Temporal changes in the abundance of the fish-killing dinoflagellate <italic>Karlodinium veneficum</italic> (Dinophyceae) in Tongyeong, Korea
Temporal changes in the abundance of the fish-killing dinoflagellate Karlodinium veneficum (Dinophyceae) in Tongyeong, Korea
ALGAE. 2011. Jun, 26(3): 237-241
Copyright ©2011, The Korean Society of Phycology
This is an Open Access article distributed under the terms of theCreative Commons Attribution Non-Commercial License( permits unrestrictednon-commercial use, distribution, and reproduction in any medium,provided the original work is properly cited.
  • Received : June 06, 2011
  • Accepted : August 08, 2011
  • Published : June 30, 2011
Export by style
Cited by
About the Authors
Tae-Gyu Park
Southeast Sea Fisheries Research Institute, National Fisheries Research and Development Institute (NFRDI), Tongyeong650-943, Korea
Yu-ran Ok
Southeast Sea Fisheries Research Institute, National Fisheries Research and Development Institute (NFRDI), Tongyeong650-943, Korea
Young-Tae Park
Southeast Sea Fisheries Research Institute, National Fisheries Research and Development Institute (NFRDI), Tongyeong650-943, Korea
Chang-Kyu Lee
Southeast Sea Fisheries Research Institute, National Fisheries Research and Development Institute (NFRDI), Tongyeong650-943, Korea
The toxic dinoflagellate Karlodinium veneficum has been implicated in numerous fish kill events around the world.Since this species commonly co-occurs with other morphologically similar dinoflagellates, field monitoring of this species in natural waters via light microscopy only has been problematic. In this study, we investigated temporal changes in K. veneficum’s abundance in the waters of Obido, Tongyeong, using a species-specific real-time polymerase chain reaction (PCR) assay. The field survey, from April to December 2010, revealed K. veneficum occurred at low densities (12 to 425 cells L ?1 ) during this time and that cell numbers peaked in June (early summer in Korea), indicating this species generally occurs in the warmer season (mostly at 16.9-22.3°C and 33.4-34.5‰) in the Obido area.
Karlodinium veneficum (Ballantine) J. Larsen, a mixotrophic dinoflagellate with a worldwide distribution,has been implicated in numerous fish kill events around the world (Place et al. 2008). K. veneficum produces water-soluble toxins that kill fish through gill disruption;however, researchers have successfully determined the structure of these karlotoxins (KmTxs), as they occur in K. veneficum (Kempton et al. 2002, Place et al. 2008). K.veneficum superficially resembles other small dinoflagellates< 15 ㎛ in size, including Pfiesteria piscicida and P. shumwayae , which commonly co-occur with K. veneficum in the marine environment (Litaker et al. 2005, Garcés et al. 2006). These species are characterized by their distinct Kofoidian thecal plate formula. Definitive identification of these dinoflagellates relies on ultrastructural analyses via scanning electron microscopy (SEM), which are labor-intensive and unsuitable for rapid sample processing(Bergholtz et al. 2006, Garces et al. 2006). The real-time polymerase chain reaction (PCR) technique very sensitively detects and quantifies DNA over a broad dynamic range (Walker 2002). Certain studies have used this method for detecting and quantifying a number of dinoflagellates (Bowers et al. 2000, Park et al. 2009). A previous study developed the TaqMan and SYTO9 format real-time PCR probes for K. veneficum , and these probes showed comparable results and high detection sensitivities(Park et al. 2009). In this study, we used a TaqManbased real-time PCR probe that does not require a melting curve analysis to investigate temporal variations of K.veneficum abundances in Obido waters, Tongyeong, the location of many finfish farms.
- Culture and analysis of environmental factors
We obtained Karlodinium veneficum (CCMP 415) from the Provasoli-Guillard National Center for Culture of Marine Phytoplankton (CCMP). The culture was maintained in 30‰ f/2 medium (Guillard and Ryther 1962), without sodium silicate, at 20°C, under cool white fluorescent lamps (100-㎛ol photons m -2 s -1 ) on a 12 : 12-h light : dark cycle. Surface water temperature and salinity were measured in situ with a water quality monitor (YSI 600 XL; YSI Nanotech, Yellow Spring, OH, USA).
- Water sample collection and DNA extraction
From April through December 2010, we collected 250 mL surface water samples, at 1 month intervals, from each of 12 stations in Obido, Tongyeong, Korea ( Fig. 1 ). We filtered the water samples onto a 1.2 ㎛ pore, 25 mm diameter glass microfiber GF/C filter (Whatman Ltd., Maidstone, England), placed each filtered sample in a 2 mL microcentrifuge tube, and stored it at -70°C until DNA extraction. To prevent target DNA degradation, we processed these filtering samples upon a research vessel and extracted the samples genomic DNA from the samples within 2 months, using a phenol-chloroform extraction protocol (Hosoi-Tanabe and Sako 2005).
- Real-time PCR condition
We used the following reagents to create the reaction mixture, to a final volume of 10 μL : 5 μL of platinum quantitative PCR supermix-UDG (Invitrogen, Eugene, OR, USA); forward and reverse primers, each at a final concentration of 0.3 μM; fluorogenic probe at a final concentration of 0.1 μM; 0.5 μL of template DNA (Park et al. 2009); and PCR grade water ( Table 1 ). The thermal cycling condition comprised 2 min at 50°C and 2 min at
Primers and TaqMan probe for the Karlodinium veneficum-specific real-time polymerase chain reaction assayPrimers / probes are labeled: F, forward; R, reverse; P, probe.
PPT Slide
Lager Image
Primers and TaqMan probe for the Karlodinium veneficum-specific real-time polymerase chain reaction assay Primers / probes are labeled: F, forward; R, reverse; P, probe.
PPT Slide
Lager Image
Surface water sample collection locations for this study.
95°C, followed by 45 ten-s cycles at 95°C and 45 s at 60°C. All samples were analyzed in triplicate. We collected the fluorescence data at the end of each cycle, while a Rotor-Gene 6000 instrument (Corbett Research, Sydney, Australia) automatically determined the cycle threshold. To remove the surface waters’ PCR inhibitors, we diluted the template DNA tenfold before use.
- Construction of the standard curve for cell quantification
Before harvesting the cells (12,000 cells), we collected the laboratory-cultured K. veneficum and estimated its cell numbers via light microscopy (LM). After extracting the DNA, we used 10-fold serial dilutions of the DNA extracts to construct the standard curve (triplicate measurements by means of real-time PCR). To evaluate the success of the real-time PCR measurements, we calculated the correlation coefficient (r 2 ), reaction efficiency [-1 + 10 (-1/slope) ], slope (M), and intercept (B), using the Rotor-Gene software version 1.7 (build 61; Corbett Research, Cambridge, UK). In the environmental samples, we calculated the target species’ cell numbers as C t values and measured them via comparison with the standard curve. In addition, we observed the surface water samples via LM to check the K. veneficum cell numbers.
PPT Slide
Lager Image
A standard Karlodinium veneficum curve showing the linear relationship between the Ct values and cell numbers from the K. veneficum-specific assay (r2 = 0.993). The standard errors from each set of three measurements are shown as error bars.
PPT Slide
Lager Image
(A) Temporal variations in temperature and salinity of surface waters in Obido. (B) Temporal variations in Karlodinium veneficum abundance in Obido Tongyeong from April through December 2010 as quantified by real-time polymerase chain reaction. The values are the means of the triplicate wells.
We constructed a standard curve with known cell numbers and established a strong linear relationship between the Ct and the log of the starting cell number, with a correlation coefficient (r 2 ) ≥ 0.993 ( Fig. 2 ). The assay could detect less than one K. veneficum cell in a reaction.
The field survey of the Obido waters showed that K. veneficum cell concentrations were generally low ( Table 2 , Fig. 3 ). The 12 sampling stations’ average cell numbers ranged from 12 to 425 cells L -1 , and these cell numbers increased to 425 cells L-1 in June. K. veneficum was more abundant in early summer in the Obido area. The microscopic analysis revealed low K. veneficum and Karlodinium spp. cell abundances during the survey, and we observed these species only in samples that tested positive via the real-time PCR assay (Table 2). Surface water temperature and salinity ranged from 13.4-24.3°C and 31.3-34.8‰, respectively ( Fig. 3 ).
Researchers have used a number of molecular methods, including real-time PCR, fluorescent in situ hybridization (FISH), sandwich hybridization, competitive PCR, a heteroduplex mobility assay, and fluorescent fragment PCR, to identify dinoflagellates rapidly (Oldach et al. 2000, Haywood et al. 2007, Park et al. 2007). TaqMan based real-time PCR probes have been previously designed to the internal transcribed spacer (ITS) rDNA and small subunit rDNA for the quantitative detection of K. veneficum (Handy et al. 2008, Park et al. 2009). Studies have extensively tested those species-specific assays against related organisms for their assay specificity and have successfully used these assays specifically for detecting K. veneficum in environmental samples (Handy et al. 2008, Park et al. 2009). The real-time PCR assay this study used specifically and sensitively detected K. veneficum , allowing us to identify low quantities of this dinoflagellate in our water samples (below one cell per reaction;
Karlodinium veneficum abundance in Obido Tongyeong from April through December 2010 as measured by real-time polymerase chain reactionValues are the positive detection means: +, positive detection; ?, negative detection by light microscopy (LM) analysis.
PPT Slide
Lager Image
Karlodinium veneficum abundance in Obido Tongyeong from April through December 2010 as measured by real-time polymerase chain reaction Values are the positive detection means: +, positive detection; ?, negative detection by light microscopy (LM) analysis.
the real-time PCR could theoretically detect even one copy of the dinoflagellate’s DNA). The rDNA-based real-time PCR probe possesses such a high sensitivity because the rDNA in most eukaryotes is repeated in tandem at a high copy number. For example, one study reports 100 to 200 copies in one P. piscicida cell (Saito et al. 2002).
K. veneficum commonly co-occurs with morphologically similar species, such as Pfiesteria species, and research has correlated K. veneficum with numerous fish kill events in many countries (Fensin 2006, Place et al. 2008). Small gymnodinioid dinoflagellates, including K. veneficum , have been associated with toxic activity since the 1950s (Ballantine 1956, Place et al. 2008). This species produces a suite of compounds with hemolytic, cytotoxic, and ichthyotoxic properties (Deeds et al. 2002) which are often known as KmTxs. In laboratory bioassays, the purified toxins cause the deaths of supportive cells in menhaden gills and eventually result in fish mortality (Deeds et al. 2006). In the present study, a temporal survey of K. veneficum cell densities in Obido waters shows K. veneficum (maximum 425 cells L -1 ) mostly peaked in June, indicating potential, early-summer KmTx fish kills in the Obido area (16.9-22.3°C and 33.4-34.5‰) if blooms occur during favorable environmental conditions. In K. veneficum cells, the KmTxs’ toxicities are KvTX1, 11.6 ± 5.4 ng mL -1 and KvTX2, 47.7 ± 4.2 ng mL -1 at 4.0 × 10 6 cells L -1 (Galimany et al. 2008). Researchers have generally reported that fish kill events in nature correlate with this species when it is at over 300 cells mL -1 . Although studies have also reported negative effects on marine animals, such as mussels, at pre-bloom concentrations (Galimany et al. 2008), the cell amounts that this study found might have negligible effects on aquaculture animals such as oysters, mussels, and finfishes in Obido waters.
In conclusion, the real-time PCR assay was highly sensitive and specific for detecting and quantifying K. veneficum in the environment, and we successfully implemented this real-time PCR assay in a distributional study of this species in the Obido area. The results of this field survey via real-time PCR suggests K. veneficum occurs commonly in the warmer season in the Obido area and that researchers need to make ongoing investigations of the relationship between environmental factors and cell occurrences to illuminate the bloom dynamics of K. veneficum .
We thank Hyun-Min Hong of the National Fisheries Research and Development Institute (NFRDI) for technical support regarding real-time PCR. We are also grateful to the NFRDI personnel for providing water samples. This work was funded by a grant from NFRDI (RP-2011-ME-023).
Ballantine D 1956 Two new marine species ofGymnodiniumisolated from the Plymouth area J. Mar. Biol. Assoc. U. K 35 467 - 474
Bergholtz T , Daugbjerg N , Moestrup Ø , Fernández-Tejedor M 2006 On the identity ofKarlodinium veneficumand description ofKarlodinium armigersp. nov. (Dinophyceae) based on light and electron microscopy nuclear-encoded LSU rDNA and pigment composition J. Phycol 42 170 - 193
Bowers H. A , Tengs T , Glasgow H. B , Burkholder J. M , Rublee P. A , Oldach D. W 2000 Development of real-time PCR assays for rapid detection ofPfiesteria piscicidaand related dinoflagellates Appl. Environ. Microbiol 66 4641 - 4648
Deeds J. R , Reimschuessel R , Place A. R 2006 Histopathological effects in fish exposed to the toxins fromKarlodinium micrum J. Aquat. Anim. Health 18 136 - 148
Deeds J. R , Terlizzi D. E , Adolf J. E , Stoecker D. K , Place A. R 2002 Toxic activity from cultures ofKarlodinium micrum(=Gyrodinium galatheanum) (Dinophyceae): a dinoflagellate associated with fish mortalities in an estuarine aquaculture facility Harmful Algae 1 169 - 189
Fensin E. E 2006. Impact of tropical storms and drought on the dinoflagellatesKarlodinium micrumandProrocentrum minimumin estuarine rivers of North Carolina USA Afr. J. Mar. Sci 28 277 - 281
Galimany E , Place A. R , Ramón M , Jutson M , Pipe R. K 2008 The effects of feedingKarlodinium veneficum(PLY # 103;Gymnodinium veneficumBallantine) to the blue musselMytilus edulis Harmful Algae 7 91 - 98
Garcés E , Fernandez M , Penna A , Van Lenning K , Gutierrez A , Camp J , Zapata M 2006 Characterization of NW MediterraneanKarlodiniumspp. (Dinophyceae) strains using morphological molecular chemical and physiological methodologies J. Phycol 42 1096 - 1112
Guillard R. R. L , Ryther J. H 1962 Studies of marine planktonic diatoms. ?.Cyclotella nanaHustedt andDetonula confervacea(cleve) Gran. Can Can. J. Microbiol 8 229 - 239
Handy S. M , Demir E , Hutchins D. A , Portune K. J , Whereat E. B , Hare C. E , Rose J. M , Warner M , Farestad M , Cary S. C , Coyne K. J 2008 Using quantitative real-time PCR to study competition and community dynamics among Delaware Inland Bays harmful algae in field and laboratory studies Harmful Algae 7 599 - 613
Haywood A. J , Scholin C. A , Marin R. 3rd , Steidinger K.A , Heil C , Ray J 2007 Molecular detection of the brevetoxin-producing dinoflagellateKarenia brevisand closely related species using rRNA-targeted probes and a semiautomated sandwich hybridization assay J. Phycol 43 1271 - 1286
Hosoi-Tanabe S , Sako Y 2005 Species-specific detection and quantification of toxic marine dinoflagellatesAlexandrium tamarenseandA. catenellaby real-time PCR assay Mar. Biotechnol 7 506 - 514
Kempton J. W , Lewitus A. J , Deeds J. R , Law J. M , Place A. R 2002 Toxicity ofKarlodinium micrum(Dinophyceae) associated with a fish kill in a South Carolina brackish retention pond Harmful Algae 1 233 - 241
Litaker R. W , Steidinger K. A , Mason P. L , Landsberg J. H , Shields J. D , Reece K. S , Haas L. W , Vogelbein W. K , Vandersea M. W , Kibler S. R , Tester P. A 2005 The reclassification ofPfiesteria shumwayae(Dinophyceae):Pseudopfiesteriagen Nov. J. Phycol 41 643 - 651
Oldach D. W , Delwiche C. F , Jakobsen K. S , Tengs T , Brown E. G , Kempton J. W , Schaefer E. F , Bowers H. A , Glasgow H. B. Jr , Burkholder J. M , Steidinger K. A , Rublee P. A 2000 Heteroduplex mobility assay-guided sequence discovery: elucidation of the small subunit (18S) rDNA sequence ofPfiesteria piscicidaand related dinoflagellates from complex algal culture and environmental sample DNA pools Proc. Natl. Acad. Sci. U. S. A 97 4303 - 4308
Park T. -G , de Salas M. F , Bolch C. J. S , Hallegraeff G. M 2007 Development of a real-time PCR probe for quantification of the heterotrophic dinoflagellateCryptoperidiniopsis brodyi(Dinophyceae) in environmental samples Appl. Environ. Microbiol 73 2552 - 2560
Park T. -G , Park Y. -T , Lee Y 2009 Development of a SYTO9 based real-time PCR probe for detection and quantification of toxic dinoflagellateKarlodinium veneficum(Dinophyceae) in environmental samples Phycologia 48 32 - 43
Place A. R , Saito K , Deeds J. R , Robledo J. A. F , Vasta G. R , Botana L. M 2008 A decade of research onPfiesteriaspp. and their toxins: unresolved questions and an alternative hypothesis InSeafood and Freshwater Toxins: Pharmacology Physiology and Detection CRC Press New York 717 - 751
Saito K , Drgon T , Robledo J. A. F , Krupatkina D. N , Vasta G. R 2002 Characterization of the rRNA locus ofPfiesteria piscicidaand development of standard and quantitative PCR-based detection assays targeted to the nontranscribed spacer Appl. Environ. Microbiol 68 5394 - 5407
Walker N. J 2002 Tech. Sight. A technique whose time has come Science 296 557 - 559