Fig. 2. Nodularia spumigena from Lake Forsyth/Te Wairewa at 400 magnification (A) and
blooms of the cyanobacterium at the lake in 2006 (B).
Fig. 3. Eel fishing channels at Lake Forsyth/Te Wairewa (A) and members of the rūnanga of
Wairewa catching eels in the channels by gaffing (B; photo provided by Jack Jacob).
The data from the water samples
indicated that there was seasonal vari-
ation in concentrations of N. spumigena
and nodularin, but that the severity of
the blooms were decreasing over the
study period 8. Being able to maintain
higher lake levels via the new canal may
have contributed to these decreases in
N. spumigena blooms. However, high
concentrations of other phytoplankton
(including cyanobacteria) remain per-
sistent in the lake and it is still consid-
ered hypertrophic 12. In December
2016, a statutory plan for reducing sed-
iment and phosphorus inputs into Lake
Forsyth/Te Wairewa was announced
and this may lead to further reductions
in phytoplankton blooms in the lake.
In the eel samples, higher nodula-
rin concentrations were observed in
the liver of the eels than in the muscle
tissue of the corresponding specimen.
This was consistent with similar studies
on nodularin accumulation in aquatic
animals 4,13,14. The highest nodula-
rin concentrations detected in the eels
from Lake Forsyth/Te Wairewa (29 μg
kg -1 wet-weight in muscle tissue and
147 μg kg -1 wet-weight in liver) 8 were
within the same order of magnitude for
those reported in aquatic organisms
gathered from other ecosystems expe-
riencing N. spumigena blooms (473 μg
kg -1 dry-weight in flounder muscle tis-
14
sue, 139 μg kg -1 dry-weight in mussels
and 399 μg kg -1 dry-weight in floun-
der liver) 4,7,13. Mulvenna et al. 15
suggested a guideline for safe human
consumption of microcystin and/or
nodularin in fish of 24 μg toxin kg -1 (for
a 2-16 year age group). The concentra-
tions in the muscle of shortfin eels from
Lake Forsyth/Te Wairewa exceeded
this suggested safe human consump-
tion guideline only on one occasion (29
μg kg -1 wet weight). Concentrations de-
tected in the liver exceeded the suggest-
ed value in 36 of samples analysed.
Fortunately, local Rūnanga (who are the
main consumers of the eels) currently
remove the liver prior to consumption,
and removal of the gut/organs would
be recommended for anyone consum-
ing aquatic foodstuffs from bloom-af-
fected waters.
Shortfin eels from Lake Forsyth/Te
Wairewa are an important mahinga kai
source for the local rūnanga of Waire-
wa and are a taonga species (treas-
ured species) around New Zealand.
Our study suggested that, provided the
liver (and other intestinal organs) are
removed, the risk of adverse effects to
human health from consumption of
the eels was low 8. The data from our
study also indicated that the concentra-
tions of nodularin in the water column
impacted on the levels detected in the
eels. Therefore, the assumption of low
human health risk may need to be re-
visited now that intense and prolonged
blooms have returned to Lake Forsyth/
Te Wairewa. While the risk to humans
may be considered low, the conse-
quences of nodularin exposure on the
eels remains unknown. We suggest that
better understanding of these effects
and improving knowledge on the trans-
port of nodularin through trophic levels
should be a priority for future research
in this area.
References
1. Woodward CA & J Shulmeister 2005.
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2. Jacobson WEM 1940. Akaroa and Banks
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3. Karjalainen M et al 2003. Environ Toxi-
col 18: 52-60
4. Mazur-Marzec H et al 2007. Environ
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5. Sipiä VO et al 2002. Ecotoxicol Environ
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6. Sipiä VO et al 2004. Environ Toxicol
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8. Dolamore B et al 2016. N Z J Mar Fresh
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235
11. Jellyman DJ & I Cranwell I 2007. The
status of eel stocks in Wairewa (Lake
Forsyth). New Zealand Fisheries Assess-
ment Report 2007/11; New Zealand
Ministry of Fisheries, p 41
12. Schallenberg M & LA Schallenberg
2013. Lake Forsyth/Wairewa: A
literature review. Report No R13/106;
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13. Sipiä VO et al 2001. Environ Toxicol 16:
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Authors
Barbara Dolamore, Ara Institute of Canter-
bury, Christchurch, New Zealand
Jonathan Puddick, Cawthron Institute,
Nelson, New Zealand
Susie Wood, Cawthron Institute and the
Environmental Research Institute, University
of Waikato, Hamilton, New Zealand
Email of corresponding author:
Barbara.Dolamoreara.ac.nz
HARMFUL ALGAE NEWS NO. 56 / 2017
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