAO statistics. The largest crayfish producer is the Peoples’ Republic of China, followed by the USA (70 000 and 50 000 tonnes in 1999, respectively). Of the quantity produced in the USA in 1999, about 35 000 tonnes was farmed. The yield in Europe was about 4500 tonnes in 1994, and of this quantity only 160 tonnes came from aquaculture. There are no official statistics for crayfish fishery production in Australia, but about 400 tonnes came from aquaculture in 1999.     

三疣梭子蟹“黄选1号”盐度耐受性分析

通过盐度突变和渐变两种方法测定了三疣梭子蟹"黄选1号"的盐度耐受性。盐度突变条件下,Ⅱ期幼蟹24、48、72h低盐半致死浓度分别为21.655、22.109、23.184;高盐半致死浓度分别为50.711、50.061、49.612。80日龄成蟹24、48、72h低盐半致死浓度分别为5.13、7.49、8.56;高盐半致死浓度分别为54.49、52.74、52.21。在逐渐降低盐度条件下,Ⅱ期幼蟹可在盐度6.7的海水中存活,而80日龄成蟹可在盐度为5.7的海水中存活;随着盐度逐渐升高,Ⅱ期幼蟹和80日零成蟹均可在盐度47.7的海水中存活。三疣梭子蟹"黄选1号"具有较宽的盐度耐受范围。     

Acclimation of rainbow trout to sea water

In some fish farms it is advantageous to transfer rainbow trout from fresh water to sea water at as small a size as possible. It has been shown that a relatively small reduction in salinity at the marine site can give appreciable improvements in survival rates during acclimation by smaller fish, thus rainbow trout of 15 g have routinely been put directly into sea cages at a salinity of 22% with mortality levels of from 1 to 8%.     

红螯螯虾的室内人工育苗

于1996-1998年,在浙北地区,对澳大利亚引进的红螯螯是进行亲虾培育、人工越冬,怀卵孵化,室内人工育苗技术的研究。研究表明,在浙北地区,2.8-4.9g的幼虾经5个月左右的饲养可以达到性成熟并部分怀卵,利用电厂余热水水泥池人工越冬的成活率可达70%以上。越冬后亲是在水温20℃以上即开始交配怀卵,怀卵盛期4-6月。红螯螯虾一年可产卵4次,但只有第一、二次怀卵可用于育苗生产,个体一次怀卵量较少,一般为400-500粒,但群体怀卵比率较高。试验还表明,红螯螯虾出膜幼体即呈幼虾状,需依附母体7-10d后才营独立生活并开口摄食外源性饵料,所研制的幼虾Ⅰ号饲料为红螯螯虾室内人工育苗较好的开口饲料。室内人工育苗成活率可达60%以上。     

Distribution of freshwater crayfish in the British Isles,with particular reference to crayfish plague,alien introductions and water quality

1. The distribution of native and alien crayfish in the British Isles, based on records from 1970–1991, is figured at the 10 km square level and that for Britain is tabulated regionally. 2. Since 1981 crayfish plague has been recorded from six catchments in Britain and one in Ireland, and suspected from an additional four catchments in Britain; 56.2% of native crayfish sites in Britain occur in catchments from which plague has been confirmed. 3. Since the mid-1970s approximately 300 signal crayfish implants have been made in Britain. Only 117 “successful” implants of signals are known to the authors; 39 crayfish farmers were registered in 1986 and 68 by 1990. In 1989 declared production was approximately 7 tonnes. 4. Some mixed populations of natives and disease-free signals exist. Evidence for exclusion of natives is being monitored. 5. Signal crayfish are found in the flowing waters of seven catchments; 58.1% of native crayfish sites are located in catchments which support farmed and wild populations of signals. Some rapidly-expanding Turkish crayfish populations are known, particularly in the Thames catchment. 6. At least 87% of native crayfish records are from good quality waters. 7. Native populations from 88.6% of sites recorded in Britain since 1970 have either been eliminated, or are directly threatened, by crayfish plague infection, and/or habitat invasion by signals, and/or pollution. 8. The native crayfish was added to the list of species protected under the Wildlife and Countryside Act in 1986. 9. Recommendations to assist in the conservation of the native crayfish include a ban on future imports of alien crayfish, a reassessment of records, the setting up of “no-go” areas, the protection of isolated sites, and a restocking programme. 10. There are many restrictedt, healthy populations of native crayfish in areas which could be protected by designating them as Sites of Special Scientific Interest (SSSIs).     

Impact of hydropattern disturbance on crayfish population dynamics in the seasonal wetlands of Everglades National Park,USA

1. The natural hydropattern in the seasonally‐flooded marl prairie wetlands of Everglades National Park has been severely disrupted by human water control activities, seriously impacting higher trophic organisms, e.g. wading birds, that depend on these wetlands. Less is known about the impacts on key aquatic fauna, such as crayfish Procambarus alleni, or how these populations might respond to proposed habitat restoration strategies. 2. Under severe environmental stress, populations of burrowing crayfish are predicted to have skewed size structure, low reproductive success, low survival, and widespread dispersal. As predicted for populations in stressed habitats, crayfish density was low, small dispersing adults were dominant, juvenile abundance was low, and survival was low in habitats where the hydroperiod (duration of flooding) was short and groundwater level was lowest. 3. Crayfish dispersed during flooding, but during the drydown, they burrowed rather than sought deeper water. This dispersal strategy may be adaptive for surviving in seasonal wetlands, but this had severe consequences on survival in disturbed habitats with shortened hydroperiods. Survival in burrows during the dry season was high in the longer‐hydroperiod habitats but was zero in the short‐hydroperiod habitat where the groundwater level fell more than 1 m. 4. Long‐hydroperiod marl prairie may function as sources, whereas short‐hydroperiod habitats act as population sinks. Our study suggests that the threshold conditions for preventing mass mortality of crayfish in these wetlands are hydroperiods >7 months and groundwater levels <0.5 m below the surface during the dry season. 5. Historical (pre‐drainage) hydroperiods appear to be restricted to the longest hydroperiod areas of the marl prairie. This indicates that much of the marl prairie wetlands now function as population sinks for crayfish and other invertebrates. The historical hydropatterns need to be re‐established throughout the marl prairie wetlands to achieve the restoration goal of increasing productivity in the aquatic faunal community. Copyright © 2001 John Wiley & Sons, Ltd.