2004年东海原甲藻赤潮爆发的现场调查和分析

2004年4～5月对东海赤潮高发区开展了赤潮原因种的大面观测并对期间爆发的特大赤潮进行跟踪调查,在56个站位采集了171份样品。表层东海原甲藻(Prorocentrum donghaiense)变化范围为2.5×10³～6.0×10⁷cells·L^-1,最大值出现在122.94°E,30°N的rb12A站;中层东海原甲藻变化范围为1.0×10³～5.32×10⁶cells·L^-1,最大值出现在rf40站。从水平分布看,东海原甲藻呈不均匀分布,从垂直分布看,赤潮爆发前原甲藻细胞在水体中层密集,大量增殖后上升到表层,爆发赤潮。     

Life history strategies of four small-size fishes in the Suez Canal, Egypt

Of 35 species collected from the shores of the Suez Canal and its lakes, five were abundant year round. Sihouettea aegyptia and Aphanius dispar are of Red Sea (warm water) origin, whereas Pomatoschistus marmoratus, Aphanius fasciatus and Atherina boyeri are Mediterranean species. S. aegyptia and A. dispar are distributed throughout the Suez system whereas A. fasciatus is restricted to the northern canal. P. marmoratus and A. boyeri have not spread southward beyond the Bitter Lakes. Salinity is the main limiting factor for the distribution of Mediterranean species. S. aegyptia and A. dispar are dominant in the Bitter Lakes (salinity 44‰), whereas P. marmoratus and A. boyeri are abundant in Timsah Lake (salinity 7·8–41·6‰). There was considerable interannual and monthly variation in the relative abundance of each species. The populations were dominated by a single age group, and life spans were no more than 2 years. Rapid growth was evident during the first spring in P. marmoratus and A. boyeri and during the first summer, early autumn in S. aegyptia and A. dispar . The relative abundance of each food item in the diet varied with fish size and season. S. aegyptia, P. marmoratus and A. dispar fed mostly on harpacticoid copepods, polychaetes, demersal eggs, diatoms and blue-green algae whereas A. boyeri fed mostly on planktonic copepods. The warm water species are summer spawners, whereas the temperate species are autumn-winter spawners.     

Macroalgal palatability and the flux of ciguatera toxins through marine food webs

The benthic dinoflagellate Gambierdiscus toxicus produces polyether toxins that cause ciguatera fish poisoning in humans. The toxins initially enter food webs when fish forage on macroalgae, or other substrates, hosting this epiphytic dinoflagellate. Population studies of G. toxicus and risk assessments in ciguatera-prone regions often rely on quantifying dinoflagellates on macroalgae. Underlying these studies is the assumption that the algae sampled represent a readily consumable resource equally available for benthic grazers. However, many algal hosts of G. toxicus possess a variety of defenses against grazing, and host–dinoflagellate associations may act as toxin sources or sinks depending on their palatability. Marine macroalgae may tolerate or avoid herbivory by exhibiting fast growth, by having poor nutritional quality, by utilizing spatial or temporal escapes or by using chemical or structural defenses. Thus, rapidly consumed algae that cope with herbivores by growing fast, such as many filamentous turfs, could be responsible for a high toxin flux even at low dinoflagellate densities. In contrast, ubiquitous unpalatable algae with much higher dinoflagellate densities might contribute little to toxin flux, and effectively act as refuges for G. toxicus. To date, G. toxicus has been reported from 56 algal genera, two cyanobacteria, one diatom, and one seagrass; 63% of these contain species that are defended from fish grazing and other grazers via chemical, morphological or structural defenses, by low nutritional quality, or by a combination of defensive strategies. High dinoflagellate densities on unpalatable macroalgae could indicate passive accumulation of cells on undisturbed hosts, rather than population explosions or active toxin sources for food webs. Understanding the flow of ciguatoxins in nature requires consideration of the ecology of both G. toxicus and its algal hosts. The complexity of marine algal–herbivore interactions also has consequences for other benthic dinoflagellates that produce toxins, which accumulate in consumers.     

Sampling harmful benthic dinoflagellates: Comparison of artificial and natural substrate methods

This study compared two collection methods for Gambierdiscus and other benthic harmful algal bloom (BHAB) dinoflagellates, an artificial substrate method and the traditional macrophyte substrate method. Specifically, we report the results of a series of field experiments in tropical environments designed to address the correlation of benthic dinoflagellate abundance on artificial substrate and those on adjacent macrophytes. The data indicated abundance of BHAB dinoflagellates associated with new, artificial substrate was directly related to the overall abundance of BHAB cells on macrophytes in the surrounding environment. There was no difference in sample variability among the natural and artificial substrates. BHAB dinoflagellate abundance on artificial substrates reached equilibrium with the surrounding population within 24 h. Calculating cell abundance normalized to surface area of artificial substrate, rather than to the wet weight of macrophytes, eliminates complications related to the mass of different macrophyte species, problems of macrophyte preference by BHAB dinoflagellates and allows data to be compared across studies. The protocols outlined in this study are the first steps to a standardized sampling method for BHAB dinoflagellates that can support a cell-based monitoring program for ciguatera fish poisoning. While this study is primarily concerned with the ciguatera-associated genus Gambierdiscus, we also include data on the abundance of benthic Prorocentrum and Ostreopsis cells.     

The reproduction of Chaetodon austriacus,C. fasciatus and C. paucifasciatus (Chaetodontidae,Perciformes) in the Jordan Gulf of Aqaba

Synopsis Aspects of the reproduction of three sympatric and endemic chaetodontids, Chaetodon austriacus, C. fasciatus and C. paucifasciatus, from the Jordan Gulf of Aqaba were investigated. Chaetodon fasciatus had a higher fecundity than the other species which, in turn, had similar fecundities. The major egg release of C. austriacus and C. paucifasciatus began in August, that of C. fasciatus in September. Based on the gonadosomatic index of both sexes, the spawning period of C. austriacus was from July through October, that of C. paucifasciatus from August through October and that of C. fasciatus from September through December. The maturity length of the three chaetodontids is given and reproductive isolation among the sympatric species is discussed.     

Ecological observations on mangroves of the Red Sea shores of the Sudan

An ecological survey of the mangrove vegetation in the littoral salt marshes of the Red Sea coast of the Sudan was made during short periods between 1980 and 1982.Avicennia marina (Forsk) Vierh occurs in pure stands of different dimensions in four types of locations. In each location, the responses of Avicennia are expressed in the degree of compactness of aggregation, canopy, height and regeneration potential. Grazing by camels is the primary agent in degradation of accessible locations; salt pans and to a limited extend cutting contribute in part to the process of degradation. The badly damaged aggregations may benefit from protection through control of grazing by nomadic camel tribesmen.     

Population fluctuation and vertical distribution of meiofauna in the Red Sea interstitial environment

The composition and distribution of the benthic meiofauna assemblages of the Egyptian coasts along the Red Sea are described in relation to abiotic variables. Sediment samples were collected seasonally from three stations chosen along the Red Sea to observe the meiofaunal community structure, its temporal distribution and vertical fluctuation in relation to environmental conditions of the Red Sea marine ecosystem. The temperature, salinity, pH, dissolved oxygen, and redox potential were measured at the time of collection. The water content of the sediments, total organic matters and chlorophyll a values were determined, and sediment samples were subjected to granulometric analysis. A total of 10 meiofauna taxa were identified, with the meiofauna being primarily represented by nematodes (on annual average from 42% to 84%), harpacticoids, polycheates and ostracodes; and the meiofauna abundances ranging from 41 to 167 ind./10 cm². The meiofaunal population density fluctuated seasonally with a peak of 192.52 ind./10 cm² during summer at station II. The vertical zonation in the distribution of meiofaunal community was significantly correlated with interstitial water, chlorophyll a and total organic matter values. The present study indicates the existence of the well diversified meiofaunal group which can serve as food for higher trophic levels in the Red Sea interstitial environment.