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    30 December 1992, Volume 4 Issue 4 Previous Issue    Next Issue

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    MICROBES IN THE AREA OF SOUTH SHETLAND ISLANDS
    1992, 4 (4):  1-1. 
    Abstract ( 1373 )   PDF (156KB) ( 1007 )  

    Microbial exploration of the air, sediment and seawater in the area of the South Shetland Islands was performed during December, 1986-March,1987. The results obtained show that: for terrigenous microbes over the South Shetland Islands and Maxwell Bay, their detection rates were more than 90%and their amounts were generally a few CFU/m 3 ; for marine microbes, their detection rates were more than 50% and their amount only 1 CFU/m 3 . The amounts of air-borne microbes over the area surveyed presented somewhat diurnal variations, They were influenced to some extent by nearby islands.Air temperature and relative humidity, etc. were factors affecting their quantitative variations. The bacterial amount of the outshore surface water in the Great Wall Bay, Antarctica was about n·10 CFU/m 3 (0≤n<10, the same below), the amount of microbes decreased with the monthly decreases of the temperature of seawater and shows some states of diurnal variations. The seawater in the Bay has been fairly clean. Community contained at least thirteen genera, in which Pseudomonas was common. In the intertidal zone of Deception Island, there were only a few CFU of bacteria per cubic meter in seawater; and n·10 CFU/g(w.w) in surface sediment; and n·10 CFU/g(w.w) in the volcano ash. The results reflected the general situation about microbes of air, sea and land in the area of South Shetland Islands. It provides data for further exploration and utilization of microbial resources in the area of South Shetland Islands, Antarctica.

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    MICROBIOLOGICAL RESEARCH EXPLORATION IN GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  7-13. 
    Abstract ( 1404 )   PDF (312KB) ( 1377 )  

    During the third CHARE in 1986/1987,microbes in outdoor and indoor air, ice, snow, lake water,virgin soil,offshore seawater and seaweeds were investigated. The results obtained indicate:there were relatively few microbes in the open air of the Great Wall Station, Antarctica, i.e. the quantity of marine microbes was about 148.7 CFU/m 3 and that of terrigenous microbes about 17.9CFU/m 3. Which indicated that the open air was quite clean. Contents of air-bore microbes indoors were much higher than those outdoors and in the field air.The detection rates and amount of mildew were not high. The amounts of air-borne microbes in different areas varied with human activi-ties and environmental parameters. The results presented here suggested tous that we should continuously improve the purity of indoor air in the Great Wall Station. The amounts of microbes from different sources in the Great Wall Station were arranged in order of magnitude, i.e. ice and snow

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    SEASONAL VARIATIONS OF CHLOROPHYLL-A IN GREAT WALL BAY IN ANTARCTICA
    1992, 4 (4):  14-17. 
    Abstract ( 1356 )   PDF (220KB) ( 1102 )  

    The seasonal variation of chlorophyll a in Great Wall Bay,Antarctica and its adjacent waters was investigated in the period from March 1988 to February 1989. The content of chlorophyll a ranged from 0.16mg/m 3 to 1.33mg/m 3.The vertical distribution of chlorophyll a was basically uniform from December 1988 to February 1989,with a mimuinum value at surface layer.The relationships between chlorophyll a content and environmental factors such as light and temperature are also discussed in this paper.

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    A PRELIMINARY ANALYSIS OF THE PIGMENTS FROM ICE ALGAE IN THE ADJACENT WATERS OF THE GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  18-23. 
    Abstract ( 1359 )   PDF (382KB) ( 1107 )  

    This paper reports the results of isolation and identification of the pigments from ice algae in the adjacent waters (62°12.5′S, 62°14.5′S -58°57′W,58°53′W) of the Great Wall Station, Antarctica during the icing period (from June 1988--December 1988) and studies on the compostion and seasonal variations of the pigments of ice algae in that area as well as their role in marine ecosystems.The results indicate that 15 kinds of ice algal pigments have been isolated, 13 kinds been identified. They are respectively:carotene, pheophytin a, chlorophyll-a, -b, -c,lutein, fucoxanthin, chlorophyllide-a, violaxanthin, pheophorbide-a,chlorophyllin-a, derivative of chlorophyll-c(diadinoxanthin)and two kinds of unidentified pigments. There are distinct seasonal variations of ice algae pigments in that area.

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    THE ISOLATION AND IDENTIFICATION OF PHYTOPLANKTON PIGMENTS IN THE ADJACENT WATERS OF THE GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  24-28. 
    Abstract ( 1359 )   PDF (201KB) ( 1203 )  

    Of the 15 kinds of phytoplankton pigments collected in the adjacent waters(62°12.5′S, 58°53′W-62°14.5′S, 58°57′W)of the Great Wall Station, Antarctica during March 1988-February 1989, 13 kinds were identified according to the Rf values of various marine algae pigments (Jeffrey, 1961). The features of seasonal variations of phytoplankton pigments from the study area are also discussed.

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    THE PIGMENTAL COMPOSITION AND ABSORPTION SPECTRUM OF AN ANALYSIS OF ULOTHRIX SP. AND BENTHIC DIATOMS IN THE INTERTIDAL ZONE OF THE GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  29-33. 
    Abstract ( 1268 )   PDF (301KB) ( 1477 )  

    This paper reports the results of absorption spectrum of Ulothrix sp. attached to the rocks collected from the high tide area in front of the Great Wall Station, Antarctica in February 1989 as well as the benthic diatoms growing on small stones and in the edge of swamps. Six kinds of pigments were isolated and identified in benthic diatoms.They are carotene, chlorophyll a,fucoxanthin, chlorophyllin,P.neoxanthin and chlorophyll c.Nine kinds of pigments were identified in Ulothrix sp.. They are carotinoid, pheophytin, chlorophyll a, b, chlorophyllin chlorophyllide a,neoxanthin, chlorophyll c and pheophytin c. The intertidal benthic diatoms and Ulothrix sp. have specific absorption spectra and there are also marked differences in the composition of algal pigments they contain since the pigments of marine algae show differences in their absorption spectra, the absorption spectrum can be used to identify the species of marine algae.

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    A PRELIMINARY STUDY ON THE ECOLOGY OF THE PHYTOPLANKTON IN GREAT WALL BAY,ANTARCTICA
    1992, 4 (4):  34-39. 
    Abstract ( 1276 )   PDF (330KB) ( 1307 )  

    This paper presents the identification and quantitative analysis of thephytoplankton samples collected during the comprehensive investigation ofmarine organisms in the Great Wall Bay, Antarctica from the period of March1988 to February 1989. The results indicated that the species composition ofthe phytoplankton showed the ecological characteristics of the maincold-water and near-shore eurythermal species; the dominant species showedalternation with seasonal variation, the variation of their cell numbershowed the period of single-peak variation, the peak being in the summer andthe variation of cell number in each month depended upon the alternation ofthe dominant species in that month.The distribution of the phytoplankton isrestricted by a number of environmental factors, the number of hours of daylength being the dominant factor.

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    SPECIES COMPOSITION AND QUANTITATIVE VARIATION OF ZOOPLANKTON IN THE GREAT WALL BAY,ANTARCTICA AND ITS ADJACENT WATERS
    1992, 4 (4):  40-46. 
    Abstract ( 1366 )   PDF (411KB) ( 1456 )  

    A preliminary identification has been made of 35 species of the zooplankton in the Great Wall Bay, Antarctica and its adjacent waters.The dominant species in the investigated area are Calanus propinquus,Calanoides acutus, Metrdia gerlachei and the larvae of antarctic krill. The results indicated that the zooplankton of the investigated waters were simple in species number, which conforms to the general pattern of the distribution of the zooplankton in Antartic waters. The total biomass and number of individuals of the zooplankton in the investigated waters showed obvious seasonal variation. In summer there were Calanioides acutus and the larvae of antarctic krill; in winter there were Metrdia gerlacher, Calanus propinquus, Oithon similis, O.frigda and the larvae of antarctic krill. The quantity of Copepoda occupied a considerable proportion in each month.The water temperature is the important factors in controling the biomass of zooplankton.

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    TWO SPECIES OF LARVAL FISH FROM THE ADJACENT WATERS OF THE SOUTHEAST OF FILDES PENINSULA
    1992, 4 (4):  47-50. 
    Abstract ( 1475 )   PDF (244KB) ( 1120 )  

    Larval fish collected from the adjacent waters of the southeast of Fildes Peninsula from November 1987 to April 1988 were 13.1-15mm long and all in the early stages of development. Through identification, they belongto two species (N. larseni Lonnb and N.gibberfrons Lonnb) of the family of Notothenidae in the order of Notothenia.N.larseni accounting for 88% of the total and N.gibberfrons 12%. The morphology of these two larvalwere decribed in detail.

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    A PRELIMINARY STUDY ON THE FOOD HABIT OF NOTOTHENIA CORIICEPS OF ANTARCTICA
    1992, 4 (4):  51-54. 
    Abstract ( 1262 )   PDF (285KB) ( 1228 )  

    A preliminary analysis of the stomach contents of Notothenia coriiceps Richardson collected in the adjacent waters of the Great Wall Bay was made during the period from 25th to 26th, December 1988. The results of the analysis showed that the main kinds of food included 6 species of benthic animals, many species of Amphipoda, 3 species of zooplankton and 8 species of benthic algae. The benthic animals occupied 52.82% of the total weight of food ingested, of which Patinigers polanis amounting to 16.77%, Amphipoda 33.78%; the Zooplankton accounting for 6.74%,of which, the Euphausia superba accounting for 5.47%; the benthic algae 35.49%, of which Porphyra audiviifolium accounting for 6.35% and Iridaea obovata 18.69%. There was an obvious correlation between the body weight and length of the fish, the correlation coefficient being 9.6. The analytical results also revealed that the main source of the food of Notothenia coriiceps was benthic animals and benthic algae.

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    A STUDY ON THE QUANTITY OF SHALLOW SEA BENTHOS IN THE GREAT WALL BAY,ANTARCTICA
    1992, 4 (4):  55-61. 
    Abstract ( 1437 )   PDF (325KB) ( 1183 )  

    Based on the investigation material acquired during the three cruises of the 4th Chinese Antarctic Research Expedition at 19 quantitative dredging stations and 4th trawling stations from the period December 1987 to March 1988, this paper studies the quantity of the benthos in Great Wall Bay,the distributive characteristics and variations, points out that the stock number of the benthos in the bay is extremely large and that there are two large ranged high mass area and 2-3 low small-ranged mass area. The instability of the sediments is the cause for the low mass areas. The warm season is the vigorous reproductive period of the various kinds of the benthos and the monthly variation of the quantity is remarkable.

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    COMMUNITY ANALYSIS OF SHALLOW SEA BENTHOS IN THE GREAT WALL BAY,ANTARCTICA
    1992, 4 (4):  62-67. 
    Abstract ( 1311 )   PDF (325KB) ( 1285 )  

    The data used in this paper were acquired at 19 quantitative dredging stations and 4 trawling station during the three crusies of the 4th Chinese Antarctic Research Exproditions for investigating the shallow sea benthos in Great Wall Bay, from the period of December 1987 to March 1988. Based on environmental characteristics, diversity of species composition and the eveness of interspecific distribution of individuals, cluster methods were used to divide the investigated area into three benthic community distribution areas. The structures of the various communities were further divided into 3 structural types, namely, high diversity, intermediate diversity and low diversity types. From the study of the relationship between community structure and environmental factors it was pointed out that there is an extremely close relationship between benthic community structure and the stability of the bottom types and sediments, whereas in sea areas where depth gradient is not large, there isno obvious relationship between benthic community structure and depth gradient.

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    THE FOOD WEB IN INTERTIDAL ECOSYSTEM OF FILDES PENINSULA
    1992, 4 (4):  68-73. 
    Abstract ( 1286 )   PDF (262KB) ( 1529 )  

    The Fildes Peninsula (Antarctic) food Web has been considered to be simple. The main producers in this food web were benthic macroalgae,variation in biomass and standing crops have been described by the authors in another paper. The major consumers were molluscs (gastropods and chitons), echinoderms (sea urchins and a seastar), crustaceas, fishes and seabirds. The most abundant mobil species included fishes and seabird which occupied the top trophic level, predaceous gastropods and herbivorous molluscs, which occupied intermediate trophic levels. The most abundant sessile organisms were foliose algae, encrusting algae, and bivalves. These were all tested in two intertidal sections. Field experiments demonstrate that (1)Seabirds and fishes reduced the abundance of herbivorous molluscs, and predaceous snails. (2) Predaceous gastropods reduced the abundance of herbivorous molluscs and sessile invertebrates. (3) Herbivous molluscs reduced the abundance of foliose algae, and altered relative abundance of the encrusting algae. The encrusting algae proved to be inferior competitors for space with other sessile organisms when consumers were experimentally excluded. In this paper we evaluate the influences of substratum heterogeneity and consumers on patterns of diversity of sessile organisms in this habitat,local substratum topography is highly variable, ranging from smooth to irregular surfaces. Algal crusts typically dominate all low zone rock surfaces,and most other sessile species (invertebrates and foliose algae) occur in holes and crevices. The number and diversity of sessile species are lower on homogeneous surface than on heterogeneous surfaces. When consumers are excluded from the general rock surface, algal crusts are overgrown by foliose algae and sessile invertebrates.

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    ECOLOGICAL STUDY OF INTERTIDAL ORGANISMS OF THE FILDES PENINSULA
    1992, 4 (4):  74-83. 
    Abstract ( 1571 )   PDF (190KB) ( 1399 )  

    Although Antarctic rocky intertidal belt and shallowwater area had been dealt with in numerous publications, but few of them refer to soft substratum.Based on field work carried out during Nov.,1985-Mar.,1986,intertidal ecosystems in gravel beach of Great Wall Bay and exposed rocky shores of Marsh Base(62°12′S,58°55′W),the South Shetland Islands, Antarctica are described and studied in this paper. Species composition, ecological distribution, biomass, and density are described and their probable ecological role in the population structure and dynamics of intertidal communities discussed. Great Wall Bay and Marsh Base are situated at King George Island and about two kilometers apart. The temperature there is rather varied, the monthly mean for February is about 1.5℃, while that for August is about -7.8℃. The tides are of irregular semidiurnal types,with a tidal range of not over 2.02 meters usually. The survey method involved the use of both biomass and density using field quadrat (50×50). Two randomly selected intertidal transects were studied. A station was set every xmeters along the transect and a nondestructive method was used to evaluate the community. The degree of dominance was measured in every station. The supralittoral zone is extremely poor in organisms. only Capitella exists. The thick crust of ice covering the surface of the sea for 8-9 months each year changes into a stabilized brackish or freshwater layer when the thawsets in, and makes the tidal zone nearly impossible as a permanent habitat for plants and animals. Here ice and cold are the "controlling factors" and out-weighs all other factors. Toward the littoral the increase of marine species becomes more gradual. The supralittoral fringe, is characterized by a green belt of Urospora penicilliformis and Ulothrix sp. Porphyra endiviifolium,Enteromorpha bulbosa, Spongomorpha arcta and yellow lichens are also found in this belt. Nacella concinna was the dominant species at midlittoral, its density reached 14670 individual/m 2. Harpacticus sp. also exists in this region.The gastropod Laevilittorina antarctica and L.caliginosa are present all along this belt. At the sublittoral fringe, a great number of organisms occur such as Neobvuccinum eatoni,Necella concinna,Laevilittorina antarctica,L.caliginosa,Iridaea obovata and Monostroma applanatum etc. among which Necella concinna and Laevilittorina antarctica were dominant, their biomass averaged 2195g/m 2and 845g/m 2, their density averaged 117 individuals per square meter and 3700 individuals per square meter respectively. Infralittoral belt, was characterized mainly by dense concentrations of the common animals sterechinus new mageri, Magellanea joubini, Glytonotus antarcticus, Cheirimedon femoratus,Philine alatu, Priapulus tuberculatospinosus, and the presence of several species of macroalgae, i.e. Desmarestia anceps, D.menziesii, Gigartina papillosa, Iridaea obovata, Cystosphaera jacquinotii, Adenocystis utricularis,Ascosseira mirabilis. Toward the sublittoral the annual temperature becomes more nearly constant than other zones. Accordingly, the selective effect of each single microhabitation in the sublittoral zone acts upon those organisms which find their optimal conditions there. The sublittoral is a suitable habitat for more species. Benthic marine animals can be differentiated into two principal and ecologically different groups: 1). The epifauna, comprising all animals living upon or associated with rocks, stones, shells, piling, and vegetation. 2).The infauna comprising all animals inhabiting the sandy or muddy surface layers of the sea bottom. The infauna is most fully developed below the intertidal zone. Such constantly submerged infaunas are associated with a level bottom and are exposed to nearly the same types of environmental conditions. In antarctic as in tropical seas, the only factor that is really different is the t

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    A PRELIMINARY ANALYSIS OF THE DISTRIBUTION OF FECAL COLIFORM BACTERIA IN THE NEAR-SHORE WATERS OF THE SOUTH OF FILDES PENINSULA, ANTARCTICA
    1992, 4 (4):  84-87. 
    Abstract ( 1321 )   PDF (158KB) ( 1243 )  

    In this paper a preliminary analysis is made of the number of fecal coliform bacteria in the surface layer of the nearshore waters of the south of Fildes Peninsula, using fermentation method. The results of the investigation indicate that in the surface water of the nearshore waters the highest density of the detection of fecal coliform bacteria is 40/L,generally 20/L and the lowest density less than 20/L, the latter occurring in most stations. In January, the density of the detection in the portion of the intertidal zone at the outlet of pollutant discharge is 40/L and in March 2800/L. As to the distribution of the fecal coliform bacteria, the nearer to the coast, the greater the quantity, which shows its close relation to frequent human activities. It follows that the water bodies of the near-shore waters of the south of Fildes Peninsula have been polluted by domestic sewage, the pollution being yet slight. But the trend of the pollution of the intertidal zone at the outlet of pollutant discharge should arouse our great attention.

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    BACTERIAL MONITORING BEFORE AND AFTER TREATMENT OF SEWAGE IN THE GREAT WALL STATION,ANTARDTICA
    1992, 4 (4):  88-90. 
    Abstract ( 1266 )   PDF (232KB) ( 1297 )  

    This paper reports the results of determination of fecal coliform bacteria and the content of residual chlorine in water samples collected from the outlet of sewage discharge before and aften treatment of the sewage in the Great Wall Station, Antarctica. Results indicate that before the treatment of sewage the number of fecal coliform bacteria was high, reaching 24000/1,but after treatment the decrease of the number of the coliform bacteria group was related to the addition of chlorine in sewage treatment. The more the addition of chlorine, the more the decrease in the bacterial number. In consideration of the fact that an excess of the concentration of residual chlorine may produce an impact on the nearshore ecology, attention should be paid as far as possible to the control of the quantity of the addition of chlorine in carrying out effective treatment of sewage.

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    A PRELIMINARY STUDY ON PETROLEUM POLLUTION IN THE ADJACENT WATERS OF THE SOUTH OF FILDES PENINSULA
    1992, 4 (4):  91-94. 
    Abstract ( 1365 )   PDF (269KB) ( 1345 )  

    This paper reports for the first time on the petroleum pollution in the water and biological samples collected in the adjacent waters of the south Fildes Peninsula, Antarctica. The results of the determinatin of surficial water samples indicate that the investigated sea area has been markedly polluted by oil.Among the investigated stations, station A,at the front of the Great Wall Station of China was the least polluted, the oil concentration in water samples was 512.25 μg/L, slightly higher than the maximum permissible concentration of class 3 water stipulated in the "Criteria for Sea Water Quality in China",the oil pollution in the front cove of Chile Station and Sea Harbor was the heaviest, reaching 4149.23 μg/L and 4169.72μg/L, respectively, being 8 times the oil content of sea water in the front cove of the Great Wall Station. Several species of marine organisms were contaminated with oil in varying degrees, the organisms in intertidal zone were markedly more heavily contaminated with oil than fish. In view of the fact that the investigated sea areas have been markedly polluted and that it is hard to remove the oil once it enters Antarctic sea areas, and for the purpose of protecting the ecological environment of Antarctica, it is very necessary to make a thorough study of the process of purification of oil as well as the effect of petroleum pollution on ecosystems.

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    A PRELIMINARY STUDY OF ORGANOCHLORINE PESTISIDE POLLUTION IN THE ADJACENT WATERS OF THE GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  95-98. 
    Abstract ( 1428 )   PDF (266KB) ( 1309 )  

    In January of 1990 we collected 20 sets of water samples, 2 sets of bottom samples, 4 sets of biological samples and 1 set of ice and snow sample from the adjacent waters of the Great Wall Station, Antarctica, and performed the determination of organochlorine pesticides in these samples in May of the same year. The results of the determination indicate that DDT and BHC (benzone hexachloride) were present to varying degrees in water, bottom sediments, bodies of organisms as well as in ice and snow in the adjacent waters of the Great Wall Station, Antarctica.

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    A PRELIMINARY ANALYSIS OF SONG CHARACTERISTIC OF THE SEA GULL IN ANTARCTICA
    1992, 4 (4):  99-101. 
    Abstract ( 1239 )   PDF (82KB) ( 1202 )  

    This paper describes and analyzes the structure of the wave form and parameters of the song characteristics of Larus Dominicanus in the Fildes Peninsula, Antarctrica under different ecologic behaviour. After analysing and processing the sound signals in laboratory, we obtain four kinds of continuous sound signals in different behaviour. (1) The frequency of signal "zhi" made by a juvenile Larus Dominicanuswas 1610. 4-4831.2Hz. The spectrum crests in this frequency range mainly concentrated on 1.7, 2.5 and 2.9kHz. (2) Larus Dominicanus made signal "e" with a frequency of 1171.2-4343.2Hz. The spectrum crests in the frequency domain concentrate on about 1.5kHz. (3) The frequency of signal "ea" made by the Larus Dominicaus was 1072.5-3932.5Hz, and its spectrum energy in this frequency range mainly concentrated on 1.2, 1.7 and 3 kHz. (4) The frequency of singnal "ge" was 1360.5-4153.5Hz. The spectrum crests focussed on 1.3, 2 and 2.9kHz.

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    ANALYSIS OF CHARACTERISTICS OF THE TIDE AT THE GREAT WALL STATION, ANTARCTICA
    1992, 4 (4):  102-108. 
    Abstract ( 1225 )   PDF (172KB) ( 1160 )  

    In this paper, the characteristics of the tide in the sea area near the Great Wall Station, Antarctica are analysed by means of hourly water level observations acquired at the Great Wall Station from March 1987 to February 1988. The conclusions are as follows: 1.The tidal waves near the Great Wall Station come mainly from the M component of tide wave systems which rotate clockwise in the South Pacific Ocean and the South Atlantic Ocean. They propagate into the Great Wall Bay through the Bransfield Strait and the Maxwell Bay from northwest and from southwest, respectively. 2.The tide at the Great Wall Station belongs to an irregular semi-diurnal tide. On an average in a year, there are monthly about 21 days when two high and two low tides occur daily; and about 6 days when one high and one low tide occur daily; and the other 4 days lie in the transition state. 3.The daily inequality of tide, mainly the daily inequality of low tide,is obvious. 4.The yearly mean duration of rise is not equal to the yearly mean duration of fall, and the difference between both is 21 min. in the year. The monthly mean durations of rise and fall all have two peaks (in March and October, respectively) and two troughs (in June and December respectively) for that year, which is closely related to the number of days when the diurnal tide occur monthly. 5.During the period of investigation, the yearly mean tidal range was 1.243 m and the maximal tidal range was 2.380 m for that year. The monthly mean tidal range reached the maximum and the monthly maximal tidal range reached the minimum near the vernal and autumnal equinoxes (in March and September) and, conversely, near the summer and the winter solstices (In June and December). 6.During the investigation period, the annual mean water level was 3.235m, the maximum water level, 4.351 m (at 08:28, March 31, 1987) and the minimum water level, 1.654 m(at 14:02, Dec. 22, 1987) for that year. In the winter semi-year, the mean water level was lower (the lowest in August) and its change was larger and in the summer semi-year, it was higher (the highest in November) and had smaller changes.

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    SEASONAL VARIATION CHARACTERISTICS OF BOTTOM WATER TEMPERATURE IN THE GREAT WALL BAY, ANTARCTICA
    1992, 4 (4):  109-113. 
    Abstract ( 1432 )   PDF (294KB) ( 1587 )  

    In this paper, the seasonal variation characteristics of the bottom water temperature in the Great Wall Bay, Antarctica are analysed by means of the successive observational data (once per hour) acquired from March, 1987 to February 1988. The preliminary conclusions are as follows: 1. The bottom water temperature is relatively low throughout the year and has no obvious change in the Great Wall Bay, Antarctica. The annual mean temperature is -0.77℃, the maximum temperature, 2.56℃ , and the minimum temperature, -1.97℃. According to monthly statistics, the monthly mean maximum temperature, 1.49℃, occurs in January and February and the monthly mean minimum temperature, -1.88 ℃, occurs in July and August The monthly mean temperature above 0℃ occurs in 4 months of a year, and that below 0℃ in the other months. 2. The temperature-decreasing season of the bottom water is in autumn,and the temperature-decreasing speed is about 0.05℃/d on an average. The temperature-increasing season is in spring, and the temperature increasing speed is about 0.04 ℃/d on an average. Winter ( approximately from May to October ) is the coldest season and the bottom water temperature, about -1.87℃, keeps basically unchanged. Summer is the warmest season and the averaged temperature is 1.10℃. 3. The bottom water temperature interacts with the sea surface air temperature. The annual range of the former is relatively small (4.53℃),and that of the latter is relatively large (39.20℃). The sea surface air temperature rapidly changes from May to October, but the bottom water temperature still keeps the critical temperature, -1.88℃, before freezing and basically unchanged due to the shielding effect of sea ice. 4. The Great Wall Bay is close to the Antarctic Circle. Both the bottom water temperature and the sea surface air temperature have no clear diurnal variations in the winter semi-year, but the difference in temperature of either of them between the daytime and the nighttime is slight in the summer semi-year. It is found by analysing their diurnal change in summer that the difference in the bottom water temperatures between the daytime and the nighttime is relatively small, i.e. 0.11℃ and the difference in the sea surface air temperations is relatively large, 0.78℃. The diurnal change of the bottom water temperature has a time lag, its averaged daily maximum occurring about 2h later than that of sea air temperature and its averaged daily minimum occurring about 5h later than that of air temperature. Contrasting the summer of 1987 with that of 1988, the averaged diurnal changes are roughly identical.

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