主养草鱼高密度池塘溶氧收支平衡的研究

采用原位生态学的方法测定广东省中山市9口主养草鱼高密度池塘中浮游植物光合作用产氧量、水柱呼吸耗氧量、底泥呼吸耗氧量和鱼呼吸耗氧量, 并用数学模型计算增氧机增氧量及用差减法计算大气扩散作用引起的得氧或失氧, 对高密度养殖池塘中溶氧收支平衡状况进行了研究。结果显示: 在水深为1.5-2.0 m的主养草鱼高密度池塘中, 光合作用产氧量随着水深的增加而显著降低(P0.05), 底层出现负值呈现氧债现象。水呼吸耗氧量在表层、中层和底层之间没有显著差异(P0.05)。表层水光合作用产氧量显著大于水呼吸耗氧量(P0.05), 而中层和底层水光合作用产氧量却显著小于水呼吸耗氧量(P0.05)。在主养草鱼高密度池塘溶氧的收入中, 浮游植物光合作用产氧量、增氧机增氧量和大气扩散溶入氧量分别占总溶氧来源的44.7%、42.3%和13.0%, 机械增氧作用已接近光合作用, 成为溶氧来源的主要贡献者; 在池塘溶氧的支出中, 水呼吸、鱼呼吸和底泥呼吸耗氧量分别占总耗氧量的45.9%、45.0%和9.1%, 鱼呼吸耗氧与水呼吸耗氧相当, 成为水体中氧气的主要消耗者。结果表明在草鱼高密度养殖过程中, 合理使用机械增氧是池塘溶氧管理的有效措施。       

溶氧对Candida glycerinogenes产甘油发酵过程的影响

研究了溶氧浓度对产甘油假丝酵母分批发酵生产甘油过程的影响。实验结果表明：当溶氧浓度控制在30%时,C. glycerinogenes的甘油产量、得率和产率达到最高,分别为120.7 g/L、0.575 g/g和1.69 g/(L•h),而糖酵解代谢副产物形成最少。当溶氧浓度为10%时,发酵过程呈现出“巴斯德效应”的特征,生成的酵解代谢副产物维持在较高水平。在快速生长阶段,随着溶氧从10%增加到60%,细胞呼吸类型表现为从厌氧呼吸向好氧呼吸转变,酵解代谢副产物依次减少。在生长稳定期,控制的溶氧浓度越高,酵解代谢副产物乙醇、乙酸等的生成减少。分别选用Logistic方程、Luedeking-Piret方程和Luedeking-Piret-like方程,能较好地模拟细胞生长、甘油合成和葡萄糖消耗的动力学过程。     

赤霉素发酵溶氧优化调控研究

为了解溶氧对赤霉素发酵过程影响以及相应工艺优化,采用不同溶氧条件下藤仓赤霉菌Gibberella fujikuroi分批发酵生产赤霉素的过程进行菌丝浓度、残糖浓度和GA3产物浓度检测,并微分运算得出比生长速率与比产物合成速率随发酵时间变化,分析了溶氧对比生长速率与比产物合成速率以及得率的影响,进而提出Gibberella fujikuroi发酵高产的溶氧控制策略:在发酵初始阶段(0–50h)控制溶氧30%左右,以维持较高的菌体生长速率;发酵中后期(50–184h),溶氧控制在15%,以获取菌丝持续较高的GA3合成速率能力。采用这一优化溶氧控制策略,发酵过程中最大菌丝浓度19.24g/L、最终赤霉素浓度2 180mg/L和平均比产物合成速率0.616mg/(g·h),比未优化前发酵分别提高了8.33%、13.25%和4.58%,表明所采取的分阶段溶氧控制策略对促进GA3生产有效。     

溶氧对杀菌肽-X发酵工艺的影响

本研究采用 30L自动控制发酵罐研究了重组杀菌肽 X工程菌的基本发酵条件。经 12h发酵培养 ,发酵培养基中氨苄青霉素浓度为 0和 100μg/mL时 ,包涵体得率基本一致 ,干重分别为1.24和1.20g L ;控制溶氧为 20%～30%和溶氧自然变化 (转速分别为 250和150r/min)的条件下 ,包涵体得率有较大差异 ,干重分别为0.05、0.71和1.24g L。在较优化的发酵条件下 ,目的融合蛋白的表达量占菌体总蛋白的 45%～50%。     

鱼池中溶解氧的预测预报

本文主要是阐明我国传统池塘养鱼夜间溶氧下降的三种临测方法。溶氧下降的主要因子是浮游生物呼吸、鱼呼吸、淤泥中生物的呼吸,有机肥料耗氧以及氧的扩散,其中浮游生物是鱼池中耗氧的主要因子。用化学需氧量(COD)和温度作为主要指标,通过回归分析,应用计算公式可以预报鱼池中氧的消耗。当浮游生物是透明度的主要因子时,也可以应用透明度法来估计鱼池中氧的消耗。实测和计算的误差平均在20.1％范围之内。应用简易的图示法估计溶氧的含量也获得良好的效果。虽然这一监测方     

米槠和杉木人工林土壤呼吸及其组分分析

区分森林土壤呼吸组分是了解生态系统碳循环的重要环节。该文以福建省三明市格氏栲自然保护区米槠(Castanopsis carlesii)人工林和邻近的杉木(Cunninghamia lanceolata)人工林为研究对象, 于2012年8月至2013年7月, 采用LI-8100开路式土壤碳通量系统, 通过挖壕沟方法, 测定了土壤呼吸及异养呼吸的速率, 同时测定了5 cm深处的土壤温度和0-12 cm深处的土壤含水量。利用指数模型和双因素模型, 分析土壤呼吸及其组分与土壤温度和土壤含水量的关系, 同时计算了土壤呼吸各组分在土壤呼吸中所占的比例, 并分析了不同森林类型对土壤呼吸及其组分的影响。结果表明: 米槠人工林和杉木人工林土壤呼吸及其组分的季节变化显著, 均呈单峰型曲线, 与5 cm深处的土壤温度呈极显著正相关关系。土壤温度可以分别解释米槠人工林土壤呼吸、自养呼吸和异养呼吸变化的70.3%、73.4%和58.2%, 可以解释杉木人工林土壤呼吸、自养呼吸和异养呼吸变化的77.9%、65.7%和79.2%。土壤呼吸及其组分与土壤含水量没有相关关系。米槠和杉木人工林自养呼吸的年通量分别为4.00和2.18 t C·hm^-2·a^-1, 占土壤呼吸年通量的32.5%和24.1%; 异养呼吸年通量分别为8.32和6.88 t C·hm^-2·a^-1, 分别占土壤呼吸年通量的67.5%和75.9%, 米槠人工林土壤呼吸及其组分的年通量都大于杉木人工林。     

西双版纳热带季节雨林与橡胶林土壤呼吸的季节变化

采用挖壕沟法与红外气体分析法,研究了西双版纳热带季节雨林和人工橡胶林内土壤呼吸包括根系呼吸、异养呼吸的干湿季动态变化.结果表明：季节雨林内土壤呼吸和异养呼吸速率均显著大于橡胶林(P＜0.01),但根系呼吸差异不显著;土壤温湿度是呼吸速率变化的主要影响因子,季节雨林和橡胶林内土壤呼吸和异养呼吸速率均为雨季＞干热季＞雾凉季,但季节雨林内根系呼吸为雨季＞雾凉季＞干热季,而橡胶林内为雾凉季＞雨季＞干热季;季节雨林内根系呼吸对土壤呼吸的贡献率(29%)小于橡胶林(42%,P＜0.01),而季节雨林内异养呼吸对土壤呼吸的贡献率为71%、橡胶林为58%;当5 cm土壤温度在12 ℃～32 ℃范围内变化时,季节雨林内土壤呼吸及根系呼吸、异养呼吸的Q₁₀值均大于橡胶林,且异养呼吸的Q₁₀值最大而根系呼吸的Q₁₀值最小.     

溶氧振荡对聚β羟基丁酸混合培养过程的调控作用

研究生物可降解塑料PHB(Poly β-hydroxy butyrate)生产的低成本和高产率发酵。采用廉价碳源——废食品糕点作为原料,其中同时具有葡萄糖和乳酸。培养是在同一5L发酵罐中先后接入2种细菌,先由乳酸杆菌Lactobacillus delbrueckii消耗葡萄糖产生乳酸,再由真养产碱菌Ralstonia eutrophus消耗乳酸产生PHB。本文应用混沌控制理论设计溶氧振荡来协调混生菌矛盾的生理需求,同时改变振荡节律激励细胞的代谢能。考虑真养产碱菌在乳酸里的代谢,有异养和真养两种途径,其中两种重要代谢通量,生物氧化能ATP和还原能NADPH,能够反映混生菌细胞的生理状态,二者都与供氧密切有关。实验通过取样进行细胞破碎后,由荧光分析仪监测不同发酵阶段的ATP和NADPH,发现2种代谢能随着溶氧控制的不同节律变化而起伏,溶氧节律振荡能够使混合培养的PHB的浓度比常规供氧方法提高1倍。     

出芽短梗霉发酵过程溶氧控制的研究

在搅拌罐式生物反应器中,通过控制DO（溶氧浓度）的变化,对出芽短梗霉（Aureobasidium pullulans）发酵过程的控制进行了研究。以100g/L玉米粉水解液做碳源,比较了不同溶氧控制条件下发酵参数的变化及其对出芽短梗霉发酵结果的影响。结果表明,过低的DO对菌体生长和多糖生产都不利,过高的DO使培养液中糖大部分消耗在菌体的生长上,也不利于多糖的生产,通过控制搅拌速度和通气量能将DO维持在较合适的水平。     

正十二烷强化氧传递促进法夫酵母虾青素的合成

对虾青素的氧载体强化氧传递双液相发酵进行了研究。实验结果表明,添加正十二烷(作为氧载体)可提高法夫酵母发酵时的溶氧水平,促进虾青素的合成:添加正十二烷 0.5-1.0%(w/v),虾青素产量随正十二烷添加量逐步提高,最高时达到3.0mg/L,对照组虾青素产率为2.15mg/L;当正十二烷浓度大于2%时,对虾青素的合成表现出明显抑制作用;而正十二烷的添加对细胞的干重没有表现出促进作用。因此虾青素产量的提高是单位质量细胞的虾青素合成效率提高的结果。罐上实验结果表明,发酵开始后的12-24 h时段的溶氧水平对于虾青素的整个合成周期的合成活性至关重要,为发酵供氧进行分段控制提供了依据。根据法夫酵母虾青素合成活性与细胞呼吸活性之间的关系,推测法夫酵母合成虾青素过程对氧的依赖可能与柠檬酸生产菌有着相似的机制。     

池塘混养模式下生态基对鲤生长及水质的影响

为探索池塘混养模式下生态基对鱼类生长的影响, 在6个土池中进行了一个饲养试验, 将土池分为2组, 一组为不放生态基的对照组, 另一组为放置生态基的生态基组, 每组3个重复。将尾均重为(310±11) g鲤3867尾、尾均重(810±15) g鲢及鳙370尾平均分别分为2组, 平均放养于6个土池中。对池塘鲤每天饲喂颗粒饲料3次, 饲养周期62d。在饲养期内, 每隔10天左右采集水样与底泥样品, 检测其中的浮游生物与微生物群落。在饲养结束后, 将试验鱼捕出并称重, 计算鲤的饲料效率。结果表明, 生态基组鲤鱼的增重率与饲料效率显著高于对照组; 生态基组的鲢、鳙末重显著低于对照组; 生态基组水体透明度与微生物群落多样性显著高于对照组; 生态基组浮游生物浓度低于对照组。结果表明, 在混养模式下土池中生态基的应用有利用促进鲤的生长, 然而池塘生态基的应用对于滤食性鲢、鳙的生长并无促进作用。     

溶氧水平对鲫鱼代谢模式的影响

为了探讨水体溶氧水平对鲫幼鱼(Carassius carassius)运动、消化能力及其交互作用的影响,在(25.0±0.5)℃温度条件下,测定了8(饱和溶氧水平)、2和1mg/L溶氧水平下摄食(饱足摄食)和空腹组(空腹2 d)鲫鱼的临界游泳速度(Ucrit)、运动前耗氧率(MO2pre-exercise)、活跃耗氧率(MO2active)和代谢范围(MS)。摄食诱导的耗氧率上升在各溶氧水平下无显著差异。在饱和溶氧水平下,摄食组和空腹组的Ucrit没有显著差异,但在1和2 mg/L条件下,摄食组的Ucrit显著低于空腹组(P<0.05)。在饱和溶氧水平条件下,消化和运动诱导的耗氧率上升在各个游泳水平均能完全叠加,且摄食组鱼类与空腹组鱼类具有相似的MS和Ucrit和更高的MO2active,提示鲫鱼在常氧下为添加代谢模式。随着溶氧水平下降至2和1mg/L,呼吸能力(摄食组的MO2active)对溶氧水平下降较运动耗氧率更为敏感,消化诱导的耗氧率增加只能在较低游泳速度叠加,与空腹组鱼类比较,摄食组鱼类的MS和Ucrit显著下降,MO2active无显著差异,提示低氧下消化和运动对氧气需求竞争的加剧使其代谢模式转化为消化优先。     

池塘养殖匙吻鲟与鳙胃肠道饵料生物的比较

通过对同一试验池中匙吻鲟（Polyodon spathala）和鳙（Aristichthys nobilis）胃肠道内含物的连续3次分析,揭示他们滤食的天然饵料生物组成及差异。首先根据物种鉴定结果对2种鱼的胃肠道内饵料生物组成进行了UPGMA聚类分析,结果显示:相同采样时间同一池塘内2种鱼饵料生物组成存在差异,分别聚为不同的分枝;分析匙吻鲟和鳙胃肠道内饵料生物种类时还发现不同采样时间前者枝角类和桡足类种类数均多于后者。同时对2种鱼胃肠道内各饵料生物的生物量进行分析,结果显示:当大型饵料生物充足时,枝角类和桡足类的生物量在2种鱼胃肠道内没有显著差异（P0.05）;当大型饵料生物减少时,匙吻鲟摄食强度减小,但其枝角类和桡足类的生物量仍显著较大（P0.05）;当大型饵料生物消失后,轮虫生物量在匙吻鲟胃肠道内显著增加 （P0.05）;相比较,鳙在各采样期则主要滤食较小型的浮游动物和浮游植物。另外,当动物性饵料减少后,匙吻鲟和鳙均通过大量滤食植物絮团来补充能量。综上,同一试验池养殖的匙吻鲟和鳙存在摄食竞争压力,该压力的大小与环境中大型饵料生物的丰富度密切相关。       

Changes in the lower trophic levels as a consequence of the level of fish manipulation in the ponds

Cyprinid fish of different mature age classes (3+ -4+) and stocks (100, 300 and 500 kg/ha) were introduced into each of three experimental ponds with area of 0.3 ha (average depth ca 1.7 m) while the fourth pond was left free of fish. Bream (Abramis brama L.), white bream (Blicca bjoerkna L.) and roach (Rutilus rutilus L.) made up 75% of the total cyprinid biomass, with wild carp (Cyprinus carpio L.) as the remaining 25%. The introduced fish spawned successfully. The high (above 300 kg/ha) planktivorous and benthivorous fish stocks resulted in several qualitative and quantitative alterations of the food chain structure in our simulation pond experiments. These alterations must primarily be assigned to changes caused by both the zooplanktivory and benthivory nature of the stocked fish populations. At the higher levels of fish biomass, Secchi depth was influenced significantly by chlorophyll-a concentration. Most of the variance in suspended solids concentration could be explained by the biomass ratio of the mature benthivorous fish. There was a clear shift in algal cell size in the ponds with the higher fish stocks: ponds with more fish had larger cells later in the summer. The relative influence of young cyprinid fish on crustaceans species composition and biomass, and mature populations on benthic fauna abundance and biomass, was sufficiently greater at higher (300–500 kg/ha) fish stock rates.     

野生与人工养殖鲫鳃部寄生指环虫的群落结构

为了阐明养殖环境对鱼类寄生指环虫群落的影响,研究调查了湖北省梁子湖和湖北省石首市养殖池塘中鲫鳃部寄生指环虫的种类和感染情况。在梁子湖中的野生鲫共发现6种指环虫,分别为坏鳃指环虫（Dactylogyrus vastator）、中型指环虫（D. intermedius）、弧形指环虫（D. arcuatus）、弓茎指环虫（D. baueri）、美丽指环虫（D. formosus）、望外指环虫（D. inexpeatatus）;在养殖池塘中,除了望外指环虫外,其他5种指环虫均有发现。分析结果表明,来自于梁子湖野生鲫鳃部的坏鳃指环虫的平均丰度以及其他4种指环虫（不含望外指环虫）的感染率与平均丰度明显高于养殖池塘的。梁子湖中的指环虫群落平均物种丰富度、平均寄生虫数量以及Brillouin多样性指数都明显高于养殖池塘的;梁子湖野生鲫寄生指环虫的优势种是弧形指环虫（0.54）,而池塘中的是坏鳃指环虫（0.76）。在宿主密度、种群大小、光照和溶氧等影响指环虫群落的因子中,溶氧可能是最主要因子。       

Size‐specific effects of bighead carp predation across the zooplankton size spectra

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Food habits, feeding behaviour and impact of triploid bighead carp, Hypophthalmichthys nobilis, in experimental ponds

Food of sterile triploid bighead carp, Hypophthalmichthys nobilis , was examined in ponds receiving water from a hypereutrophic take in Florida. No distinctive seasonal changes in food composition were found. The fish fed selectively on Botryococcus braunii Kuetzing, a large nuisance algal species, which constituted 61% of the volume and 50% of the dry weight of the food. Zooplankton was highly selected, but constituted only 3% of the food volume because of the low zooplankton density in the ponds. The remaining proportion of food consisted mainly of blue-green algae. Final fish biomass was low, ranging from 60 to 97 kg ha⁻¹ in individual ponds. Low biomass was due to slow fish growth and high fish mortality. Despite low biomass, the fish lowered the ratio of blue-green/green algae in the ponds and tended to lower phyto- and zooplankton abundance.     

Photobioreactor design: Mixing, carbon utilization, and oxygen accumulation

Photobioreactor design and operation are discussed in terms of mixing, carbon utilization, and the accumulation of photosynthetically produced oxygen. The open raceway pond is the primary type of reactor considered; however small diameter (1-5 cm) horizontal glass tubular reactors are compared to ponds in several respects. These are representative of the diversity in photobioreactor design: low capital cost, open systems and high capital cost, closed systems. Two 100-m(2) raceways were operated to provide input data and to validate analytical results. With a planktonic Chlorella sp., no significant difference in productivity was noted between one pond mixed at 30 cm/s and another mixed from 1 to 30 cm/s. Thus, power consumption or CO(2) outgassing limits maximal mixing velocities. Mixing power inputs measured in 100-m(2) ponds agreed fairly well with those calculated by the use of Manning's equation. A typically configured tubular reactor flowing full (1 cm diameter, 30 cm/s) consumes 10 times as much energy as a typical pond (20 cm deep flowing at 20 cm/s). Tubular reactors that flow only partially full would be limited by large hydraulic head losses to very short sections (as little as 2 m length at 30 cm/s flow) or very low flow velocities. Open ponds have greater CO(2) storage capacity than tubular reactors because of their greater culture volume per square meter (100-300 L/m(2) vs. 8-40 L/m(2) for 1-5-cm tubes). However, after recarbonation, open ponds tend to desorb CO(2) to the atmosphere. Thus ponds must be operated at higher pH and lower alkalinity than would be possible with tubular reactors if cost of carbon is a constraint. The mass transfer coefficient, K(L), for CO(2) release through the surface of a 100-m(2) pond was determined to be 0.10 m/h. Oxygen buildup would be a serious problem with any enclosed reactor, especially small-diameter tubes. At maximal rates of photosynthesis, a 1-cm tubular reactor would accumulate 8-10 mg O(2)/L/min. This may result in concentrations of oxygen reaching 100 mg/L, even with very frequent gas exchange. In an open pond, dissolved oxygen rises much more slowly as a consequence of the much greater volume per unit surface area and the outgassing of oxygen to the atmosphere. The maximum concentration of dissolved oxygen is typically 25-40 mg/L. The major advantage of enclosed reactors lies in the potential for aseptic operation, a product value which justifies the expense. For most products of algal mass cultivation, open ponds are the only feasible photobioreactor design capable of meeting the economic and operating requirements of such systems, provided desirable species can be maintained.     

Management of an ornamental pond as a conservation site for a threatened native fish species, crucian carp Carassius carassius

Ornamental ponds are important sites for conserving threatened native fish species (e.g. crucian carp Carassius carassius L.), but pond management plans rarely include considerations of native fishes. We developed and implemented a management plan for a small (0.8 h), ornamental estate pond in Hertfordshire (England) using historical information (aquatic plant and animal surveys) and a 9-year data set on climatic variables and crucian carp body condition. Crucian carp growth was not correlated with climatic variables, but body condition decreased with increasing temperature (in degree-days), which suggests that temperature influences on growth are counter-balanced by environmental factors. Management included the removal of one fish species (to eliminate hybridization with another species) and the introduction of two native species (to re-balance the fish assemblage), a reduction in floating aquatic plants (to reduce shading of the sediments) as well as the use of a chemical agent to compact the pond’s fine sediments and barley straw to enhance invertebrate habitat and thus fish prey production. Electronic supplementary material The online version of this article (doi:) contains supplementary material, which is available to authorized users. Guest editors: R. Céréghino, J. Biggs, B. Oertli and S. Declerck The ecology of European ponds: defining the characteristics of a neglected freshwater habitat