Chapter Twelve - In Situ and Real-Time Identification of Toxins and Toxin-Producing Microorganisms in the Environment

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Introduction

Bloom-forming species of algae and cyanobacteria, along with the diverse array of toxins they produce, presently represent a clear threat in coastal regions throughout the world's oceans that is likely to worsen under the anticipated effects of climate change [1]. Harmful algal blooms (HABs) and their toxins adversely affect human, animal and ecosystem health and can cause extensive damage to regional and local economies via fishery closures, water quality/contamination issues and impacts on tourism and recreational water use. Effective HAB management and mitigation efforts rely heavily on the availability of timely and actionable information about the development, trajectory and toxicity of bloom populations. Considerable work is being directed at establishing location-specific early warning capabilities and developing models to support regional forecasts of bloom dynamics and toxicity [2], [3]. In the same way that real or near-real time observing data are ingested into and assimilated by weather forecast models, such data streams for HAB-specific physicochemical and biological variables are essential to producing accurate forecasts of bloom events and assessing their associated risks.

Over the past decade significant advances have been made in the development of deployment platforms and sensor technologies for the in situ and real-time detection of HAB species and toxins. The ability to measure concentrations of both organisms and toxins is essential given that cellular toxicity, and thus the potential to realize many of the adverse impacts identified above, is highly variable and influenced by a complex suite of interactions between organisms and their environment (e.g., Ref. [4]). A wide range of autonomous and field-deployable sensor technologies is currently available to provide sustained observations of HAB species and toxins, and these are described below with a primary focus on the actual technologies and their applications, along with brief, high-level explanations of the theory/methodology underpinning their operation. The prospects for integrating certain of these technologies into the rapidly advancing infrastructure of observing networks in support of HAB management and mitigation are also considered.

Section snippets

Satellite/Airborne Technologies

Remote sensing has long been considered an obvious tool for studying the distribution of HAB organisms over larger spatial and shorter time scales than are possible with ship-based sampling [5], [6]. Legacy and next-generation instrumentation and sensors, including Sea-viewing Wide Field-of-view Sensor (SeaWiFS), Moderate Resolution Imaging Spectroradiometer (MODIS), Medium Resolution Imaging Spectrometer (MERIS) and the ocean and land colour instrument (OLCI) sensor on Sentinel-3 (Fig. 1), are

In-water deployment platforms

HAB and toxin detection have often relied on traditional methods such as volunteer sampling networks and shore-based sampling, often with event-based or trigger-based tiered approaches [22], [23]. Although extremely valuable, these shore-based programs frequently under sample the coastal ocean where bloom events typically originate. It has long been recognized that augmented sampling based on an understanding of the inherent variability of a system from point (shore-based observations,

FlowCAM (Fluid Imaging Technologies, Inc.)

The FlowCAM combines flow cytometry with light microscope-like optics to detect and monitor for the presence of HAB species. Although primarily a benchtop instrument, its portability outside of the laboratory has been demonstrated by dockside and shipboard applications. Material for analysis can be introduced either as discrete water samples or via integration with a continuous flow-through pumping system. A computer-controlled syringe pump pulls fluid through a flow cell oriented perpendicular

The Future Is Now: Integrating Harmful Algal Bloom Detection Technologies Into Observing Networks

Development of coordinated observing networks capable of detecting, monitoring and predicting HAB events has long been a goal of the oceanographic community. In 2001, the ICES-IOC Working Group on Harmful Algal Bloom Dynamics proposed a workshop ‘Real Time Observation Systems Applied to Harmful Algal Bloom Dynamics Studies and Global Ecosystem Functioning’, which was strongly endorsed by both GOOS and the Global Ecology and Oceanography of Harmful Algal Blooms program. This ultimately led to

Disclaimer

This publication does not constitute an endorsement of any commercial product or intend to be an opinion beyond scientific or other results obtained by the National Oceanic and Atmospheric Administration (NOAA). No reference shall be made to NOAA, or this publication furnished by NOAA, to any advertising or sales promotion, which would indicate or imply that NOAA recommends or endorses any proprietary product mentioned herein, or which has as its purpose an interest to cause the advertised

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References (94)

  • I.C. Robbins et al.

    Improved monitoring of HABs using autonomous underwater vehicles (AUV)

    Harmful Algae

    (2006)
  • J. Zhao et al.

    Three-dimensional structure of a Karenia brevis bloom: observations from gliders, satellites, and field measurements

    Harmful Algae

    (2013)
  • E. Berdalet et al.

    Understanding harmful algae in stratified systems: review of progress and future directions

    Deep-Sea Res. II

    (2014)
  • C.A. Scholin

    Ecogenomic sensors

  • C.J. Lorenzen

    A method for the continuous measurement of in vivo chlorophyll concentration

    Deep Sea Res. Oceanogr. Abstr.

    (1966)
  • Z.S. Kolber et al.

    Measurements of variable chlorophyll fluorescence using fast repetition rate techniques: defining methodology and experimental protocols

    Biochim. Biophys. Acta Bioenerg.

    (1998)
  • T. Bjørnland et al.

    Gyroxanthin – the first allenic acetylenic carotenoid

    Tetrahedron

    (2000)
  • G.S. Bullerjahn et al.

    Global solutions to regional problems: collecting global expertise to address the problem of harmful cyanobacterial blooms. A Lake Erie case study

    Harmful Algae

    (2016)
  • A.B. Bochdansky et al.

    Mesoscale and high-frequency variability of macroscopic particles (> 100μm) in the Ross Sea and its relevance for late-season particulate carbon export

    J. Mar. Syst.

    (2017)
  • G.J. Doucette et al.

    Remote, subsurface detection of the algal toxin domoic acid onboard the environmental sample processor: assay development and field trials

    Harmful Algae

    (2009)
  • J.P. Ryan et al.

    Boundary influences on HAB phytoplankton ecology in a stratification-enhanced upwelling shadow

    Deep Sea Res. II

    (2014)
  • Y. Zhang et al.

    Tracking and sampling of a phytoplankton patch by an autonomous underwater vehicle in drifting mode

  • E.J. Buskey et al.

    Use of the FlowCAM for semi-automated recognition and enumeration of red tide cells (Karenia brevis) in natural plankton samples

    Harmful Algae

    (2006)
  • L. Reverté et al.

    Alternative methods for the detection of emerging marine toxins: biosensors, biochemical assays and cell-based assays

    Mar. Drugs

    (2014)
  • F. Colas et al.

    A surface plasmon resonance system for the underwater detection of domoic acid

    Limnol. Oceanogr. Methods

    (2016)
  • S. Devlin et al.

    Next generation planar waveguide detection of microcystins in freshwater and cyanobacterial extracts, utilising a novel lysis method for portable sample preparation and analysis

    Anal. Chim. Acta

    (2013)
  • R.A. Devlin et al.

    Physical and immunoaffinity extraction of paralytic shellfish poisoning toxins from cultures of the dinoflagellate Alexandrium tamarense

    Harmful Algae

    (2011)
  • S.E. McNamee et al.

    Development of a planar waveguide microarray for the monitoring and early detection of five harmful algal toxins in water and cultures

    Environ. Sci. Technol.

    (2014)
  • J.L. Kleindinst et al.

    Categorizing the severity of paralytic shellfish poisoning outbreaks in the Gulf of Maine for forecasting and management

    Deep Sea Res. II

    (2014)
  • K. Davidson et al.

    Forecasting the risk of harmful algal blooms

    Harmful Algae

    (2016)
  • K. Davidson et al.

    A large and prolonged bloom of Karenia mikimotoi in Scottish waters in 2006

    Harmful Algae

    (2009)
  • P.A. Gillibrand et al.

    Individual-based modelling of the development and transport of a Karenia mikimotoi bloom on the North-west European continental shelf

    Harmful Algae

    (2016)
  • D.M. Anderson et al.

    Progress in understanding harmful algal blooms: paradigm shifts and new technologies for research, monitoring, and management

    Ann. Rev. Mar. Sci.

    (2012)
  • E. Granéli et al.

    Chemical and physical factors influencing toxin content

  • P.A. Tester et al.

    An expatriate red tide bloom: transport, distribution, and persistence

    Limnol. Oceanogr.

    (1991)
  • B.A. Keafer et al.

    Use of remotely-sensed sea surface temperatures in studies of Alexandrium tamarense bloom dynamics

  • S. Alvain et al.

    Seasonal distribution and succession of dominant phytoplankton groups in the global ocean: a satellite view

    Global Biogeochem. Cycles

    (2008)
  • T.K. Westberry et al.

    An improved bio-optical model for the remote sensing of Trichodesmium spp. blooms

    J. Geophys. Res.

    (2005)
  • T.T. Wynne et al.

    Relating spectral shape to cyanobacterial blooms in the Laurentian Great Lakes

    Int. J. Remote Sens.

    (2008)
  • H. Dierssen et al.

    Red and black tides: quantitative analysis of water-leaving radiance and perceived color for phytoplankton, colored dissolved organic matter, and suspended sediments

    Limnol. Oceanogr.

    (2006)
  • S.L. Palacios

    Identifying and Tracking Evolving Water Masses in Optically Complex Aquatic Environments

    (2012)
  • M. Kahru et al.

    Ocean color reveals increased blooms in various parts of the world

    EOS

    (2008)
  • W.W. Chen et al.

    Automatic red tide detection from MODIS satellite images

  • P. Lyu et al.

    Autonomous cyanobacterial harmful algal blooms monitoring using multirotor UAS

    Int. J. Remote Sens

    (2017)
  • V. Klemas

    Remote sensing of algal blooms: an overview with case studies

    J. Coast. Res.

    (2011)
  • P. Andersen

    Design and Implementation of Some Harmful Algal Monitoring Systems

    (1996)
  • M. Babin et al.

    Real-time Coastal Observing Systems for Marine Ecosystem Dynamics and Harmful Algal Blooms: Theory, Instrumentation and Modelling

    (2008)
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