盐度对波部东风螺幼虫存活、生长及变态的影响   总被引：13，自引：0，他引：13  

郑怀平  柯才焕  周时强  李复雪 《台湾海峡》2001,20(2):216-223

采用突变和渐变两种实验方法检验了盐度对波部东风螺幼虫存活、生长和变态的影响。这两个实验，在盐度21．0－27．5的范围内，幼虫均有较高的存活率、变态率和较快的生长速度。其中，在盐度24．0处，幼虫的存活率和变态率都最高，生长速度也最大。不管盐度如何，幼虫较快的生长速度总是和自发变态前较短的浮游期联系的，尽管渐变盐度没能使幼虫的存活率、变态率、生长速度、变态个体的大小以及浮游期的长度得到显著的改变，却明显地加宽了幼虫存活和变态的盐度范围。渐变盐度的实验方法优于突变盐度的实验方法。  相似文献   

冠瘤海鞘幼体附着和变态的离子控制   总被引：3，自引：0，他引：3  

黄英  柯才焕  冯丹青  周时强  李复雪 《海洋学报》2005,27(1):137-144

研究了人工海水中三种金属离子K+,Mg2+和Ca2+分别在不同浓度下对冠瘤海鞘(Styelaca nopusSavigny)幼体附着和变态的影响,同时采用K+通道阻滞剂TEA检验其可兴奋细胞膜上的K+通道特性,对冠瘤海鞘幼体附着和变态的离子控制机制进行初步探讨,结果表明:K+的浓度为20~40mmol/dm3时诱导幼体附着和变态的效果最佳,低于45 mmol/dm3和高于80mmol/dm3的K+浓度都表现出抑制效果;Mg2+浓度在0~32 mmol/dm3时显著促进幼体附着和变态,达88mmol/dm3时起抑制作用;在人工海水中无论添加或减少Ca2+,均有效抑制幼体变态.TEA不能阻抑增加K+的诱导作用,这表明冠瘤海鞘幼体可兴奋细胞膜上的K+通道对外部TEA不敏感.另外,人工海水中缺乏K+或Ca2+或K+浓度达80mmol/dm3都会对冠瘤海鞘幼体产生毒害作用.  相似文献   

海洋生物监测新技术探索:幼虫变态实验     

吴荣军  张学雷  郑家声  朱明远 《海洋科学进展》2002,20(1):66-71

回顾了近年来海洋环境污染生物监测中的海洋底栖无脊椎动物早期发育和变态阶段的毒性实验的研究进展 ,强调应根据敏感性和代表性水平来选取生物有机体进行生物毒性实验 ,并探讨了运用幼虫变态实验来进行海洋污染监测的可行性  相似文献   

受短期停食胁迫下三疣梭子蟹幼体的存活与变态     

王志铮  杨阳 《海洋学报》2007,29(4):111-119

2005年4月以三疣梭子蟹各期幼体为实验动物,开展了短期停食对三疣梭子蟹幼体存活与变态影响试验.结果表明:完全停食处理条件下三疣梭子蟹各期幼体的平均全致死时间按发育先后次序(Z₁,Z₂,Z₂,Z₄,M)依次为81,120,141,162和200 h,平均半致死时间为39,66,90,64和174h;短期停食后恢复正常给饵条件下三疣梭子蟹各期幼体停食处理后的变态临界点按发育先后次序依次为停食处理后的33,57,69,54和150 h;单次停食时间在变态临界点内,先停食后正常给饵与"给饵+停食"循环两处理模式中各期幼体的存活率和变态率均随着停食时间的延长而下降,幼体变态所需时间和变态后个体死亡率也分别随之延长和增加,其中Z₁停食3 h组与"给饵3 h+停食3 h"循环组、Z₂停食4 h组与"给饵4 h+停食4 h"循环组、Z₃停食4.5 h组与"给饵4.5 h+停食4.5 h"循环组,Z₄停食6 h组与"给饵6 h+停食6 h"循环组、M停食7.5 h组、停食15 h组以及"给饵7.5 h+停食7.5 h"循环组均与对照组无差异.最后,还分别就三疣梭子蟹各期幼体停食处理极限值和限食处理总实验时间的确定、短期停食胁迫对三疣梭子蟹幼体的存活与变态特征以及三疣梭子蟹各期幼体的补偿生长水平及其应用等进行了分析与探讨.  相似文献   

Neurophysiological control of swimming behaviour,attachment and metamorphosis in black-footed abalone (Haliotis iris) larvae     

AC Alfaro  T Young  K Bowden 《新西兰海洋与淡水研究杂志》2014,48(3):314-334

Experiments were conducted to test the effect of a range of chemicals on larval responses in swimming behaviour, attachment and metamorphosis of the black-footed abalone (Haliotis iris). The effect of antibiotics on larval survival was first tested within negative (filtered seawater) and positive (GABA at 10^?5, 10^?4 and 10^?3 mol L^?1) control assays over 3 days. This experiment corroborated the effectiveness of using antibiotics to improve survival of larvae without obvious synergistic interactions with the GABA inducer or confounding effects of potential bacterial interactions. Chemical treatments (acetylcholine, potassium chloride, dopamine and glutamine) were then tested at various concentrations for their ability to modulate swimming behaviour and induce larval attachment and metamorphosis over 14 days. Generally, larval state shifted from swimming to attached, and from attached to metamorphosed, in the control and treatments over time. However, the peak percentage of attached and metamorphosed larvae varied in time among chemicals and concentrations. While overall percent metamorphosis was minimally enhanced after 14 days of exposure to some chemical treatments at certain concentrations, all treatments displayed significant capacities to down-regulate larval swimming and induce early attachment and metamorphosis. Mortality was recorded throughout the duration of the experiment, and was generally low (<20%) across controls and most treatments for exposures of less than 12 days. Interpretations of specific results from this study are used to elucidate neurophysiological control of larval activities for this abalone species. Comparisons with other marine invertebrates highlight the specificities of chemical cues and endogenous regulatory mechanisms across relatively closely related taxa.  相似文献   

几种微藻对方斑东风螺浮游幼虫生长和变态的影响     

杨章武 《台湾海峡》2007,26(4):583-589

本文报道了4种微藻不同浓度对方斑东风螺幼虫生长和变态的影响.结果表明,幼虫对4种微藻都能摄食,当投喂不同浓度的牟氏角毛藻、湛江叉鞭金藻时,摄食角毛藻(20×104cells/cm3)生长最快达77.9μm/d、变态率52.5%;摄食金藻(20×104cells/cm3)变态率最高达59.0%、生长速度70.4μm/d,随金藻浓度的上升,幼虫生长速度和变态率都上升.投喂不同浓度的青岛大扁藻时,最高变态率是24.4%(1×104cells/cm3),最快生长速度是59.3μm/d(7×104cells/cm3),随扁藻浓度的上升,幼虫的生长速度上升而变态率下降.摄食云微型藻幼虫生长缓慢,浮游期全部死亡.幼虫单独摄食角毛藻、金藻和扁藻,其首次出现变态个体的日龄分别是10、11、14d,而完成变态的日龄分别是22~23d、21~23d和26~28d.比较上述4种微藻,角毛藻和金藻是方斑东风螺幼虫的最适饵料,根据大水体人工育苗的具体条件,合适浓度应为角毛藻(5~10)×104cells/cm3,金藻(10~15)×104cells/cm3.而扁藻不宜单独投喂,作为辅助饵料较合适.  相似文献   

Tipping points in Texas rivers          下载免费PDF全文

Jonathan D. Phillips 《地球表面变化过程与地形》2018,43(9):1768-1781

Anticipating geomorphic tipping points requires that we learn from the past. Major geomorphic changes in coastal plain rivers of Texas resulting in river metamorphosis or regime shifts were identified and the major driving factors determined. Eleven such transformations – possible tipping points – were identified from contemporary observations, historical records, and Quaternary reconstructions. Two of the tipping points (between general aggrading and degrading valley states) are associated with reversals in a fundamental system control (sea‐level). One (stable or aggrading versus degrading channels) is associated with an abrupt change in sediment supply due to dam construction, and two others (changes from meandering to anastomosing channel patterns, and different anastomosis styles) are similarly related to changes in sediment supply and/or transport capacity, but with additional elements of historical contingency. Three tipping points are related to avulsions. One, from a regime dominated by re‐occupation of former channels to one dominated by progradation into flood basins, is driven by progressive long‐term filling of incised valleys. Another, nodal avulsions, is triggered by disturbances associated with tectonic uplift or listric faults. The third, avulsions and related valley metamorphosis in unfilled incised valleys, is due to fundamental dynamical instabilities within the fluvial system. This synthesis and analysis suggests that geomorphic tipping points are sometimes associated with general extrinsic or intrinsic (to the fluvial system) environmental change, independent of any disturbances or instabilities. Others are associated with natural (e.g. tectonic) or human (dams) disturbances, and still others with intrinsic geomorphic instabilities. This suggests future tipping points will be equally diverse with respect to their drivers and dynamics. Copyright © 2018 John Wiley & Sons, Ltd.  相似文献   

鞍带石斑鱼(♀)×蓝身大斑石斑鱼(♂)杂交F1代变态发育和生长特征分析     

成美玲  田永胜  吴玉萍  李振通  张晶晶  王林娜  马文辉  庞尊方  刘成磊  孙芳芳  翟介明 《海洋学报》2019,41(8):52-62

为了深入研究鞍带石斑鱼(Epinephelus lanceolatus) (♀)×蓝身大斑石斑鱼(E. tukula) (♂)杂交F1代的变态发育及生长特征，本研究对杂交组和纯种鞍带石斑鱼胚胎发育时间、受精率、畸形率、孵化率和仔稚幼鱼生长性状(全长、体长、体高、肛前距），以及杂交组卵黄囊和油球吸收过程，第二背鳍棘和腹鳍棘生长和收缩，口径和眼裂的变化等进行了详细的观察描述和统计分析。结果显示，在水温28℃条件下，杂交组和鞍带石斑鱼受精卵分别经21 h 24 min和21 h 32 min完成胚胎发育；杂交F1代受精率、畸形率和孵化率分别是89.09%±0.08%、35.16%±5.05%和62.59%±10.70%，与纯种鞍带石斑鱼无显著性差异。根据卵黄囊、第二背鳍棘、腹鳍棘、鳞片、体色等形态变化，将其胚后变态发育分为前期仔鱼(孵化后0～6 d)、后期仔鱼(孵化后7～34 d)、稚鱼期(孵化后35～46 d)和幼鱼期(孵化后47～86 d)，前期仔鱼生长较缓慢，后期仔鱼到幼鱼期生长逐渐加快，86 d时杂交组和对照组体长分别达(60.80±0.50) mm和(51.80±0.47) mm，杂交组生长速度极显著高于对照组(P<0.01)。在胚胎发育时期卵黄囊消耗量为29.45%，油球消耗量为20.75%，卵黄囊在孵化后1 d消耗最快，达58.70%。油球在孵化后3 d消耗最快，达32.08%，孵化后第5 d仔鱼卵黄囊和油球基本吸收完毕。第二背鳍棘、腹鳍棘在孵化后29 d达到最长，分别是(8.15±0.02) mm和(5.80±0.10) mm，至47 d完全退化，变态发育完成。第一天仔鱼眼径为(0.16±0.01) mm，至86 d眼径增大22倍，第四天口裂长为（0.09±0.02） mm，至86 d增大99倍。结果表明，鞍带石斑鱼(♀)×蓝身大斑石斑鱼(♂)杂交F1代胚胎和仔稚幼鱼发育正常，而且杂交F1代与母本相比具有较显著的生长优势，本研究为两种石斑鱼杂交苗种培育、发育研究和品种改良提供了丰富的数据。  相似文献   

单体牡蛎诱导变态的研究   总被引：1，自引：0，他引：1       下载免费PDF全文

陈亨  方军  滕爽爽  肖国强  张炯明  柴雪良 《海洋科学》2016,40(1):10-17

为了得到壳型规则、大小均一的单体牡蛎,作者以葡萄牙牡蛎(Crassostrea angulata)和长牡蛎(Crassostrea gigas)眼点幼虫为材料,从肾上腺素(EPI)浓度梯度、处理时间梯度和眼点幼虫密度梯度3个因素诱导产生不固着变态的单体牡蛎。结果表明,葡萄牙牡蛎用EPI处理24 h的最适浓度为5×10–4 mol/L,不固着变态率为72.8%,在该最适浓度下,最佳处理时间为12 h,不固着变态率为82.7%。长牡蛎用EPI处理6 h的最适浓度为5×10–5 mol/L,不固着变态率为53.2%,在该最适浓度下,最佳处理时间为8h,不固着变态率为56.8%,眼点幼虫密度在80个/m L以下EPI处理效果没有显著性差异。对长牡蛎幼虫进行后续生长测定,结果显示EPI处理组幼虫的壳长、壳高和存活率要高于对照组,表明EPI可能促进牡蛎幼虫变态长出次生壳并提高其生存能力。  相似文献   

L-DOPA对西施舌眼点幼虫附着变态诱导的研究   总被引：2，自引：0，他引：2  

刘文彪  高如承  黄振彬  骆轩  罗彩林  王静 《海洋科学》2006,30(2):26-29

采用试验水体中添加化学诱导物的方法研究L-DOPA(L-多巴)对西施舌(Coelomctraantiquata)眼点幼虫附着变态的诱导作用。结果表明,L-DOPA能诱导西施舌眼点幼虫变态,但对其附着的诱导效果不明显。用直径小于1 mm的细沙为附着基质,1×10-6mol/L的L-DOPA处理西施舌眼点幼虫12 h,变态率为73.3%,对照组为62.6%。浓度为1×10-7mol/L的L-DOPA处理西施舌幼虫12 h,生长速率为25.6%,对照组为14.7%,表明适当浓度的L-DOPA能促进西施舌幼虫的生长。在无沙附着的条件下,西施舌幼虫可正常附着变态,但生长速率较低且变态后死亡率高。  相似文献