identification, ecology and control of nuisance … · 2013-05-29 · algal ecology phytoplankton...
TRANSCRIPT
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IDENTIFICATION, ECOLOGY AND CONTROL OF NUISANCE
FRESHWATER ALGAE
KENNETH J. WAGNER, Ph.D, CLM WATER RESOURCE SERVICES
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PART 1: THE PROBLEMS
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ALGAL PROBLEMS
Algal problems include: • Ecological imbalances • Physical impacts on the
aquatic system • Water quality alteration • Aesthetic impairment • Taste and odor • Toxicity
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ALGAL PROBLEMS Ecological Imbalances
High algal densities: • Result from overly successful growth processes
and insufficient loss processes • Represent inefficient processing of energy by
higher trophic levels • May direct energy flow to benthic/detrital
pathways • May actually reduce system productivity
(productivity tends to be highest at intermediate biomass)
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ALGAL PROBLEMS Aesthetic Impairment
High algal densities lead to:
• High solids, low clarity • High organic content • Fluctuating DO and pH • “Slimy” feel to the water • Unaesthetic appearance • Taste and odor • Possible toxicity
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ALGAL PROBLEMS Taste and Odor
• At sufficient density, all algae can produce taste and odor by virtue of organic content and decay
• Some algae produce specific taste and odor compounds that are released into the water
• Geosmin and Methylisoborneol (MIB) are the two most common T&O compounds; these can induce T&O at very low concentrations
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ALGAL PROBLEMS Taste and Odor
T&O by blue-greens • Anabaena, Aphanizomenon, Microcystis, and
Oscillatoria are most common T&O producers, but many other genera produce T&O as well
• Geosmin and MIB often produced • Odors usually include musty, grassy, and
septic • May be produced by planktonic or benthic
growths
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ALGAL PROBLEMS Taste and Odor
T&O by greens • Chara, Cladophora, Chlorococcales
(Dictyosphaerium, Scenedesmus, Pediastrum, Hydrodictyon), Volvocales (Chlamydomonas, Volvox), and desmids (Staurastrum, Closterium, Cosmarium, Spirogyra) are primary greens causing T&O, but almost any genus can induce T&O at high density
• Main odors are fishy, skunky, musty, grassy and septic (wide range, species-specific)
• Not usually as severe as with blue-greens
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ALGAL PROBLEMS Taste and Odor
T&O by diatoms • Melosira/Aulacoseira, Stephanodiscus,
Cyclotella, Asterionella, Fragilaria/Synedra, and Tabellaria are primary diatoms causing T&O, usually only at high density
• Main odors are geranium, spicy and fishy, with occasional musty or grassy scent
• Not as severe as with blue-greens unless diatom density is very high
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ALGAL PROBLEMS Taste and Odor
T&O by goldens • Synura, Dinobryon, Mallomonas, Uroglenopsis,
and Chrysosphaerella are major T&O producers, others impart odor at high density Main odors are cucumber, violet, spicy and fishy
• Can produce substantial T&O even at low density
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ALGAL PROBLEMS Taste and Odor
T&O by other algae • Dinoflagellates can produce a
fishy or septic odor at elevated densities
• Euglenoids can produce a fishy odor at elevated densities
• Major die-off of high density algae may produce a septic smell
• Actinomycetes, a non-photosynthetic bacterium, can also produce geosmin and MIB
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ALGAL PROBLEMS Taste and Odor
Control of T&O • Minimizing algal density and specific T&O
producers is desirable for T&O control • Activated carbon removes most T&O, but
effective use is slow and increases treatment cost
• Aeration/mixing may oxidize/volatilize T&O compounds, but not completely effective
• Possible toxic link, but no severe direct health effects known from T&O; aesthetic issues can be major
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ALGAL PROBLEMS Toxicity-Cyanotoxins
• Cyanobacteria are the primary toxin threats to people from freshwater; acute toxicity is rare, but chronic effects may be significant and are difficult to detect.
• Research (e.g., 3 papers in Lake and Reservoir Management in September 2009) indicates widespread occurrence of toxins but highly variable concentrations, even within lakes.
• Water treatment in typical supply facilities is adequate to minimize risk; the greatest risk is from substandard treatment systems and direct recreational contact.
• Some other algae produce toxins - Prymnesium, or golden blossom, can kill fish; marine dinoflagellates, or red tides, can be toxic to many animals and humans.
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ALGAL PROBLEMS Toxicity-Cyanotoxins
• Dermatotoxins – produce rashes and other
skin reactions, usually within a day (hours)
• Hepatotoxins – disrupt proteins that keep
the liver functioning, may act slowly (days to weeks)
• Neurotoxins – cause rapid paralysis of
skeletal and respiratory muscles (minutes)
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ALGAL PROBLEMS Toxicity-Which Blue-Green Has Which
Toxin? Blue-Green Algae Microcystin Nodularin Cylindro-
spermopsin Anatoxin Saxitoxin Dermato-
toxin Anabaena X X X X Anabaenopsis X Aphanizomenon X X X Cylindrospermopsis X Cylindrospermum X X Hapalosiphon X Lyngbya X X Microcystis X X Nodularia X X Nostoc X Oscillatoria X X X Schizothrix X Umezakia X
More forms found each year – methods or actual increase?
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ALGAL PROBLEMS Toxicity-Analytical Methods
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100
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ity
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25 Bioassay
(mouse)
µg ng pg Sensitivity
Mass Spec LC/MS
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ELISA Phosphatase Assay
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ALGAL PROBLEMS Toxicity- Key Issues
• Acute and chronic toxicity levels - how much can be tolerated?
• Synergistic effects - those with liver or nerve disorders at higher risk
• Exposure routes - ingestion vs. skin • Treatment options - avoid cell lysis,
remove or neutralize toxins
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ALGAL PROBLEMS Recommended Toxicity Precautions
• Monitor algal quantity and quality • If potential toxin producers are detected,
increase monitoring and test for toxins • For water supplies, incorporate capability to
treat for toxins (PAC or strong oxidation seem to be best)
• For recreational lakes, be prepared to warn users and/or limit contact recreation
• Avoid treatments that rupture cells
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PART 2: ALGAL FORMS
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Algal Forms Algal “Blooms”
♦ Water discoloration usually defines bloom conditions
♦ Many possible algal groups can “bloom”
♦ Taste and odor sources, possible toxicity
♦ Potentially severe use impairment
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Algal Forms Algal Mats
♦ Can be bottom or surface mats - surface mats often start on the bottom
♦ Usually green or blue-green algae
♦ Possible taste and odor sources
♦ Potentially severe use impairment
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Algal Types: Planktonic Blue-greens
Aphanizomenon
Microcystis
Anabaena
Coelosphaerium
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Algal Types: Planktonic Blue-greens Planktolyngbya Planktothrix
(Oscillatoria)
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Algal Types: Planktonic Blue-greens Gloeotrichia
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Algal Types: Planktonic Blue-greens Cylindrospermopsis
•A sub-tropical alga with toxic properties is moving north.
•Most often encountered in turbid reservoirs in late summer, along with a variety of other bluegreens.
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Algal Types: Mat Forming Blue-greens
Oscillatoria
Lyngbya/Plectonema
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Algal Types: Planktonic Greens Pediastrum
Scenedesmus
Lagerheimia Dictyosphaerium
Schroederia
Oocystis
(Order Chlorococcales)
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Algal Types: Planktonic Greens
Chlamydomonas
Pyramichlamys
Carteria
Eudorina
Volvox
(Order Volvocales)
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Algal Types: Mat Forming Greens
Cladophorales, with Cladophora (above), Rhizoclonium and Pithophora
Zygnematales, with Spirogyra (above), Mougeotia and Zygnema
Hydrodictyon, an unusual type of Chlorococcales
Oedogoniales, with Oedogonium and Bulbochaete
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Algal Types: Mat Forming Greens Zygnematales - Unbranched filaments, highly
gelatinous
Mougeotia Spirogyra
Zygnema
Mats trap gases and may float to surface
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Cladophorales - Large, multinucleate cells, reticulate chromatophores, filamentous forms
Pithophora
Rhizoclonium Cladophora
Algal Types: Mat Forming Greens
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Algal Types: Mat Forming Greens
Hydrodictyon
Oedogonium
Bulbochaete
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Algal Types: Planktonic Diatoms Aulacoseira
Asterionella
Cyclotella
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Algal Types: Planktonic Diatoms
Fragilaria Nitzschia Tabellaria
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Algal Types: Plankton Goldens
Dinobryon
Synura
Chrysosphaerella
Prymnesium
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Algal Types: Mat Forming Goldens Tribonema
Vaucheria
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Algal Types: Other Plankton
Ceratium
Peridinium
Euglena
Trachelomonas
Phacus
(Euglenoids)
(Dinoflagellates)
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PART 3: THE ECOLOGICAL BASIS FOR ALGAL CONTROL
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ALGAL ECOLOGY Key Processes Affecting Abundance
Growth Processes • Primary production – controlled by light
and nutrients, algal physiology • Heterotrophy – augments primary
production, dependent upon physiology and environmental conditions
• Release from sediment – recruitment from resting stages, related to turbulence, life strategies
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ALGAL ECOLOGY Key Processes Affecting Abundance
Loss Processes • Physiological mortality – inevitable but
highly variable timing – many influences • Grazing – complex algae-grazer interactions • Sedimentation/burial – function of
turbulence, sediment load, algal strategies • Hydraulic washout/scouring – function of
flow, velocity, circulation, and algal strategy
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ALGAL ECOLOGY Key Processes Affecting Abundance
Annual variability in growth/loss factors in dimictic temperate lakes
• Winter – – Possible ice cover, reverse stratification – Under ice circulation is an important factor – Low light and temperature affect production – Variable but generally moderate nutrient availability – Possibly high organic content – Grazer density usually low
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ALGAL ECOLOGY Key Processes Affecting Abundance
Annual variability in growth/loss factors in dimictic temperate lakes
• Spring/fall – – Isothermal and well-mixed – Relatively high nutrient availability – Light increases in spring, decreases in fall – Temperature low to moderate – Stratification setting (spring) or breaking down (fall) – Grazer density in transition (low to high in spring,
high to low in fall)
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ALGAL ECOLOGY Key Processes Affecting Abundance
Annual variability in growth/loss factors in dimictic temperate lakes
• Summer – – Potential stratification, even in shallow lakes – Often have low nutrient availability – Light limiting only with high algae or sediment levels – Temperature vertically variable – highest near surface – Vertical gradients of abiotic conditions and algae – Grazer densities variable, often high unless fish
predation is a major factor
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ALGAL ECOLOGY Phytoplankton Succession - Winter
• Often cryptophytes, chrysophytes, diatoms, naked dinoflagellates
• Some non-nitrogen fixing blue-greens, but also possibly Aphanizomenon
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ALGAL ECOLOGY Phytoplankton Succession –Spring
• Most lakes experience rapid increase in algal density with light and temperature increases
• Diatoms, cryptophytes, and chrysophytes tend to dominate in colder water
• Greens or blue-greens may show up in warmer water
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ALGAL ECOLOGY Phytoplankton Succession – Late Spring
• Increasing light cues spring blooms where nutrients are available
• Grazing and algal settling increases during spring with rising water temperature
• Clear water phase often results from loss processes overshadowing growth in late spring
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ALGAL ECOLOGY Phytoplankton Succession – Early Summer • Increasing light and temperature • Nutrient availability may decrease as internal sources
are isolated by stratification - N, P, Si • Grazing, sinking and metabolism all increasing • Composition will depend upon resource gradients -
low N:P favors blue-greens, high N:P favors chlorophytes, chrysophytes and dinoflagellates
• N:P ratio at sediment:water interface can be more important than ratio in epilimnion
• High variability among lakes and within lakes among years
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ALGAL ECOLOGY Phytoplankton Succession – Early Summer • Greens may
increase, especially Volvocales and Chlorococcales, at high N:P ratio
• Blue-greens appear at increased density, usually at low N:P ratio, but can dominate any high temperature water
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ALGAL ECOLOGY Phytoplankton Succession – Summer
• May get metalimnetic blooms of cryptophytes, chrysophytes, dinoflagellates or blue-greens, especially Planktothrix
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ALGAL ECOLOGY Phytoplankton Succession – Late Summer
• High bloom potential - most often blue-greens, but also thecate dinoflagellates, large desmids
• Temperature is a major factor in blooms
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ALGAL ECOLOGY Phytoplankton Succession – Late Summer
• Nitrogen-fixing blue-greens especially common bloomers
• May get blooms of non-N fixing blue-greens if N is high
• May get population oscillations between N-fixers and non-N-fixers
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ALGAL ECOLOGY Phytoplankton Succession – Late Summer
• May also get green or blue-green mats floating to the surface
• Most often Cladophorales or Oscillatoriales
• Mats tend to start on bottom, floating to surface after trapping gases
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ALGAL ECOLOGY Phytoplankton Succession - Autumn
• “Leftover” blue-greens may remain abundant well into autumn, exception is Cylindrospermopsis which often blooms late summer into mid-fall
• Metalimnetic growths often reach surface upon mixing
• Diatoms often assume dominance after turnover
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ALGAL ECOLOGY Phytoplankton Succession - Notes
• Biomass can vary by 1000X from winter minimum to late summer maximum in temperate to polar waters
• Primary productivity and biomass may not correlate due to time lags, cell size and nutrient or light limitations
• Highest productivity normally at intermediate biomass (Chl a = 10 ug/L)
• High pH during blooms may trigger resting cyst formation
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ALGAL ECOLOGY Trophic Gradients
• Based on decades of study, more P leads to more algae
• More algae leads to lower water clarity, but in a non-linear pattern
0102030405060708090
100110120130140150160170180190200
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200
Chl
(ug/
l)
TP (ug/l)
Total Phosphorus vs. Chlorophyll a
0123456789
10
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200
SDT
(m)
TP (ug/l)
Total Phosphorus vs. Secchi Disk Transparency
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ALGAL ECOLOGY Trophic Gradients
• As algal biomass rises, a greater % of that biomass is cyanobacteria. So more P = more algae + more cyanobacteria.
From Canfield et al. 1989 as reported in
Kalff 2002
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ALGAL ECOLOGY Trophic Gradients
• High P also leads to more cyanobacteria, from considerable empirical research. Key transition range is between 10 and 100 ug/L
(10 ug/L) (100 ug/L) From Watson et al. 1997 L&O 42(3): 487-495
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Three step process: – Don’t lose your head – Get ducks in a row – Don’t bite off more than you can chew
PART 4: METHODS OF ALGAL CONTROL
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Algal Control: Watershed Management
Understand the watershed and
manage it!
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Algal Control: Watershed Management ♦ Source controls • Banning certain high-impact actions • Best Management Practices for minimizing risk of
release ♦ Pollutant trapping • Detention • Infiltration • Uptake/treatment • Maintenance of facilities
Watershed management should be included in any successful long-term algal management plan
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Algal Control: In-Lake Management Data needs include: ♦ Algal types and quantity (planktonic and benthic) ♦ Water quality (nutrients, pH, temp., oxygen,
conductivity, and clarity over space and time) ♦ Inflow and outflow sources and amounts, with
water quality assessment ♦ Lake bathymetry (area, depth, volume) ♦ Sediment features ♦ Zooplankton and fish communities ♦ Vascular plant assemblage All of which facilitate a hydrologic and nutrient
loading analysis and biological assessment essential to evaluating algal control options
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Algal Control: In-Lake Management
In-lake detention and wetland
systems to limit nutrient inputs
Fulfilling a
watershed function in the
lake
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Algal Control: In-Lake Management Dredging
♦ Dry (conventional) ♦ Wet (bucket/dragline) ♦ Hydraulic (piped)
♦ Removes nutrient reserves
♦ Removes “seed” bank ♦ Potential mat control
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Algal Control: In-Lake Management
Harvesting ♦ Not feasible
for many algal nuisances
♦ Possible to collect surface algal mats
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Algal Control: In-Lake Management
Dilution and Flushing
♦ Add enough clean water to lower nutrient levels
♦ Add enough water of any quality to flush the lake fast enough to prevent blooms
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Algal Control: In-Lake Management Selective withdrawal
♦ Often coupled with drawdown
♦ May require treatment of discharge
♦ Best if discharge prevents hypolimnetic anoxia
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Algal Control: In-Lake Management Dye addition
♦ Light limitation - not an algaecide
♦ May cause stratification in shallow lakes
♦ Will not prevent all growths, but colors water in an appealing manner
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Algal Control: In-Lake Management Sonication
♦ Disruption of cells with sound waves – may break cell wall or just dissociate plasma from wall
♦ Used in the lab to break up algal clumps
♦ Won’t eliminate nutrients, but may keep algae from growing where running all the time
♦ Varied algal susceptibility
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Algal Control: In-Lake Management Algaecides
♦ Relatively few active ingredients available
♦ Copper-based compounds are by far the most widely applied algaecides
♦ Peroxides gaining acceptance
♦ Some use of endothall
♦ Effectiveness and longevity are issues
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Algal Control: In-Lake Management About copper
♦ Lyses cells, releases contents into water ♦ Formulation affects time in solution and
effectiveness for certain types of algae ♦ Possible toxicity to other aquatic organisms ♦ Long term build up in sediment a concern, but no
proven major negative impacts ♦ Resistance noted in multiple nuisance blue-greens
and greens ♦ Usually applied to surface, but can be injected
deeper by hose ♦ Less effective at colder temperatures
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Algal Control: In-Lake Management About peroxide
♦ Lyses cells, but more effective on thin walled forms; less impact on most diatoms and greens
♦ Degrades to non-toxic components; adds oxygen to the water, may oxidize some of the compounds released during lysis
♦ Typically applied to surface, but may reach greater depth with adequate activity (slower release/reaction rate)
♦ No accumulation of unwanted contaminants in water or sediment
♦ Considerably more expensive than copper
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Algal Control: In-Lake Management Proper Use of Algaecides
♦ Prevents a bloom, not removes one ♦ Must know when algal growth is accelerating ♦ Must know enough about water chemistry to
determine most appropriate form of algaecide ♦ May involve surface or shallow treatment where
nutrients are fueling expansion of small population ♦ May require deep treatment where major migration
from sediment is occurring ♦ May require repeated application, but at an
appropriate frequency - if that frequency becomes too high, recognize that the technique requires adjustment or will not be adequate for the long-term
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Algal Control: In-Lake Management
Phosphorus inactivation - anti-fertilizer
treatments
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Algal Control: In-Lake Management ♦ Iron is the most
common natural binder, but does not hold P under anoxia
♦ Aluminum is the most common applied binder, multiple forms, permanent results, toxicity issues
♦ Calcium used in some high pH systems
♦ Used for water column or sediment P
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Algal Control: In-Lake Management Factors in Planning Lake Treatments:
• Existing P load, internal vs. external • Sources and inactivation needs – field and lab tests • System bathymetry and hydrology • Potential water chemistry alteration - pH, metals
levels, oxygen concentration • Potentially sensitive receptors - fish, zooplankton,
macroinvertebrates, reptiles, amphibians, waterfowl
• Accumulated residues - quantity and quality
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Algal Control: In-Lake Management
Lake Water Column Treatment:
• Doses vary - need 5- 20 times TP conc.
• Can achieve >90% P removal, 60-80% more common
• Effects diminish over 3-5 flushings of the lake
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Algal Control: In-Lake Management Lake Sediment
Treatment: • Can reduce longer-
term P release • Normally reacts with
upper 2-4 inches of sediment
• Dose usually 25-100 g/m2 - should depend upon form in which P is bound in sediment
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Secchi Disk Transparency in Hamblin Pond, 1992-2003
0.02.04.06.08.0
10.0
2/27/1992
4/28/1992
6/10/1992
7/14/1992
8/13/1992
9/18/1992
10/23/1992
7/6/1993
7/31/1993
8/14/1993
8/30/1993
9/12/1993
6/26/1994
7/11/1994
7/31/1994
8/11/1994
9/15/1994
5/23/1995
6/4/1995
6/23/1995
7/21/1995
9/22/1995
6/28/1996
7/22/1996
8/10/1996
10/1/1996
6/26/1997
8/8/1997
8/31/1997
9/30/1997
8/28/1998
5/26/1999
7/6/1999
8/25/1999
9/18/1999
6/12/2000
8/4/2000
9/4/2000
6/18/2001
9/10/2002
9/10/2003
Date
SDT (
M)
Treatment Date
SDT = 1.22 m
Hamblin Pond Example Cape Cod, MA
P levels dramatically
reduced, water clarity substantially increased
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Algal Control: In-Lake Management Selective nutrient
addition ♦ Addition of nutrients
(most likely N or Si) to shift ratio (N:P:Si) to favor more desirable algae
♦ Sometimes practiced in association with fertilization for fish production, but rare in water supplies or recreational lakes
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Algal Control: In-Lake Management
Aeration/Mixing
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Algal Control: In-Lake Management Oxygenation/circulation can work by:
♦ Adding oxygen and facilitating P binding while minimizing release from sediments
♦ Alteration of pH and related water chemistry that favors less obnoxious algal forms
♦ Creation of suitable zooplankton refuges and enhancement of grazing potential
♦ Turbulence that neutralizes advantages conveyed by buoyancy mechanisms
♦ Physical mixing that disrupts growth cycles of some algae
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Algal Control: In-Lake Management Key factors in oxygenation:
♦ Adding enough oxygen to counter the demand in the lake (usually about 75% from sediment) and distributing it where needed in the lake
♦ Maintaining oxygen levels suitable for target aquatic fauna (fish and invertebrates)
♦ Having enough of a P binder present to inactivate P in presence of oxygen
♦ Not breaking stratification if part of goal is to maintain natural summer layering of the lake
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Algal Control: In-Lake Management Destratifying oxygenation
(really circulation by aeration): Lake is mixed, top to bottom, input of oxygen comes
from bubbles and interaction with lake surface
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Algal Control: In-Lake Management Non-destratifying oxygenation:
Bottom layer is oxygenated, but top layer is unaffected; oxygen input can be air or pure oxygen
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Algal Control: In-Lake Management Key factors in circulation:
♦ Moving enough water to prevent stagnation; may mix whole lake or just the top layer (if any)
♦ Fostering greater homogeneity in mixed zone and greater interaction with the atmosphere (oxygen and pH effects may be large)
♦ Getting enough motion or change in water quality to disrupt target algal species; moving algae to dark zone can reduce biomass, but may be possible to alter types of algae with only surface layer mixing
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Algal Control: In-Lake Management Circulation systems:
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Algal Control: In-Lake Management Barley straw as an algal
inhibitor ♦ Decay of barley straw
appears to produce allelopathic substances
♦ Bacterial activity may also compete with algae for nutrients
♦ Limited success with an “unlicensed herbicide” in USA
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Algal Control: In-Lake Management Viral controls were
attempted without much success in the
1970s, but recent research suggests renewed potential.
Virus SG-3 in tests at
Purdue Univ.
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Algal Control: In-Lake Management Bacterial additives
♦ Many formulations, details proprietary
♦ Seem to focus on limiting N; competitive with algae
♦ Claims of sediment reduction
♦ Often paired with aeration/mixing
♦ Variable results, inadequate scientific documentation
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Algal Control: In-Lake Management Biomanipulation -
altering fish and zooplankton
communities to reduce algal
biomass
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Algal Control: In-Lake Management Alewife and other planktivore control - cascading effects
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Algal Control: In-Lake Management “Rough” fish
removal - limiting nutrient
regeneration
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Algal Control: In-Lake Management
Rooted plant assemblages as algal inhibitors
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Algal Control: In-Lake Management Techniques that didn’t quite make the list
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Algal Control: In-Lake Management Roll call for algal control
♦ Watershed management (where external load is high) ♦ Phosphorus inactivation (for internal load or inflow) ♦ Algaecides (with proper timing, limited usage) ♦ Circulation to 3X Secchi depth (deep systems) ♦ Circulation, possibly with dyes or bacteria (shallow systems) ♦ Oxygenation (deeper lakes, internal load dominant) ♦ Dredging (where feasible, especially for mats) ♦ Sonication (for susceptible algae, nutrient control limited) ♦ Biomanipulation (P<80 ug/L, high variability acceptable) ♦ Other techniques as scale and circumstances dictate (do not
throw away any tool!)
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The End
QUESTIONS?
After that, we might need another one of these…