surface water standards for nature and agriculture How?...photo: Waterboard Hollands Noorderkwartier...

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Some results from Dutch practice with constructed wetlands for effluent polishing Some results from Dutch practice with constructed wetlands for effluent polishing Peter de Jong and Rob van den Boomen Witteveen+Bos consulting engineers Peter de Jong and Rob van den Boomen Witteveen+Bos consulting engineers

Transcript of surface water standards for nature and agriculture How?...photo: Waterboard Hollands Noorderkwartier...

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Some results from Dutch practicewith constructed wetlands for

effluent polishing

Some results from Dutch practicewith constructed wetlands for

effluent polishing

Peter de Jong and Rob van den Boomen

Witteveen+Bos consulting engineers

Peter de Jong and Rob van den Boomen

Witteveen+Bos consulting engineers

Page 2: surface water standards for nature and agriculture How?...photo: Waterboard Hollands Noorderkwartier -6 Witteveen+Bos WWTP Everstekoog-WWTP mainly recreational pollution (Isle of Texel)-major

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Content:

I purpose of application

II examples and experiences

III lessons learned

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I. Purpose of applicationWhy?

To improve the quality of the effluent to meet the surface water standards for nature and agriculture

How?

- reduce the oxygen consuming components

- regenerate oxygen day-night rithm

- decrease N, P and bacterial loads

- turn “bacterial” Suspended Solids in i.e algae

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II. Examples and experiences3. Large scale constructed wetlands

two examples:

- WWTP Everstekoog (Texel)

- WWTP Land van Cuijk

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WWTP Everstekoog

photo: Waterboard Hollands Noorderkwartier

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WWTP Everstekoog

- WWTP mainly recreational pollution (Isle of Texel)

- major goal: turn effluent into water with a naturaloxygen concentration, limited oxygen demandand better hygienic condition

- constructed wetland built in 1994

- horizontal system: retention basin, reedzone and submerged water plants

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retention basinreed zone

submerged waterplants

discharge ditch

WWTP

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WWTP Everstekoogsome characteristics:

- wet area = 1,3 ha

- volume = 7.150 m3

- hydraulic load = 4.000 m3/day

- residence time = approx. 2 days (paralel ditchesfrom 7 hours to 10 days)

- 4 years research / monitoring (1995 - 1999)

Page 10: surface water standards for nature and agriculture How?...photo: Waterboard Hollands Noorderkwartier -6 Witteveen+Bos WWTP Everstekoog-WWTP mainly recreational pollution (Isle of Texel)-major

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WWTP Everstekoogsome results:

- effective regeneration of oxygen day-night rithm(natural surface water)

- reduction P (8 - 11%, residence time 2-10 days)

- reduction N (26 - 67%, residence time 2–10 days)

- good desinfection (residence time 2- 3 days)

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WWTP Land van Cuijk

photo: Waterboard Aa en Maas

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WWTP Land van Cuijk

- constructed wetland built in 2000

- major goal: turn effluent into natural water for use in agricultural and nature area and further reduction of P and N

- horizontal system: retention basin, reedzone andsubmerged water plants

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retention basins

reed zone

submerged

water plants

out

WWTP

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WWTP Land van Cuijksome characteristics:

- wet area = 3,9 ha

- volume = 35.000 m3

- hydraulic load = 8.500 m3/day

- residence time = approx. 4 days

- 3 years research, monitoring (2001 - 2003)

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WWTP Land van Cuijksome results:

- effective regeneration of oxygen day-night rithm(natural surface water)

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WWTP End of constructed wetland

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WWTP Land van Cuijksome results:

- reduction P (20-40%)

- reduction N (10-30%)

through filtering of the reed roots / accumulation

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II. Examples and experiences4. reed systems for small scale applications:

i.e. two agricultural farms:

- 3 mushroom farms

- poultry farm

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Three mushroom farms

graphic: Waterboard De Aa and Waterboard Limburg

some characteristics:

- reed area’s = 80, 135 and 260 m2

- hydraulic loads = 40-55 mm/day (max. 140)

- vertical flow

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Three mushroom farmssome results:

- reduction Suspended Solids = 89 - 99%

- reduction BZV = 88 - 97%, CZV = 43 - 83%

- reduction P = 0 - 57%, N = 0 - 69%

- effluent is non-toxic, influent was.

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Poultry farmssome characteristics:

- reed area = 75 m2 on 75 m3 vertical sand bed

- reed area = 70 m2 on 2 horizontal ditches

- hydraulic load = 45 mm/day

some results:

- reduction BZV = 75 - 99%, CZV = 21 - 95%

- reduction P = 41 - 99%, N = 9 - 91%

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III. Lessons learned1. Large scale horizontal systems:

- good reduction of bacteria and Suspended Solids (res.time = min. 2 days)

- moderate P reduction (10 - 40%, max 60 kg/ha/y at res.time = 5 days)

- moderate N reduction (10 - 60%, max 1.250 kg/ha/y at res.time = 10 days)

- best reduction in summer, less in winter

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III. Lessons learned1. Large scale horizontal systems:

- combination of retention basin (sedimentation), reedzone (filtration) and a zone with submergedwaterplants (oxygen regeneration) is optimal

- total residence time: min. 2 days, better 5 days

- good combination with nature and recreation is possible

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III. Lessons learned1. Large scale horizontal systems:

- need for a bypass? => constant hydraulic loadfor optimal treatment results

- remove duckweed at max. 80% coverage

- yearly mowing of reed to keep it in goodcondition (very limited reduction of nutrientswith removal)

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III. Lessons learned1. Large scale horizontal systems:

- need for a maintenance plan (mowing of the reed, removal of duckweed, boundaries of hydraulic load, removal of sludge)

- constructed wetlands = natural system => seasonal changes, not a constant output quality

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III. Lessons learned2. Small scale vertical systems:

- good reduction of bateria and Suspended Solids(due to vertical filtering)

- moderate fosfor reduction (40-60%)

- moderate nitrogen reduction (10-70%)

- reed plants mostly effective for nitrogenreduction

- hydraulic load: 30-50 mm/d

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Constructed wetlands for effluent polishing?

- moderate treatment efficiency, large landuse

- attractive combination with nature and recreation