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1. Multiple Barriers the role of Phosphorus & Eutrophication Control in Water Bodies Dr David Garman
Chairman Phoslock Limited
Executive Director Environmental Biotechnology CRC Pty Ltd
President International Water Association
15/3/2008
2. 15/3/2008
3. IWA - The Premier Global Network for Water Professionals 7,000+ members in over 120 countries
Professions: Science & research, utilities, consultants, regulators, manufacturers
Scope > All aspects of water management -> water and wastewater
Leading Edge of science and practice 15/3/2008
4. Water Availability Per Capita 1950 15/3/2008
5. Water Availability Per Capita 2010 15/3/2008
6. Water Availability Per Capita 2025 15/3/2008
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8. A Rearranged Population 15/3/2008
9. Development of World Cities 15/3/2008
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11. Urban Portion of Worlds Population 15/3/2008
12. Recognition of the Impacts of Climate Change 15/3/2008
13. Great Natural Disasters 19502005 15/3/2008
14. Convergence of Forces:Population, Urbanization, Climate Change and Regulatory Requirements 15/3/2008
15. Emergent Themes Do more with less new conventional sources are not likely
Need to manage both sets of extremes
Even those that are wet (underwater) are facing seasonal water shortages
Expect the unexpected
Seek security through diversity 15/3/2008
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17. New sources - implications for water Re-analysis of the fundamentals of supply:
micronutrients in new water supply sources can lead to increased biofilm growth & treatment costs,
pathogen risk increases esp. non-culturable organisms,
energy & pumping costs particularly with membranes
disinfectant management & control
trace contaminants esp EDCs
15/3/2008
18. 15/3/2008 Quality issues for water Toxic chemical control ??
Organics
Heavy metals
Eutrophication ?
Nitrogen NH3- NOX
Phosphorus
Biodiversity optimum trophic status
Sustainability - variability
19. 15/3/2008 Water source quality control Multiple barriers from source to tap
Critical factors for waterbodies
Source protection
Water quality control
Ecological protection
Diversity maintenance/protection
20. 15/3/2008 Other pressures Speed for compliance
Compliance
Risk management
Operating costs (Opex)
Investment (Capex)
Non-compliance penalties
21. 15/3/2008 Catchment controls Implementation
Environmentally sound with public support
Typically 4+ years to implement
Expensive but early control is effective
Full impact only after 10 to 40 years
Variability in environmental conditions requires expensive monitoring programs
Uncertainty in outcomes dictates increased monitoring to provide greater degrees of resolution
22. 15/3/2008 Phosphorus as limiting nutrient Hypothesis: Any micronutrient may become the limiting nutrient
Limitations associated of other micronutrient controls:
N leads to N fixing organisms
Metals disrupts local ecology
23. 15/3/2008 Implications of making P the limiting nutrient Changes algal populations
Reduces total productivity
Alters trophic status
Reduces microbial regrowth & survival
Reduces biofilm growth
in distribution systems
as epiphytes/seagrass populations
in natural systems reduces bacterial regrowth, viruses etc
24. 15/3/2008 Biofilms as hazards Bacteria grow in biofilms as flocs or slimes
Cyanobacteria are a large visible indicator of this
The slimes contain mixtures of bacteria including pathogens as well as viruses
The growth and re-growth of bacteria are potential hazards in eutrophic (nutrient rich) water
Epiphytes reduce diversity & distort the ecology
The growth of these is minimised in low phosphorus waters.
25. 15/3/2008 Barriers for nutrient control Biological treatment eg WTPs EBNPR
Only really suitable for point sources
Chemical dosing
Not suitable for very low levels & natural waterways
Remobilised under some conditions
Al & Fe - pH & sludge & sediment problems
Denitrification N removal is expensive
High energy(chemical costs) & equipment
Nitrogen is refixed opportunistically
26. 15/3/2008 Diffuse source control Dredging
Expensive, disruptive may not remove sediment source poses new disposal problems?
Wetlands
Short term unless nutrients harvested remobilised nutrients
Buffer zones
Similar to wetlands
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28. 15/3/2008 Why invent Phoslock? Limitations of alternative chemicals
Al & Fe based have significant risks & lower effectiveness
Removal of critical nutrient essential
Algicides - existing chemical or biological are unsustainable have risky ecological impacts
Internal recycling is critical source of nutrients
Dredging of sediments is ecologically disruptive & expensive
Secondary disposal now closely regulated
External removal unsustainable
Pumping & treatment costs prohibitive
29. 15/3/2008 Phoslock properties Forms a very low solubility complex with Phosphorus Ks <10 -23
Typical low equilibrium values ~ 0.005 mg P/L
Surplus of Phoslock other values can be selected
Not released by bacteria or wide range of water conditions
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33. Phoslock eutrophication reset Rapid reduction in FRP typically hours or days
TP takes longer- but is equally effective
Enables assessment of control measures
Provides management with time for option assessment
Selection of trophic status depending on end use objectives 15/3/2008
34. 15/3/2008 Application of Phoslock Open Water Bodies
- as slurry with applicator mixing
- aerial application of pellets
Settles as stable deposit on sediments
Industrial
- for filter uses in high concentration P
100 g Phoslock removes 1 to 1.5g P
35. 15/3/2008 How does Phoslock work? P is adsorbed onto the clay as it falls through the water
The P binds to the modified (La) clay, forming an almost insoluble complex
The clay settles to the sediments as a very thin layer 1 to 3 mm
Release of P from the sediments is adsorbed by any free Phoslock capacity
36. 15/3/2008 Phoslock performance Operates over a wide pH range ~ 4 to 11 without changing pH
Rapid phosphorus uptake (FRP) - > 90% less than 4 hours
Binds phosphorus under anoxic conditions
Phoslock is stable under natural conditions
Low toxicity
Low sludge volume less than 3mm of sediment
Continues to perform if absorbent sites free
High settlability compared with other products
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38. 15/3/2008 Phoslock is environmentally safe
Phoslock has been the subject of extensive ecotoxicity and other testing
Recent tests in NZ on algae, juvenile fish (rainbow trout) and water fleas (crustacea).
Repeated in Australia & Germany with negative impact results.
Risk assessment lodged with Australian authorities prepared by lead independent RA Centre.
39. Human health safety La used for serum phosphorus reduction in patients with chronic kidney disease
Doses equivalent >10,000L water day at max Phoslock dosing
Clay & La removed in water treatment
Phoslock settles & remains in storages 15/3/2008
40. 15/3/2008 Do Nothing Risk Algal blooms
Toxins, ecology disruption with BGA
Epiphyte impact on macrophytes
DO stress with pH changes
Ecology disruption
Shift from oligotrophic to eutrophic & exotic species
Microbial risk
Biofilm increases pathogen risk increases
Corrosion & biodeposition risk
Taste, odour
Coatings
Corrosion
41. Applications data Phoslock applications - examples of outcomes 15/3/2008
42. Applications Over 120 major applications worldwide
Many minor applications
Range of applications from 330 ha lake to 1ha
Depth from 3m to 60m
P concentrations from 50 ugP/L to >850ug/L
Period of monitoring about 3 years 15/3/2008
43. Examples to be presented Highly eutrophic urban river Torrens River SA
L Emu - Urban Lake Western Australia
Off line water reservoir Marulan NSW
Low trophic status DWR
Productive deep recreational lake - L Okaraka NZ
Europe recreational & high value waters 15/3/2008
44. 15/3/2008
45. Torrens River Consistent BG algal blooms
Odour, unsightly
Largely uncontrolled catchment
Highly enriched sediments
Algicides, aeration failed
Impacts
Restricted recreation
Tourism adversely impacted
Result re-application(1 year) following rapid restoration of WQ
15/3/2008
46. Marulan water storage pumped off river storage 15/3/2008
47. Marulan Application(4000m2)
blue green algae in water supply
assessed as health risk
rapid correction required
Result effective short & longer term BG control 15/3/2008
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49. Lake Emu High levels of BG algae in urban water feature
Trials successful full scale application proceeding 15/3/2008
50. Lake Okareka NZ 15/3/2008
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52. Lake Okareka The treated area approx 170 hectares of the 330 hectare total area,
Deeper basin approximately within the 20 m contour.
Phoslock in the form of small pellets applied at a rate of 118 kg/ha (sediment control)
20 tonnes applied with each annual treatment.
Monitoring over 2+y fish report clearance
15/3/2008
53. Applications Range of conditions have been successfully treated over a wide range of water body sizes
The residual capacity of Phoslock to deal with new inflows is well established
No adverse health or environmental issues have been observed. 15/3/2008
54. Application potential in Canada Ecological reset open water bodies
Catchment control re-assessment
Sediment capping
Inflow treatment wetlands & stormwater traps
Drinking water reservoirs
15/3/2008
55. 15/3/2008 Conclusions Phoslock offers first rapid, cost effective way of dealing with eutrophication of large natural water bodies
It enables other control measures to be more effective and their impact to be assessed more rapidly
It is a stable very low impact material which assists with re-establishment of contaminated sensitive environments.
Optimum application for respective control measures for large lake systems requires appropriate data collection
It is a control, reset and management tool it is not fix it product.
Phoslock applications have implications for water body management to achieve maximum impact and point to cost effective solutions.