David Walker University of Arizona, Environmental Research - - PowerPoint PPT Presentation

david walker university of arizona environmental research
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David Walker University of Arizona, Environmental Research - - PowerPoint PPT Presentation

David Walker University of Arizona, Environmental Research Laboratory dwalker@ag.arizona.edu All reservoirs routinely sampled for anatoxin-a, cylindrospermopsin, microcystin, and saxitoxin. Analyses are done by Dr. Greg Boyer at


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David Walker University of Arizona, Environmental Research Laboratory dwalker@ag.arizona.edu

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  • All reservoirs routinely sampled for

anatoxin-a, cylindrospermopsin, microcystin, and saxitoxin.

  • Analyses are done by Dr. Greg

Boyer at SUNY-CESF (Syracuse).

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Analytical Methods

  • Anatoxin-a, Saxitoxin

– HPLC after fluorescent derivatization.

  • Microcystin

– Protein phosphatase inhibition assay.

  • If greater than 0.5 µg/L, confirmed by

HPLC using a PDA detector.

  • Cylindrospermopsin

– HPLC using a photodiode array detector

  • Detection limit for all assays is less

than 0.1 µg/L

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Anatoxin-a (ethanone, 1-(1R,6R)-9- azabicyclo[4.2.1]non-2-en-2-yl-)

  • It is one of the most potent agonists

at the nicotinic acetylcholine receptor discovered to date.

  • LD50 of 250 µg/L (i.p. mouse).
  • Small molecular size means rapid
  • nset of symptoms (otherwise known

as Very Fast Death Factor).

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Mode of Action

  • Binds to the acetylcholine

receptor and acts as an agonist.

  • Not ejected by the nerve after

binding so impulses do not fade.

  • Additionally, it inhibits

acetylcholinesterase used to inactivate the acetylcholine released by normal nerve impulses.

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  • The result is an overstimulation
  • f chest muscles which may lead

to limp paralysis, dyspnea, cyanosis, cardiac arrhythmia and death.

  • Onset of symptoms is extremely

rapid (< 5 min.).

  • No antidote, supportive care
  • nly.
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Other Anatoxins

  • Homoanatoxin

–Homoanalogue of anatoxin-a. –Toxicity is the same as anatoxin-a.

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Anatoxin-a(S)

  • Much more potent than anatoxin-a
  • r homoanatoxin.
  • LD50 of 20 µg/kg-1 i.p. mouse.
  • The only naturally occurring
  • rganophosphate known.
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History of Anatoxin Production in the Salt River Reservoirs

  • Summer of 2001, called to

investigate a large die-off of Corbicula fluminae in the upper reaches of Saguaro.

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  • During this event, we found 120-

140 µg/L of anatoxin-a.

  • These were the highest levels ever

recorded by the reporting lab and posed an imminent risk to public safety.

  • Levels quickly diminished with

distance toward Stewart Mtn. Dam.

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Suspect Organisms Capable of Anatoxin-a Production

  • Anabaenopsis circinalis
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Cylindrospermopsis raciborskii

– Invasive exotic recently discovered during this project to be in all of the reservoirs surrounding the Valley. – C. raciborskii can produce 3 distinct toxins:

  • Cylindrospermopsin (hepatotoxin)
  • Saxitoxin (hepatotoxin)
  • Anatoxin-a
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  • Most other planktonic forms of toxic

cyanobacteria produce blooms on top of the water.

  • C. raciborskii, however, is always found

well-distributed throughout the water column and has the highest concentrations below the surface.

  • If toxins are produced at depth near the

dam of a reservoir, these could be released into the riverine portion of downstream reservoirs or into rivers/canals.

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Current Fish Kills

  • Starting in May, a fish kill
  • ccurred in Apache from

Roosevelt Dam down to Burnt Corral Campground.

  • Anecdotal reports indicated

thousands to tens of thousands of effected fish of varying species including threadfin shad, bass, bluegill, and carp

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  • A few weeks later, a fish kill
  • ccurred in Canyon.
  • This was followed by a fish kill in

the upper reaches of Saguaro and recently, another fish kill in Apache.

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  • Samples were taken for 133

VOC’s, 16 carbamates, 11

  • rganophosphates, and 9

chlorinated pesticides in each reservoir.

  • All came back as non-detects.
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  • No abnormal pathological findings

upon gross necropsy.

  • Algae identification at all sites

revealed the presence of both C. raciborskii and Anabaenopsis.

  • Thus far, all samples taken for

anatoxin-a, saxitoxin, microcystin, and cylindrospermopsin have come back as non-detectable.

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However,

  • Cylindrospermopsin, microcystin,

and saxitoxin are extremely environmentally stable compounds.

  • The non-linearity of the fish kills

indicate that this was not a spill or an environmentally stable compound.

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  • If hepatotoxicity was involved, there

would be gross pathological evidence.

  • This pathological evidence would be

lacking if neurotoxicity is involved.

  • All physico-chemical parameters are

within “normal” for the time of the year in question.

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  • We investigated the kills days after

they occurred.

  • The half life of anatoxin-a under

laboratory conditions is 5 days.

  • It is inactivated by both sunlight

and highly alkaline conditions.

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  • Under current field conditions in

reservoirs on the Salt River, the half life of anatoxin-a probably drops to hours or even minutes.

  • Difficult to quantify an extremely

fast-acting acetylcholinesterase inhibitor that kills aquatic

  • rganisms leaving no traces in its

wake.

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Data Gaps/Research Needs

  • Increased monitoring efforts on all

reservoirs for potentially toxic

  • rganisms and the toxins

themselves.

  • Monitoring of rivers and canals

downstream of reservoirs.

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  • Genetic isolation of different strains
  • f potentially toxic species.
  • Once these strains have been

identified, we need a better understanding of environmental conditions leading to toxin production.

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  • Biological indicators as early

warning of xenobiotic exposure.

  • Specifically, in vivo measurements

to quantify acetylcholinesterase inhibition in fish, zooplankton, and/or bivalves.

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  • Can be done either colorimetrically
  • r through development of an in

vivo enzyme inhibition assay based upon esterase activity.

  • Controls/baseline values for

individual species could easily be performed in the lab.

  • Once developed, could be

performed in the field in less than

  • ne hour.
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  • Once toxin-producing strains have

been genetically identified, modeling of production, fate, transport, and degradation rates of individual toxins would give some insight into what could be done, from a management standpoint, to alleviate the problem.

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Development of Real-Time Monitoring Buoys

  • Greg Boyer at SUNY already

working on.

  • Fully deployable systems are still

1-2 years away.

  • The single best way to ensure

public safety on the reservoirs surrounding the Valley.

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Robotic Monitoring Platform Buoy

Slide courtesy of Dr. Greg Boyer, SUNY-CESF

Tri-hull buoy containing on-board computer, communications and batteries Solar power unit Profiler - depth controlled by

  • n-board computer

Underwater sensors Anchor lines Meteorological instruments (~8 feet in diameter)

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Optical Biochip Sensor Technology

Slide courtesy of Dr. Greg Boyer, SUNY-CESF

Substrate Thin Film Waveguide Antibody Receptors Biotoxin Detector Solid State Laser Input Non-Harmful Biomaterial Traveling Light Wave

Light is piped through an optical wave-guide whose index of refraction is dependent on surface conditions Antibodies can be used to specifically trap biotoxins on surface with high specificity The change in index of refraction creates a highly sensitive detector

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Near Real Time Data Delivery

Slide courtesy of Dr. Greg Boyer, SUNY-CESF

Land Bridge

Delivering Remote Data

  • Remote data
  • Engaging formats

Scientific Staff Managers / Officials QA/QC intranet Health Officials robotic monitoring buoy

Land Bridge

Delivering Remote Data

  • Remote data
  • Engaging formats

Scientific Staff Managers / Officials QA/QC QA/QC intranet Health Officials robotic monitoring buoy

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Conceptual Water Monitoring Product

Communication Interface

(Secure Cellular/Satellite)

Chemical Sensor Array

(taste and odor compounds)

BioChip Sensor Array

(algal toxins)

DNA Sensor Array

(pathogens)

Intelligent Interface

(Redundant Verification)

Redundancy ensures security and dramatically reduces false positive indication

Slide courtesy of Dr. Greg Boyer, SUNY-CESF

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Summary

  • With the amount on nutrient in-loading

into the Salt River reservoirs due to the Rodeo-Chedeski fire, eutrophication has

  • ccurred.
  • Numbers of toxic cyanobacteria are, as of

today, still relatively low.

  • If these species continue to increase in

number, potential toxicity to wildlife, and people, also increases.

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  • During the summer of 2002, the

first death in the U.S. directly attributable to anatoxin-a poisoning occurred in Wisconsin after teenage boys were swimming in a golf course pond.

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Questions?