THE USE OF ALUMINUM SULFATE (ALUM) IN...
Transcript of THE USE OF ALUMINUM SULFATE (ALUM) IN...
THE USE OF ALUMINUM SULFATE (ALUM) IN LAKES AND PONDS
Joe Bischoff and Brian Beck, Wenck Associates Inc.William F. James, University of Wisconsin-Stout
Presentation Objectives• Sediment P release in lakes (internal loading)• Background on Alum in Lakes
• How does it work?• How is it applied?
• Considerations Prior to Selecting Alum• Watershed loading and long term effectiveness• Cost• Use of alum in shallow lakes• Safety for humans and aquatic organisms
Oligotrophic Mesotrophic Eutrophic Hyper-Eutrophic
Total Phosphorus (µg/L)
Relationship between Total Phosphorusand Transparency
Lake Watershed Phosphorus Loading
Internal Phosphorus ReductionWhy Alum?
• Sediment P Inactivation Tools• Aluminum Sulfate (Alum)• Ferric Iron• Phoslock (lanthanum clay)
• Water Column Manipulation• Hypolimnetic withdrawal and treatment• Hypolimnetic aeration
What is Alum? • Aluminum Sulfate (liquid)
• Dissolves in water to form aluminum hydroxide and sulfate
• Aluminum hydroxide is a white solid that settles out of the water column
• Permanently binds phosphorus in the sediments
• Aluminum phosphate complexation (Al(OH)3PO4)• Very stable in the environment• Not sensitive to anoxia (low oxygen)
Advanced Alum Application Technologies
• Advances in application technology have increased project effectiveness and safety
• Computerized GPS guidance and tracking systems ensure complete and accurate coverage and allows for multiple alum dose zones
Pinto Lake, CA Coverage Map
Factors Influencing Longevity
Watershed to Lake Area Ratio (32%)
Alum Dose (47%)
Osgood index (3%)(Average depth ÷ Area0.5)
Percentages refer to amount of variation explained by that variable in multiple regression (From Huser et al. 2015)
Recent Advances in Alum Dosage(Rydin and Welch 1999; W. F. James 2011; James and Bischoff 2015)
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Redox-sensitive P (mg g-1)
Potentially-mobile P layer
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Redox-sensitive P (mg g-1)
Potentially-mobile P layer
• Based on binding and inactivating measured P fractions that are active in internal P loading
• The Al:P binding ratio is measured for accuracy• Thickness of the sediment layer active in internal P loading is measured for
dosage calculation
Maximizing Alum Application Effectiveness
1• Collect Sediment Cores• Determine if alum treatment is necessary
2• Apply half alum dose (1st)• Collect sediment cores (6 months)
3• Apply half alum dose (2nd)• Collect Sediment Cores (1-3 year)
4• Monitor water quality to track effectiveness• Collect sediment cores (10 years)
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Potentially-mobile P layer
Adapting to Sediment Results
Factors Influencing Longevity
Watershed to Lake Area Ratio (32%)
Alum Dose (47%)
Osgood index (3%)(Average depth ÷ Area0.5)
Percentages refer to amount of variation explained by that variable in multiple regression (From Huser et al. 2015)
Lake P Sedimentation• How long does it take to
replace inactivated sediment TP?• Used Canfield Bachmann P
sedimentation term to estimate P loading to sediment
• Assumes 90% inactivation in top 5 cm
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VWCC
PP bP
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Canfield and Bachmann (1981)
VTPV
WCCPb
PCBPsed ××
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Canfield and Bachmann (1981) P Sedimentation Term
Internal or Watershed First?
Watershed Projects Internal load Lake Clarity
improvement
Traditional Thought Model
Watershed Projects
Internal loadLake Clarity improvement
Internal load Internal load
Proposed Thought Model
Factors Influencing Longevity
Watershed to Lake Area Ratio (32%)
Alum Dose (47%)
Osgood index (3%)(Average depth ÷ Area0.5)
Percentages refer to amount of variation explained by that variable in multiple regression (From Huser et al. 2015)
Alum Use in Shallow Lakes• Physical and biological factors
increase internal load potential and may limit the effectiveness of alum• Wind re-suspension of sediments• Bioturbation from rough fish,
especially carp• Sediment P pumping from deep
sediments by submerged vegetation
Strategy for Restoring Shallow Eutrophic Lakes
• Forward switch detection and removal
• External and internal nutrient control (TMDL)
• Biomanipulation (reverse switch)
• Plant establishment• Stabilizing and managing restored system
Costs for Alum Treatments• Cost is typically $1.75 to
$2.00/gallon applied• Alum prices vary significantly year
to year
• Sticker shock for upfront costs• Bald Eagle Lake $860,000• Halsted Bay $1.1M• Spring Lake $986,000• Lake Riley $480,000
Costs for Alum Treatments
Blackhawk and Thomas Lake Management Plan Wenck 2013Neighborhood Lakes Management Plan Wenck 2014 Bald Eagle Lake TMDL Implementation Plan, Wenck 2010
Aluminum and Human Health• Al is the third most abundant element in
the earths crust• food, water, air, and soil contain aluminum• Occurs naturally in lake sediments
• The average adult eats 7–9 milligrams (mg) aluminum per day in their food
• Only very small amounts of aluminum will enter the bloodstream
• The FDA concluded that aluminum as a food additive is generally safe
One dose of Maalox includes 400 mg Aluminum Hydroxide
Aluminum ToxicityFish and Macroinvertebrate Impacts
• Toxic dissolved aluminum (Al3+) forms if pH drops below 6• pH can be controlled with proper dosing or
buffering
• Aluminum does not bioaccumulate in algae or fish tissue • Huser and Kohler, 2012
• Macroinvertebrates show short term impacts followed by community recovery and improvement• Smeltzer at al. 1999; Harper et al.; Huser
and Kohler 2012
Conclusions
• Sediment P inactivation is more cost effective that watershed BMPs on a cost per pound removal
• Alum can be effective for 15 to 30+ years if dosed correctly• Controlling external P loads is important, but alum
treatments can be effective even when watershed loads are moderately high
• Alum is effective in shallow lakes and can support restoration efforts
• Alum use is safe for both humans and lake organisms