Survival and growth of Cochlodinium polykrikoides red tide after addition of yellow loess.

We examined the survival rate of Cochlodinium polykrikoides after yellow loess addition and conducted culture experiments to investigate the possibility that red tides maybe caused by C. polykrikoides individuals that are precipitated when loess is added. At least 15% of the C. polykrikoides cells that precipitated to the bottom layer either by the addition of loess or no addition survived for 1 week at all growth phases, rather than disappearing immediately after precipitating. However no live cells were observed after 20 days, regardless of phase or loess addition. In the exponential phase, the number of C. polykrikoides cells increased to >2886 cells ml(-1) after loess was added. However in the stationary phase, the number of cells did not increase until 18 days. In the exponential phase, those C. polykrikoides that survived precipitation caused by scattering loess on cultures did not appear to have the ability to cause red tides again because of the short red tide periods in the field, long lag time after loess addition, and low survival rate after loess addition.

[1]  Young Sik Lee Estimation of Cochlodinium polykrikoides growth potential using a dialysis membrane. , 2008, Journal of environmental biology.

[2]  Young Sik Lee Utilization of various nitrogen, phosphorus, and selenium compounds by Cochlodinium polykrikoides. , 2008, Journal of environmental biology.

[3]  J. Choi,et al.  Field experiments on mitigation of harmful algal blooms using a Sophorolipid—Yellow clay mixture and effects on marine plankton , 2008 .

[4]  Young Sik Lee Factors affecting outbreaks of high-density Cochlodinium polykrikoides red tides in the coastal seawaters around Yeosu and Tongyeong, Korea. , 2006, Marine pollution bulletin.

[5]  Y. Yoon,et al.  Effects of Light Quantity and Quality on the Growth of the HarmfulDinoflagellate, Cochlodinium polykrikoides Margalef (Dinophyceae) , 2006 .

[6]  Sang Yong Lee,et al.  Factors affecting outbreaks of Cochlodinium polykrikoides blooms in coastal areas of Korea. , 2006, Marine pollution bulletin.

[7]  Hyun-Woo Lee,et al.  A sulfur hexafluoride‐based Lagrangian study on initiation and accumulation of the red tide Cochlodinium polykrikoides in southern coastal waters of Korea , 2005 .

[8]  J. Choi,et al.  Synergistic effect of sophorolipid and loess combination in harmful algal blooms mitigation. , 2004, Marine pollution bulletin.

[9]  P. Ralph,et al.  APPARENT LIGHT REQUIREMENT FOR ACTIVATION OF PHOTOSYNTHESIS UPON REHYDRATION OF DESICCATED BEACHROCK MICROBIAL MATS 1 , 2002 .

[10]  H. Oh,et al.  Life cycle of the ichthyotoxic dinoflagellate Cochlodinium polykrikoides in Korean coastal waters , 2007 .

[11]  M. Iwataki,et al.  Effects of temperature, salinity and light intensity on the growth of a harmful dinoflagellate Cochlodinium polykrikoides Margalef occurring in coastal waters of west Kyushu, Japan , 2005 .

[12]  Dae-Il Kim,et al.  Effects of temperature, salinity and irradiance on the growth of the harmful red tide dinoflagellate Cochlodinium polykrikoides Margalef (Dinophyceae) , 2004 .

[13]  Yong-Chul Cho,et al.  The Outbreak, Maintenance, and Decline of the Red Tide Dominated by Cochlodinium polykrikoides in the Coastal Waters off Southern Korea from August to October, 2000 , 2002 .

[14]  Y. Jong,et al.  Removal Efficiency of Cochiodinium polykrikoides by Yellow Loess , 1998 .

[15]  Y. Yoshida,et al.  Physiological and Ecological Studies on Red Tide-I , 1957 .