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1.
本文用神经生理学和心理物理学技术,在同一声学及振动刺激条件下,在不同水平上对非骨鳔类鲡鱼(Hemichromis bimaculatus)的听觉机能进行了系统研究。结果表明鲡鱼的听觉范围在100～600Hz,敏感频率段为200～300Hz,与骨鳔类有显著差别。以内耳球状中微音器电位和中脑诱发电位测量为依据做出的等电位听力图与整体行为反应听力图的带宽相符。加速度听力图中,在400Hz以上敏感度下降。由声及振动引起的中脑诱发电位听力图相似,一般特征为在100Hz以上出现低通滚降10dB/octave。所有结果都表明鲡鱼对水中声压及质点运动成分均有明显反应,300Hz以下敏感度最高。 相似文献
2.
着重分析和讨论全球大气－海洋－海冰事环流模式的两个长时间数值积分试验－１３０年控制试验和９５年敏感性试验，尤其是控制试验中的漂移现象以及与此相关的敏感性试验中增暖信号的提取问题，在控制试验中，大气二氧化碳浓度维持当前的气候值不变；而在敏感性试验中，大气二氧化碳浓度开始时以１％的速率等比增加，它在积分至７０年且其值已达初始值的二倍后便不再变化。分析结果表明，尽管这个耦合模式的长时期积分中存在着明显的 相似文献
3.
本文４１ａ（１９４９－１９８９年）的资料，对东南亚１０°－２５°Ｎ，１０５°－１３０°Ｅ范围７－９月出现的热带风暴异常路长进行了普查统计和气候分析。结果表明：产生异常路径热风暴的机率约占区域内热带风暴总数的２０％；异常路径的产生与热带风暴所处的地理位置，季节，环下等因素有关。正确地考虑气候规律和具体的天气条件相结合是预报带式风暴异常路径成败的关键。 相似文献
4.
一个用于全球气候变化研究的海洋大气环流耦合模式Ⅱ.模式气候漂移和增强温室效应的初步分析 总被引：1，自引：0，他引：1
着重分析和讨论全球大气，海洋－海冰耦合环流模式的两个长时间数值积分试验──１３０年控制试验和９５年敏感性试验（增强温室效应试验），尤其是控制试验中的气候漂移现象以及与此相关的敏感性试验中增援信号的提取问题。在控制试验中，大气二氧化碳浓度维持当前的气候值不变；而在敏感性试验中，大气二氧化碳浓度开始时以１％的速率等比增加，它在积分至７０年且其值已达初始值的二倍后便不再变化。分析结果表明，尽管这个耦合模式的长时期积分中存在着明显的气候漂移，但敏感性试验给出的全球增暖的基本特征在物理上是合理的；这个耦合模式产生气候漂移的主要源地是在高纬度海洋的冰水交界区，且初步的热收支估算揭示它可能与冰－水交界区的耦合方案有关。本文最后在对控制试验和敏感性试验的环流型式的时间演变进行相关分析的基础上给出了有关全球增暖幅度的３种估计，同时指出：尽管全球增暖的空间分布不可避免地要受到模式气候漂移的影响，但这种影响的大部分在计算气温年较差的变化时却可以被自动扣除。 相似文献
5.
利用南麂海洋站１９８１－１９９０年实测波浪资料，探讨了该海域风浪的平均波陡与平均波龄的统计分布特征。分析结果：当风浪平均波陡介于０．０２－０．０４时，其出现频率各季在８２％以上；当风浪平均波龄介于０．５－１．２时，其出现频率各季在７８％以上；当风浪的平均波陡与平均波龄介于０．０２－０．０４和０．５－１．０时，其出现频率为５３．５％－６９．６％。 相似文献
6.
圆尾斗鱼的胚胎和仔鱼发育的研究 总被引：7，自引：0，他引：7
圆尾斗鱼的受精卵呈圆球形，光滑，略带淡黄色，浮性；卵膜吸水膨胀后的平均直径为１．１９ｍｍ，当水温２１－２３．５℃时，从受精卵到孵化出膜需４２．５小时；水温２２－２４．５℃时，刚出膜仔鱼到卵黄囊消失需４天，到油球消失约２５天。出膜３０天仔鱼的形态基本与成体相似。 相似文献
7.
硫化氢对管线钢在氯化钠溶液中应力腐蚀开裂的影响 总被引：3，自引：0，他引：3
采用动电位扫描、慢应变速率拉伸、氢渗透试验方法时X70管线钢在不同电位下含不同浓度H2S的质量分数3．5％NaCl溶液中的应力腐蚀开裂行为进行了研究。结果表明，H2S的加入使渗氢电流逐渐增大，硫化物应力腐蚀开裂（SSCC）敏感性逐渐增加，随着H2S浓度的增大，其断裂特征由塑性断裂逐渐转变为脆性断裂。在阳极极化下，X70管线钢无SSCC敏感电位区；在阴极极化程度较小时，材料对SSCC的敏感性减小；在阴极极化程度较强时，材料对SSCC的敏感性显著增加。分析表明X70管线钢的SSCC受阳极溶解和氢脆共同控制。 相似文献
8.
本文运用滤波和Ｋ－Ｌ变换对全波列声测井数据进行处理。滤波能去掉某些高、低频噪音；Ｋ－Ｌ变换，能削弱相干或不相干的噪音，分离或去掉各种波型，以加强Ｓ波信噪比。 相似文献
9.
采自广东湛江湾海域软水母亚纲(Leptomedusae Claus,1877)、锥螅水母目(Conica Broch，1916)、和平水母科(Eirenidae Haeckel, 1879)、和平水母属(Eirene Eschscholtz，1829) 2新种，即大腺和平水母新种(E. macrogonia Huang, Sun et Liu，sp. nov.)和湛江和平水母新种(E. zhanjiangensis Huang, Zhang et Zao, sp. nov.)。其鉴别特征如下:(1)大腺和平水母，新种；伞扁于半球形，胶质中等厚；胃柄基部塔状，胃柄较长，伸出伞腔口外；垂管长度短于口唇，4个发达口唇边缘呈齿状皱褶；生殖腺发达波状弯曲，着生于辐管下伞部，从胃柄基部延伸到伞缘外；19～24条缘触手，5～8个缘疣，触手基部呈球状，无排泄乳突；每2条触手间或触手和缘疣间有1个平衡囊，每个平衡囊有1～2个平衡石；4条辐管，1条环管。(2)湛江和平水母，新种；伞半球形，胶质厚；胃柄基部呈塔形，末端变窄；垂管较长，约等于口唇长度，口唇边缘有齿状皱褶；生殖腺带状，从胃柄基部延伸至近伞缘；缘触手多，70～125条，触手基球有排泄乳突；平衡囊数目约为触手数的1/2；4条辐管，1条环管。 相似文献
10.
中华绒螯蟹幼体消化系统发育的研究 总被引：20，自引：3，他引：20
于1986，1987两年的3－6月，在浙江平湖水产试验场等地采集中华绒螯蟹五期状幼体和一期大眼幼体，对其消化系统发育的研究表明：各期幼体消化道平均全长分别为0．912mm，1．332mm，1．628mm，1．998mm，2．221mm和2．644mm；胃在Z1中呈椭圆形，到Z3方才明显分化成贲门胃和幽门胃两部分；至于贲门胃内的研磨结构和幽门胃内的滤器则要到大眼幼体才完全形成；在各期幼体中，中肠均是消化道最发达的部分肠壁细胞呈圆柱状；肝胰管和中肠前盲囊在Z1中出现，而中肠后盲囊却要到Z2方才形成。 相似文献
11.
海上风电场建设期风机打桩会产生高强度的水下噪声,研究水下冲击打桩噪声的监测方法、特性分析及对海洋生物的影响是非常重要的。采用自容式水下声音记录仪,多点同步测量了福建省兴化湾海上风电场二期工程建设期单次完整的水下冲击打桩噪声,从时频域特性进行了分析,并利用最小二乘法拟合得到了打桩声源级和声暴露级。结果表明：水下冲击打桩噪声是典型的低频、高强度的脉冲信号,单个脉冲持续时间约90~100 ms,峰值声源级约209.4±2 dB,声暴露级约197.7±2 dB;主要能量分布在50 Hz~1 kHz频段,750 m测量点的该频段声压级相比海洋环境背景噪声,提高了约40~50 dB。水下冲击打桩噪声频域能量分布与大黄鱼的听觉敏感频段相重叠,对大黄鱼影响程度和范围较大,实际工程应用中宜采用声暴露级作为评价指标。 相似文献
12.
为了解水下强噪声对大黄鱼的影响,结合行为学方法开展了3个年龄的大黄鱼声刺激实验．结果发现：3个年龄的大黄鱼在水中声压约10Pa时均能对声波发生条件反应,但是,它们的声波敏感频率和直接致死的声压阈值差异较大;1个月幼苗和8个月小鱼的声波敏感频率分别为800Hz和600Hz,直接致死的声压阈值约为40Pa和4kPa．13个月大鱼的声波敏感频率也在600Hz,但当声压达到4kPa时,鱼群受惊吓明显,且未能直接致死．另外,这些曾经暴露在强声波中的各年龄段的大黄鱼在随后48h里较多出现相继死亡的现象．表明这些长时间暴露在水下噪声中的大黄鱼可能会因累积效应引起行为模式改变和间接致死等慢性危害． 相似文献
13.
Underwater sounds near a fuel receiving facility in western Hong Kong: relevance to dolphins 总被引：1，自引：0，他引：1
Western Hong Kong is home to two species of marine mammals: Indo-Pacific humpbacked dolphins (Sousa chinensis) and finless porpoises (Neophocaena phocaenoides). Both are threatened in many parts of their range in southeast Asia [for example, International Biological Research Institute Reports 9 (1997), 41; Asian Marine Biology 14 (1997) 111]. In 1998, when the new Hong Kong International Airport opened in western Hong Kong, small tankers (about 100 m long, cargo capacity about 6300 metric tons) began delivering fuel to the Aviation Fuel Receiving Facility (AFRF) just off Sha Chau Island, north of the airport. Calibrated sound recordings were taken over a 4-day period from a quiet, anchored boat at distances 80-2000 m from aviation fuel delivery activities at the AFRF. From the recordings, 143 sections were selected for analysis. Narrowband spectral densities on the sound pressures were computed, and one-third octave band levels were derived for center frequencies from 10 to 16,000 Hz. Broadband levels, viz. 10-20,000 Hz. were also computed. The results showed that the Sha Chau area is normally noisy underwater, with the lowest broadband levels measured corresponding to those expected during a storm at sea (sea state 6). This background noise is believed to come largely from heavy vessel traffic in the Urmston Road to the north and east of Sha Chau and from vessels in the Pearl River Estuary to the West. The sound levels from the AFRF tankers are comparable to the levels measured from similar- and smaller-sized supply vessels supporting offshore oil exploration. The strongest sounds recorded were from a tanker leaving the AFRF at distance 100 m from the hydrophone, for which the one-third octave band level at 100 Hz was 141 dB re 1 microPa (spectrum level 127 dB re 1 microPa2/Hz) and the 10-20,000 Hz broadband level was 146 dB. At distances of 100 m or more and frequencies above 300 Hz, the one-third octave band levels were less than 130 dB (spectrum level 111 dB re 1 microPa2/Hz) and decreased with increasing frequency and distance. At distances greater than about 500 m, AFRF-associated sounds were negligible, masked by the generally high noise level of the area and attenuated by poor transmission in the very shallow water (<10 m). Because it is believed that humpbacked dolphins and finless porpoises are not very sensitive to sounds below 300 Hz, the Airport Authority Hong Kong (AA) stipulated that dedicated terminal vessels not radiate underwater sounds at spectrum levels greater than 110 dB re 1 microPa2/Hz at frequencies above 300 Hz and distances greater than 300 m. The spectrum levels at 300 Hz and higher frequencies of sounds from the tankers arriving, departing, or off-loading at AFRF were less than 110 dB re 1 microPa2/Hz even at distances of 200 m or less. The AA stipulation was met. However, it is presently unknown whether the generally strong noise levels of western Hong Kong inhibit acoustically based feeding and communication, or result in increased stress or permanent shifts in hearing thresholds. 相似文献
14.
The underwater acoustic noise of five representative whale-watching boats used in the waters of west Maui was measured in order to study the effects of boat noise on humpback whales. The first set of measurements were performed on 9 and 10 March, close to the peak of the whale season. The ambient noise was relatively high with the major contribution from many chorusing humpback whales. Measurements of boat sounds were contaminated by this high ambient background noise. A second set of measurements was performed on 28 and 29 April, towards the end of the humpback whale season. In both sets of measurements, two of the boats were inflatables with outboard engines, two were larger coastal boats with twin inboard diesel engines and the fifth was a small water plane area twin hull (SWATH) ship with inter-island cruise capabilities. The inflatable boats with outboard engines produced very complex sounds with many bands of tonal-like components. The boats with inboard engines produced less intense sounds with fewer tonal bands. One-third octave band measurements of ambient noise measured on 9 March indicated a maximum sound pressure level of about 123 dB re 1 microPa at 315 Hz. The maximum sound pressure level of 127 dB at 315 Hz was measured for the SWATH ship. One of the boats with outboard engines produced sounds between 2 and 4 kHz that were about 8-10 dB greater than the level of background humpback whale sounds at the peak of the whale season. We concluded that it is unlikely that the levels of sounds produced by the boats in our study would have any grave effects on the auditory system of humpback whales. 相似文献
15.
Kastelein RA Heul Sv Verboom WC Jennings N Veen Jv de Haan D 《Marine environmental research》2008,65(5):369-377
World-wide, underwater background noise levels are increasing due to anthropogenic activities. Little is known about the effects of anthropogenic noise on marine fish, and information is needed to predict any negative effects. Behavioural startle response thresholds were determined for eight marine fish species, held in a large tank, to tones of 0.1-64 kHz. Response threshold levels varied per frequency within and between species. For sea bass, the 50% reaction threshold occurred for signals of 0.1-0.7 kHz, for thicklip mullet 0.4-0.7 kHz, for pout 0.1-0.25 kHz, for horse mackerel 0.1-2 kHz and for Atlantic herring 4 kHz. For cod, pollack and eel, no 50% reaction thresholds were reached. Reaction threshold levels increased from approximately 100 dB (re 1 microPa, rms) at 0.1 kHz to approximately 160 dB at 0.7 kHz. The 50% reaction thresholds did not run parallel to the hearing curves. This shows that fish species react very differently to sound, and that generalisations about the effects of sound on fish should be made with care. As well as on the spectrum and level of anthropogenic sounds, the reactions of fish probably depend on the context (e.g. location, temperature, physiological state, age, body size, and school size). 相似文献
16.
A buoy for measuring wind speed and the ambient noise sound pressure level from 10 to 1500 Hz with 1-Hz resolution is described. The measurement buoy was deployed in a remote fjord in southeastern Alaska from October to December, 1989. The results from the data collected show that, for a wind speed of 5 kn, the measured ambient noise level at 900 Hz lies well below the Knudsen curve for open-ocean, wind-generated noise. As the wind speed increases from 5 to 10 kn, the measured ambient noise level approaches the Knudsen curve, increasing at 4 dB/kn compared to 1 dB/kn for the Knudsen curve. Above 10 kn, the measured ambient noise level matches the Knudsen curve 相似文献
17.
近海海上风电场水下噪声传播模型适用性研究 总被引：1，自引：0，他引：1
通过现场采集近海海上风电场工程区运营期风机水下噪声和背景噪声数据,计算了噪声信号的倍频带声压级,功率谱级和峰值声压级,确定了海上风电场水下噪声总声源级为148.3 d B,以此开展近海海上风电工程风机水下噪声频域特性、功率密度谱特性等研究。在此基础上使用Kraken简正波模型和Bellhop射线模型对风电场运营期风机水下噪声在水平与垂直方向上的传播进行模拟,模拟了噪声在不同频带内的衰减程度,结果显示模型模拟结果在不同频率下的衰减趋势有着很大差异,产生了明显的多途干涉现象,通过实测数据对建立的噪声传播模型进行验证,发现Kraken简正波模型在500 Hz以下,Bellhop射线模型在500 Hz以上适合模拟实际水下噪声传播情形,同时海区本身背景噪声的存在会对预测的准确性产生影响。这些结论可用于进一步对近海海上风电场水下噪声传播的研究。 相似文献
18.
音响驯化技术是控制鱼群和提高放流回捕率的有效方法。目前,对海水鱼类进行音响驯化时关于音响驯化时段选择的研究积累尚少。本试验研究了在7:20、10:20、13:20、16:20和19:20 5个不同驯化时段水平下,许氏平鲉幼鱼在430Hz正弦波连续音刺激下的行为反应,分别探究了在不考虑非音频刺激因素和减轻(甚至避免)非音频刺激因素对音响驯化效果干扰的前提下,许氏平鲉幼鱼的优势音响驯化时段。结果表明,无论考虑非音频刺激因素对音响驯化效果的影响与否,7:20时段都是许氏平鲉幼鱼的优势音响驯化时段。 相似文献
19.
20.
Kastelein RA van der Heul S Verboom WC Triesscheijn RJ Jennings NV 《Marine environmental research》2006,61(1):19-39
To prevent grounding of ships and collisions between ships in shallow coastal waters, an underwater data collection and communication network (ACME) using underwater sounds to encode and transmit data is currently under development. Marine mammals might be affected by ACME sounds since they may use sound of a similar frequency (around 12 kHz) for communication, orientation, and prey location. If marine mammals tend to avoid the vicinity of the acoustic transmitters, they may be kept away from ecologically important areas by ACME sounds. One marine mammal species that may be affected in the North Sea is the harbour seal (Phoca vitulina). No information is available on the effects of ACME-like sounds on harbour seals, so this study was carried out as part of an environmental impact assessment program. Nine captive harbour seals were subjected to four sound types, three of which may be used in the underwater acoustic data communication network. The effect of each sound was judged by comparing the animals' location in a pool during test periods to that during baseline periods, during which no sound was produced. Each of the four sounds could be made into a deterrent by increasing its amplitude. The seals reacted by swimming away from the sound source. The sound pressure level (SPL) at the acoustic discomfort threshold was established for each of the four sounds. The acoustic discomfort threshold is defined as the boundary between the areas that the animals generally occupied during the transmission of the sounds and the areas that they generally did not enter during transmission. The SPLs at the acoustic discomfort thresholds were similar for each of the sounds (107 dB re 1 microPa). Based on this discomfort threshold SPL, discomfort zones at sea for several source levels (130-180 dB re 1 microPa) of the sounds were calculated, using a guideline sound propagation model for shallow water. The discomfort zone is defined as the area around a sound source that harbour seals are expected to avoid. The definition of the discomfort zone is based on behavioural discomfort, and does not necessarily coincide with the physical discomfort zone. Based on these results, source levels can be selected that have an acceptable effect on harbour seals in particular areas. The discomfort zone of a communication sound depends on the sound, the source level, and the propagation characteristics of the area in which the sound system is operational. The source level of the communication system should be adapted to each area (taking into account the width of a sea arm, the local sound propagation, and the importance of an area to the affected species). The discomfort zone should not coincide with ecologically important areas (for instance resting, breeding, suckling, and feeding areas), or routes between these areas. 相似文献