Title: Removal Mechanisms in Constructed Wetlands CE 421 Presented by
1Removal Mechanisms in Constructed WetlandsCE
421 Presented by
Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Stephen Norton December 04, 2007
Case Study
Pathogens
Metals
2Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
3Overview
- Types of Wetlands
- Free Water Surface Wetland (FWS)
- Shallow Water Flowing Over Plant Matter
- Floating Plants Known as Macrophytes
- Vegetated Submerged Bed Wetland (VSB)
- Water Flows Underneath Surface Media
- Plant Roots Grow in Course Media
Various Types of Constructed Wetlands (Vymazal,
2006)
4Overview
- Removal Processes
- Physical
- Sedimentation and Plant Trap Sediment
- Biological
- Phytodegredation uptake through roots
- Rhizodegredation secretion of contaminants
- Phytovolitization transpiring of contaminants
- Bacteria soil bacteria metabolize organics
- Chemical
- Adsorption transfer of ions to soil particles
- Precipitation converting metals to insoluble
forms - Photo oxidation uses sunlight to breakdown and
oxidize compounds - Volitization breaks down compounds and expels
as gas
Mechanisms in present in a FWS Wetland (EPA, 1999)
5Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
6Suspended Solids
- FWS Wetland
- Flocculation/Sedimentation
- Influenced by particle size, shape, specific
gravity, and fluid media - Discrete settling found by Newtons Law and
Stokes Law - Flocculent settling found experimentally
- Filtration
- Does not play large role since plant stems are
far apart - Interception
- Plays important role where biofilm absorbs
colloidal and soluble matter - Typical suspended solids concentration of 3 mg/L
7Suspended Solids
- VSB Wetland
- Highly effective due to low velocity and large
surface area of media - Sedimentation
- Straining
- Adsorption onto gravel and plant media
- Rock media of less than 5cm to stop clogging
while maintaining performance - 60-75 percent of solids removal happens in first
1/3 of wetland - United Kingdom - Primary Treatment
- Five different types of gravel media analyzed
over two years - Average of 82 removal less than 5 mg/L
8Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
9Organic Matter
- Overview
- Aerobic microorganisms
- Aerated surface waters
- Consume oxygen to breakdown organics
- Provides energy and biomass
- Anaerobic microorganisms
- Anaerobic soils
- Breakdown organics and produce methane
- Store organic carbon in plant biomass
10Organic Matter
- FWS Wetland
- Physical
- Sorption and Volitization
- Biofilms on plants
- VOC removal rate of 80-96
- Biological
- Aerobic
- Oxygen serves as terminal electron acceptor
- Most efficient
- Anoxic
- Nitrates, sulfates, and carbonates serve as
terminal electron acceptor - Less efficient than aerobic
- Anaerobic
- Organics serve as terminal electron acceptor
- Least efficient of three processes
- Bacteria
- Actinomycetes and fungi most important role
- Macrophytes
Organic matter transformations in a FWS Wetland
(EPA, 1999)
11Organic Matter
- VSB Wetland
- Functions as fixed film bioreactor
- Hydrolysis
- Produces soluble organic matter which adheres to
plant - Biological
- Aerobic/Facultative
- Predominant metabolic mechanism
- Anaerobic
- Methanogenisis
- Sulfate reduction
- Gentrification
- Decomposition rather low due to oxygen
concentration less than .1 mg/L
12Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
13Nitrogen
- Important issues
- High nitrates cause blue baby syndrome
- High nitrogen causes eutrofication
- Plant uptake
- Use nitrates and ammonium as nutrients
- Stored as organic nitrogen
- Microorganisms
- Inorganic nitrogen broken down mostly by
denitrification - Nitrogen usually pretty high
14Nitrogen
- Ammonia Volitization
- If pH greater than 9.3 ammonia can be lost to gas
forms - Ammonification
- Organic nitrogen converted to ammonia
- Catabolism of amino acids by aerobic, anaerobic,
and obligate anaerobic - Nitrate Ammonification
- First anoxic process after oxygen is depleted
- Reduction of nitrate to molecular nitrogen or
ammonia - Fixation
- Converting nitrogen gas to organic nitrogen
- Aerobic or Anaerobic by bacteria and blue-green
algae - More important in natural wetlands due to already
nitrogen rich environment
15Nitrogen
- Plant uptake
- Converts inorganic nitrogen to organic nitrogen
- Ammonia or nitrate used as energy or cell growth
- Ammonia Adsorption
- Ionized ammonia adsorbed by inorganic sediment
- Organic Nitrogen Burial
- Nitrogen incorporated into soil of wetland
- ANAMMOX
- Anaerobic ammonia oxidation
- Nitrite used as terminal electron acceptor being
oxidized to ammonium
16Nitrogen
- Nitrification
- Aerobic bacteria oxidize ammonia to nitrite
- Soil bacteria include Nitrosospira,
Nitrosovibrio,
Nitrosolobus, Nitrosococcus, and Nitrosomonas - Bacteria oxidize nitrite to nitrate
- Soil bacteria include Nitrobacter
- Denitrification
- Nitrate is converted to nitrogen gas
- Anaerobic and anoxic conditions breakdown
organics as energy source - Bacillus, Micrococus, and Pseudomonas are
important denitrifying organisms in soils - Pseudomonas, Aeromonas, and Virbio are important
in aquatic environments
Nitrogen transformations in a FWS Wetland (EPA,
1999)
17Nitrogen
- Directly reduces nitrogen
- Ammonia volatilization
- Denitrification
- Plant uptake
- Ammonia adsorption
- Organic nitrogen burial
- ANAMMOX
- Nitrification is limiting step in nitrogen
removal - Denitrification is primary mechanism for nitrogen
removal - Removal efficiencies vary between 40 and 50
18Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
19Phosphorus
- Causes eutrofication
- Removal lower since no metabolic pathway to
remove - Phosphorus present in organic and inorganic forms
Phosphorus transformations in a FWS Wetland (EPA,
1999)
20Phosphorus
- Major removal done by uptake of plant roots
- Plants store phosphorus
- Storage usually greater below ground
- Phosphorus released when plant dies
- Soil adsorption and precipitation
- Soluble inorganic phosphorus stored by soil
particles - Bacteria uptake of phosphorus is quick
- Drawbacks
- Plants and soils reach storage capacity
- Bacteria are unable to store large amounts
21Phosphorus
- VSB Wetland
- Adsorption of phosphorus through soil media
- FWS Wetland
- Uptake from free floating macrophytes
- Macrophytes can be replaced to increase removal
- Removal efficiencies vary between 40 and 60
- Unable to meet primary removal standards
22Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
23Pathogens
- Removal accomplished by sedimentation
- Reports show good removal
- 57 total coliforms
- 62 fecal coliforms
- 98 giardia
- 87 cryptosporidium
- Bacteria accumulate on sediment floor
- Can be disrupted by human activities
- Filtering through root structure
24Pathogens
- Mohammad Karim study of pathogen removal by
sedimentation - Results
- Fecal coliforms and colifages removed more by
root structure - Multispecies wetland
- 73 removal of giardia
- 58 removal of cryptosproridium
- Duckweed wetland
- 98 removal of giardia
- 89 removal of cryptosproridium
- Constructed wetlands offer promise for removing
pathogens
25Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
26Metals
- Removal mechanisms
- Plant uptake
- Soil adsorption
- Precipitation
- Removal depends on types of plants and types of
metals - Duckweed can store large amounts of copper,
cadmium, and selenium - Cadmium, copper, nickel, lead, and zinc form
insoluble compounds with sulfides - Chemisorption
- Chromium, copper, lead, and zinc form chemical
complexes with organic material - Chromium and copper can chemically bind to clays
and settle out
27Metals
(A) Small scale wetland, (B) large scale wetland
(Maine et al., 2006)
- M.A. Maine et all, study of metal uptake in small
and large wetland - 80 Eichhornia crassipes (water hyacinth)
- 14 Typha domingensis (cattail)
- 4 Panicum elephantipes (elephant panicgrass)
- 81, 66, 82 removal of Cr, Ni, Cu in small
wetland - 86, 67, 95 removal of Cr, Ni, Cu in large
wetland - Cr, Ni, Zn found in macrophytes in large wetland
- Cr, Ni, Zn found in sediment in smaller wetland
28Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
29Case Study
- Bilal Tuncsiper tested three types of wetlands in
Turkey - Horizontal-subsurface flow (H-SSF)
- Surface flow (SF)
- Free water surface flow (FWS))
The three different types of constructed wetlands
used in study (Tuncsiper, 2007)
30Case Study
- Results
- 49 52 removal of ammonianitrogen for all
three - 58 removal of nitrates on SF wetland
- 60 removal of phosphorus in H-SSF wetland
- Did not meet drinking water or irrigation
standards - 94 removal of fecal coliforms for all three
- Conclusions
- Constructed wetlands can be used as secondary
treatment of primary treated wastewater
31Removal Mechanisms
Suspended Solids
Organic Matter
Overview
Nitrogen
Phosphorus
Case Study
Pathogens
Metals
32Summary
- Suspended Solids
- Removed by flocculation/sedimentation and
filtration/interception - Organic Matter
- Removed by physical (sorption and volitization)
and biological (aerobic, anaerobic, and anoxic
environments) - Nitrogen
- 30-50 removal mostly by nitrification and
denitrification - Phosphorus
- 40-60 removal by plant uptake,
adsorption/precipitation, and storage in
microorganisms
33Summary
- Pathogens
- High percentage of removal of fecal coliforms,
giardia, and cryptosporidium by sedimentation - Metals
- Selecting proper plants can yield high removal by
plant uptake, soil adsorption, and precipitation - Constructed wetlands
- Good secondary treatment systems for treating
domestic wastewater - Aesthetically pleasing
- Use of simple technologies to remove contaminants
Questions?