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 diatom for
the toxicity was confirmed by TEM (Fig.
2). P. seriata as the responsible diatom
was not surprising, as it has previously
formed highly toxic blooms in the area
[1]. The cell concentration peaked at
the beginning of the bloom at 110,800
cells L-1 (Fig. 1), while the toxin content
in mussel meat peaked two weeks later
with 47 mg DA kg-1 of mussel meat. This
is a relatively high amount of toxin, considering the low cell concentration.
The reason for the two-weeks temporal difference between DA peaks and
peaks in cell numbers might be due to
the sampling procedure, with irregular
sampling and water samples for phytoplankton monitoring being gathered
on other days than samples for toxin
analyses of shellfish flesh. P. seriata is
known for its ability to produce high
amounts of DA given the appropriate environmental conditions. Several
physical-chemical factors are known
to induce DA production in PN. Silicate
limitation, light and temperature are
well documented as DA inducing factors
for P. seriata, and presence of copepod
grazers is a newly discovered potent inducing factor for DA production [2].
On February 3rd 2016, approximately one month prior to the bloom,
large amounts of liquid nitrogen fertilizer were spilled into the environment
as a result of thebreakdown of a fertilizer storage silo located on the harbour
of Fredericia. The magnitude of this
discharge was arguably around 4000
bloom in Denmark in
2016. Harvest of blue
mussel (Mytilus edulis) by the industry
in the affected areas
was closed as soon
as toxin was detected
in mussel meat and
the mussels already
harvested were discarded. The areas
concerned are usually
very productive and
the closure resulted in
a weekly lost revenue
of >100.000 DKK to
local fishermen. The
fishery was reopened
after 4-5 weeks, under intensified surveillance.
The bloom probably originated northFig. 1. Map of Denmark with approximate locations of the reeast of Horsens Fjord
spective mussel harvesting areas (63, 66, 68, 71), Fredericia (the
(Fig. 1). The first meaorigin of the fertilizer outlet) and Horsens. Credit: openstreetsurements of DA in
map.org
mussel samples were
detected on March 7,
In March and April 2016, a major bloom 2016. During the following weeks, DA
of toxic Pseudo-nitzschia (PN) caused an was detected in adjacent areas along
extensive closure of mussel harvesting the east coast of Jutland. Toxic PN
areas in Denmark due to raised levels blooms are rare in Denmark but these
of domoic acid (DA). Areas close to the specific areas have previously been afeast coast of Jutland (Denmark) were fected [1]. Other areas of Danish coastal
heavily affected by the bloom and sev- waters might likewise be subject to DA
eral productive shellfish areas where accumulation but toxin levels are only
closed for up to five weeks. Cell concen- measured in areas subject to mussel
trations and the PN proportion of the
total planktonic community were relatively low at the time. What caused the
high toxicity?
DA is a potent neurotoxin that bioaccumulates as shellfish and copepods
vector the toxin up the food web. Hereby DA can potentially cause problems
with intoxication of consumers such as
fish, birds, and mammals. The toxin is
known to cause Amnesic Shellfish Poisoning (ASP) in humans. Intoxication
of humans is usually avoided due to
the existence of monitoring and testing
programs of commercially harvested
bivalves worldwide. No human intoxi- Fig. 2. Concentrations of P. seriata cells in the water column and of domoic acid content in
cation was reported during the spring fresh mussel meat during spring 2016 in four different areas along the east coast of Jutland.
HARMFUL ALGAE NEWS NO. 60 / 2018
13
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
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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
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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
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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,
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