viously, sample sites should be chosen to avoid such areas if possible. Clearly, there is room for questions or criticism when this dynamic system is modelled from the assumption that bottom sediments, for example in Anderson s work in The Gulf of Maine, are in a static stable condition whereby a sample taken in the fall one year is considered representative of the seed bed the following spring. The fall sample may well contain many freshly formed cysts from that summer s bloom, but by next spring these would be expected to be at least partially disseminated into deeper sediment and possibly replaced by some older cysts of more questionable viability by the processes mentioned above. The crucial question for modelers of how many viable cysts germinate from the proposed seed bed to initiate the next bloom will always be difficult/ practically impossible to demonstrate. How can one know which cysts from the variety of seed beds in shallower to deeper water, potentially excysting at different times, produce which motiles in the water column in coastal regions with a complex interconnected hydrographic system offering different ecological opportunities? Modelers promising long-term forecasting of HAB from cysts in sediment should be expected to take account of the basic factors affecting the sediments, and they are obliged to check simple assumptions made about sediments where possible. For example, if modelers of HAB in the Gulf of Maine had calculated cyst concentrations in the postulated seed bed closer to the postulated time of excystment in the spring, and checked cyst concentrations again soon after excystment, they could see if cyst concentrations were reduced by the amounts required to support the excystment rates assumed in the models. One of the often stated justifications for modeling is that it can expose aspects of science needing further study. I hope the modelers will accept the explanations presented here as an example of this: that inadequate consideration of the dynamics in the sedimentary system contributes to the high level of uncertainty in the models. Behind Andersons complaint about unjust criticism from geologists lies an important principle that is fundamental to how science progresses: scientists have a responsibility to question/ criticize each others work. This is particularly valuable where different disciplines overlap (in this case biology and geology). Geologists know that water content varies between sediment samples, and biologists were made aware of this only when they were not accounting for it in their work. There are simple, standard methods for checking water content, and these were eventually employed by biologists to account for this factor surely a positive response to valuable criticism. From working with both geological and biological aspects of dinoflagellate cysts, I have benefitted greatly from being exposed to and learning from expertise in both fields. I know that HAB science will only benefit from a better understanding of the dynamics of the sedimentary system. References 1. Anderson DM 2018. HAN 59: 4-8 2. Dale B 2001. Sci Total Environ 264: 235240 3. Dale B & M Murphy 2014. Harmful Algae 40: 23-33 Author Barrie Dale, Geosciences Department, University of Oslo, P.O. Box 1047, Blindern, NO-0316 Oslo, Norway Corresponding author: barrie.dale@geo.uio.no HAN contributors follow an honorable tradition of disputation; differences instead of differentials. Figure shows Isaac Newton and Leibniz, protagonists of the most famous intellectual dispute in history. HARMFUL ALGAE NEWS NO. 60 / 2018 5 Harmful Algae News An IOC Newsletter on Toxic Algae and Algal Blooms No. 60 - July 2018 www.ioc-unesco.org/hab Marine eukaryote and HAB monitoring in Japan with next generation technology Sequencing technologies such as Illumina MiSeq have made it possible to obtain billions of sequence reads in a Frequency distribution (%) the surface data was used in this study. Surface seawater (0.5 L) was collected weekly with a plastic bucket during the same period. For MPS-based monitoring based on amplicon-seq of 18S-rRNA gene (V79 region), PCR amplification and 454 pyrosequencing were performed accor Inland Sea, 2-17-5 Maruishi, Hatsukaichi, Hiroshima 739-045, Japan Hiroshi Shimada, Central Fisheries Research Institute of Hokkaido Research Organization, Hamanaka-cho 238, Yoichi, Hokkaido 0468555, Japan Seiji Katakura, City of Mombetsu, Kaiyo-koryukan, Kaiyo-koen, Mombetsu, Hokkaido 094-0031, Jap Quantifying dinoflagellate cysts in bottom sediments: a response to Anderson 2018 Problems associated with quantifying dinoflagellate cysts in bottom sediments featured prominently in Don Anderson s personal retrospective view of his contribution to the early days of HAB cyst research published rece viously, sample sites should be chosen to avoid such areas if possible. Clearly, there is room for questions or criticism when this dynamic system is modelled from the assumption that bottom sediments, for example in Anderson s work in The Gulf of Maine, are in a static stable condition whereby a sa Contribution of marine invertebrates to Ciguatera poisoning : the case study of French Polynesia Reported as early as the 15th century by explorers, ciguatera fish poisoning (CFP) is the most prominent non-bacterial seafood poisoning worldwide. Widespread in tropical and subtropical regions, CFP res au développement du phytoplancton ciguatérigène en Polynésie française: CARISTO-Pf n7937/MSR/REC of 4th of December 2015 and Arrêté nHC/491/ DIE/BPT of 30th March 2016). Figure 2. Comparison of Pacific ciguatoxins (P-CTXs) profiles in A) in vitro cultures of Gambierdiscus polynesiensis (TB-92 [14]) Solid Phase Adsorption Toxin Tracking (SPATT) technology for field monitoring of Gambierdiscus toxins with passive samplers Ciguatera poisoning is a seafood intoxication classically associated with the consumption of tropical coral reef fish contaminated with ciguatoxins (CTXs), although some marine Fig. 2. Summary of the results demonstrating that SPATT passive sampling could advantageously contribute to the reinforcement of ciguateric risk assessment and management programmes as a supplementary tool. or of very low densities of toxic Gambierdiscus cells. However, CTXs were detected in numero New limits of Ostreopsis distribution in the Bay of Biscay: a first report of Ostreopsis in Santander Bay, Cantabria (Northern Spain) Fig. 1. Location of sampling sites The genus Ostreopsis encompasses benthic dinoflagellates that represent one of the main microalgal threats for beach tourism in w Bloom of Ostreopsis cf. siamensis in Lisbon Bay Fig. 1. Sampling sites on Lisbon Bay Reports of benthic HAB events have increased during the last decade in temperate regions. These have been associated with proliferations of benthic toxic dinoflagellates, in particular species of Ostreopsis. The M Table1 1- List - List the macroalgaecommunity communityspecies species Table ofof the macroalgae ITSA and ITSB primers [6]. Phylogenetic analysis (not Asparagopsis armata Corallina sp. shown) revealed that all the Caulacanthus ustulatus Cystoseira sp. studied sequences grouped Ceramiacea Derbesia s A possible link between the breakdown of a fertilizer tank and a toxic Pseudonitzschia bloom fishery, leaving toxic blooms undetected in other areas. By the time of the bloom, the diatom community primarily consisted of P. seriata (Fig. 3). Identification of P. seriata as the potential culprit diat Fig. 3. Pseudo-nitzschia seriata TEM micrograph of the poroid structure arranged within the striae consisting of two outer rows of larger poroids and one or two inner rows of smaller poroids. induce DA production in P. australis [7], and the most potent DA-inducing N form has been shown to be urea. Golden alga Prymnesium parvum Carter bloom off Azhikode, southwest India In September 2009, during the southwest monsoon season, a quasi-monospecific bloom of Prymnesium parvum was collected off Azhikode (10o 11 02 N; 76o 09 22 E), on the southwest coast of India (Fig. 1). A conspicuous pale browni Regional Workshop on Monitoring and Management Strategies for Benthic HABs if possible, establish tools for standardized procedures. The exercise is open to the entire international community. The goal of achieving improved assessments of the risks associated with BHABs will help reduce the health, Workshop on morpho-molecular methods for the study of dinoflagellate cysts A workshop on techniques for the morphological and molecular identification of cysts from toxic HAB species, led by Drs Kenneth Neil Mertens, Kirsty Smith, Lesley Rhodes and Lincoln MacKenzie, was held recently at the Cawthro Cawthron Summer Scholar Explores Bloom-Forming Freshwater Cyano bacteria Globally, cyanobacteria blooms in freshwater environments are causing water quality problems and health risks with increasing frequency. New Zealand is no stranger to this, suffering from blooms of toxin-producing cyanobacteria Canadian HAB Scientists Hold Workshop to Establish National Priorities and Develop Research Network A National Harmful Algal Bloom (HAB) workshop was organized and chaired by Dr. Ian Perry at the Institute of Ocean Sciences (IOS), Fisheries and Oceans Canada (DFO), Sidney, British Columbia, July 11- Joint FAO, IAEA, IOC and WHO Technical Meeting for the development of an InterAgency Global Ciguatera Strategy Harmful Algae News has previously brought information on an initiative between the International Atomic Energy Agency (IAEA) Environment Laboratories in Monaco jointly with the Oceanographi 12th Advanced Phytoplankton Course - APC 12 Identification, Taxonomy, Systematics Roscoff Biological Station (France) - 19th May to 8th June 2019 APC12 is organized by the Station Biologique de Roscoff together with the Stazione Zoologica Anton Dohrn and the IOC Science and Communication Centre on H ICHA 2018 News: 669 abstracts evaluated ! 250 orals + 45 ignite talks selected and participants notified ICHA 2018 News: 669 abstracts evaluated ! 9 plenaries confirmed 250 orals + 45 ignite talks selected and participants notified 3 satellite sessions 9 plenaries confirmed 3 satellite sessions