In order to clarify the seasonal composition and abundance of zooplankton community in Macheon Bay. the study was carried out trimonthly during the period from April 1996 to January 1997. 37 taxa and 7 unconfirmed species of zooplankton was identified. It consisted of 28 species of Protozoa. 1 species of Cnidaria, 1 species of Annelida, 2 larva of Mollusca, 3 species of Rotifera, 4 species and 4 larva of Arthropoda and 1 larva of Echinodermata, respectively. Seasonal succession of the dominant species was Tintinnopsis beroidea in the spring. Copepodite in the summer. Tintinnopsis directa in the autumn and Ceratium fusus in the winter. Abundance of zooplankton ranged from 4.720 to 4 1.215 inds./ . It was high in the summer (4 1.215 inds./ ) and low in the spring (4.720 inds./ 1 ). Dominant index ranged from 0.133 (in the spring) to O. 551 (in the winter). Species diversity index ranged from 1.114 (in the winter) to 1.996 (in the spring).

The dicriminant function was introduced to understand the cause and establish the prediction method of red tides occurring in Jinhae Bay, Korea. Two sea regions of Masan and Haengam Bays and Dangdong and Wonmun Bays had different types of causes and patterns for red tides. In Masan and Haengam Bays, the red tides concentrically occurred during June and September. For example, in June the red tides occurred from physical and meteorological factors, which are related to the stratification and the increase in planktons. However, in August the red tides occurred from the water quality environment, based on these conditoins. Futhermore, in September the red tides were caused by the balance between the meteorological and water quality environmental factors. In contrast to those, in Dangdong and Wonmun Bays, the red tides mainly occurred during July and October and the frequency of occurrence was not as much as Masan and Haengam Bays. Especially, in August and September most meteorological and physical factors or water quality environmental factors appeared to contribute to the occurrence of red tides. This indicates that red tides do not easily occur as they are controlled by various environmental factors particularly in these regions. The discriminant functions were applied to predict red tides which they were actually occurred in Masan and Haengam Bays in June. The results showed that they were successful for the prediction of red tide at Haengam Bay but not at Masan Bay. The reason for their discrepancy in Masan Bay could have come from using a slight higher value of pH or COD in May, instead of its value in June.

The community of phytoplankton and water quality were investigated 5 times from October, 1994 to October, 1995 in the east area of Chinhae Bay. Seasonal changes of environmental parameters were shown general pattern and related to the red tide mechanism of phytoplankton community. Seasonal variations of dissolved oxygen concentrations were affected by the photosynthetic activity of phytoplankton community and the increase of COD at the bottom water was occurred after the red tide. The standing stocks of phytoplankton in this study area ranged 202 - 1616 Cells·ml^-1 and the bloom(red tide) was formed from April to July. The diatom species, Skeletonema costatum was a dominant species all the year round and the dinoflagellate species, Alexandrium tamarense and Prorocentrum triestinum were red tide species increased standing stocks in phytoplankton bloom.

In the Chinhae Bay, Korea, sedimentation rates and sedimentary record of anthropogenic metal loads were determined by ^210Pb dating and heavy metal analysis of four sediment cores. The sedimentation rates varied from 0.16g/㎠/yr(3.1㎜/yr) at Sta. C4, located within narrow waterway to 0.24g/㎠/yr(4.8㎜/yr) at Sta. C1, located in Haengam Bay. Maximum contents of Mn, Zn, Cu and Cr were observed at Sta. C2 located near the mouth of Masan Bay, while minimum contents were observed at Sta. C4. Mn/Fe ratios at Sta. C2 and Sta. C4 showed gradually increasing and decreasing downward, respectively, in the upper layer of sediment cores. This suggests that Mn may be diagenetically redistributed in highly reduced environment. At Sta. C2, the concentrations of Zn and Cu began to increase from 1920s by anthropogenic input and have been remarkablely increasing since mid 1960s. At Sta. C3, located near Sungpo, anthropogenic input of these two elements has also slightly increased after 1970s. However, pollution of these two elements was not significant in Haengam Bay(Sta. C1) and Chiljun waterway(Sta. C4). The pollution of Co, Ni and Cr was not remarkable in all core samples except surface sediment of Sta. C2. The total input of anthropogenic Zn and Cu since 1920s was estimated to be 28∼792 ㎍/㎠ and 0∼168㎍/㎠, respectively. Sta. C2 showed remarkablely higher values relative to other stations: anthropogenic loads of Zn and Cu constituted 27% and 29% of the total sedimentary inventories at the present day, respectively. Fe, Ni, Cr and Co contents showed good correlation(r>0.8) with each other. Anthropogenic Zn and Cu also showed a very good positive correlation(>0.9). However, correlation between these two group of element was quite scattered, indicating different sources and geochemical behaviors.