The use of antifouling booster biocides on boats and ships is of environmental
concern as the leached products can affect non-target, highly susceptible
phytoplanktonic organisms. Appropriate assessment of whether or not estuarine/marine
phytoplankton are potentially at risk should include a combination of approaches,
investigating toxic effects for both single species and natural phytoplankton
communities and ideally include field verifications. This research addresses the
application and comparison of methods to investigate toxic responses to four antifouling
biocides Irgarol 1051®, diuron, Sea-Nine 211® and zinc pyrithione in laboratory-based
experiments with single species and using natural phytoplankton assemblages. The
applicability of photosynthetic parameters and pigment:chlorophyll-α ratios as
biomarkers was initially employed in unialgal experiments. Variations in results for
pigment:chlorophyll-a ratios following toxic exposures indicate that care must be taken
when using CHEMTAX estimations and that further research into this topic is needed.
Compositional changes in natural phytoplankton assemblages under toxicant
exposure were evaluated using standard techniques (microscopy) and were compared to
group-specific biomass estimation derived from CHEMTAX-High Performance Liquid
Chromatography. This broad approach proved effective in detecting changes in the main
phytoplankton groups, with prasinophytes and prymnesiophytes proving most
susceptible and chlorophytes and dinoflagellates being comparatively resistant to the
PSII inhibitor Irgarol 1051®. In addition, the impact of selected antifouling agents on
photosynthesis and pigment chemotaxonomy was investigated for a natural
phytoplankton community. Pigment signatures were determined by HPLC and growth
was determined by Analytical Flow Cytometry (AFC). Primary production (estimated by
14C-uptake) was compared to photosynthetic efficiency (FV/FM) measured using Fast
Repetition Rate Fluorescence (FRRF). Differences in species-specific sensitivity of the
phytoplankton community were detected through pigment composition after 72 h
exposures to zinc pyrithione (5 µg 1ˉ¹) and Sea-Nine 211® (10 µg lˉ¹) . The pigment
zeaxanthin was proportionally increased indicating a relative increase in Cyanophyceae.
This effect was corroborated by AFC. Both techniques (14C-uptake and FRRF) were in
good agreement (r = 0.88) suggesting the impairment of primary production and FV/FM
following exposure to the selected toxicants.
Phytoplankton responses to toxicants may be influenced by fluctuations in a variety
of environmental factors. The nutrient regime may alter the outcome of contamination
by influencing the susceptibility of phytoplankton to a toxicant. A preliminary
investigation of such effects on biocidal toxicity was conducted under controlled
laboratory conditions to determine the extent of nutrient influence. Results indicated the
influence of nutrient addition on the Irgarol 1051® toxic responses to cyanophytes.
Besides experimental approaches, data were supplemented with a pilot survey in
Plymouth coastal waters. Current concentrations of biocides together with environmental
and biological data for this survey are presented and discussed as a diagnosis that
provides an outline for future research.Plymouth Marine Laborator