Seed R
Wellcome Marine Laboratory, University of Leeds, Robin Hood's Bay, N.Yorkshire, UK.
Oecologia. 1969 Sep;3(3-4):277-316. doi: 10.1007/BF00390380.
The population structure and apparently erratic distribution patterns exhibited by M. edulis on many open exposed coasts, are discussed in the light of findings relating to the breeding and settlement of this species. In the absence of previous literature concerning open coast mussels, the reproductive cycle has been described in some detail. These mussels do contribute to the spawning stock, and in the three years from October 1964-December 1967, the period of spawning was shown to be particularly extended. Spawning occurred mainly from early spring to late summer, though individuals could be found in the spawning condition more or less throughout the year. No marked or consistent differences in the spawning periods of mussels from different local habitats or amongst animals of different size (=age) were recorded. Sexual maturity was attained in the first year of life.The appearance of larvae in plankton samples confirmed the times of major spawnings recorded from histological preparations of the gonad. Settlement of young mussels (=plantigrades) on existing beds was not direct, there being a period of temporary attachment spent especially upon filamentous substrates. This occurred after about 3-5 weeks of planktonic existence. The majority of plantigrades remained on these primary sites for a period of 4 weeks (i.e. until they measured from 1-2 mm in length), although those settling later in the year often remained there overwinter before migrating on to adult beds. The stimulus to migrate is due to changes in the thigmotactic requirements of small mussels. Whilst filamentous substrates were ideally suitable to early plantigrades, somewhat older individuals preferred the niches and crevices provided on adult beds (especially amongst the byssus threads) and by the small cracks and pits in the rock surface. Since the thigmotactic requirements of all plantigrades were not satisfied at exactly the same time, some migration to adult beds occurred throughout the year, though periods of maximum settlement occurred from 8-10 weeks after spawning. Migration from these extensive "reservoirs" of temporary attachment could account for the sporadic outbursts of settlement recorded on many shores at certain times of the year and which often could not necessarily be predicted on a knowledge of the breeding cycle alone.Although the extended settlement period is an important contributory factor, it is not thought that this alone could account for the distinctive population structure in this species. At settlement, mussels are particularly gregarious, attraction of plantigrades to adult beds being essentially a thigmotactic response, aided by their ability to attach and detach themselves until favourable situations are encountered. Settlement is favoured by roughened, scarred or pitted surfaces and the distribution patterns on many shores could partly be attributed both to the surface texture or topography of the shore (smooth, rapidly draining shores being particularly unsuitable) or the amount of local wave splash.In a subsequent publication, the population structure and distribution patterns will be examined in the light of growth and mortality rates of this species on exposed shores.
根据与该物种繁殖和附着相关的研究结果,讨论了紫贻贝在许多开阔暴露海岸所呈现的种群结构和明显不稳定的分布模式。由于此前缺乏关于开阔海岸贻贝的文献,因此对其繁殖周期进行了较为详细的描述。这些贻贝对产卵群体有贡献,在1964年10月至1967年12月的三年间,产卵期被证明特别长。产卵主要发生在早春到晚夏,不过全年或多或少都能发现处于产卵状态的个体。未记录到来自不同局部栖息地的贻贝或不同大小(=年龄)的动物在产卵期有明显或一致的差异。在生命的第一年就达到了性成熟。浮游生物样本中幼虫的出现证实了从性腺组织学切片记录的主要产卵时间。幼贻贝(=稚贝)在现有贻贝床上的附着不是直接的,有一段临时附着期,尤其在丝状基质上度过。这发生在浮游生活约3 - 5周之后。大多数稚贝在这些初始地点停留4周(即直到它们长到1 - 2毫米长),不过那些在当年晚些时候附着的稚贝通常会在那里越冬,然后才迁移到成贝床。迁移的刺激因素是小贻贝对接触趋性需求的变化。虽然丝状基质非常适合早期稚贝,但稍大一些的个体更喜欢成贝床上(特别是在足丝之间)以及岩石表面的小裂缝和凹坑所提供的壁龛和缝隙。由于并非所有稚贝的接触趋性需求都在同一时间得到满足,所以全年都有一些向成贝床的迁移,不过最大附着期出现在产卵后8 - 10周。从这些广泛的临时附着“蓄水池”的迁移可以解释在一年中的某些时候在许多海岸记录到的零星附着爆发,而仅根据繁殖周期往往不一定能预测到这种情况。虽然延长的附着期是一个重要的促成因素,但人们认为仅这一点不足以解释该物种独特的种群结构。在附着时,贻贝特别群居,稚贝对成贝床的吸引本质上是一种接触趋性反应,它们能够附着和脱离自身直到遇到有利情况,这有助于这种反应。粗糙、有疤痕或有凹坑的表面有利于附着,许多海岸的分布模式部分可归因于海岸的表面质地或地形(光滑、排水迅速的海岸尤其不合适)或当地海浪飞溅的程度。在随后的一篇出版物中,将根据该物种在暴露海岸的生长和死亡率来研究种群结构和分布模式。