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Nutrient Removal. Objective: To understand the fundamental principles of nutrient removal using chemical and biological methods To know examples of the major wastewater treatment processes for nutrient removal.
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Nutrient Removal Objective: To understand the fundamental principles of nutrient removal using chemical and biological methods To know examples of the major wastewater treatment processes for nutrient removal. Reference: “Operation of municipal wastewater treatment plants. Manual of Practice 11, Vol2 (1996). Water Environment Federation “ http://www.staff.ncl.ac.uk/p.j.sallis/teach.html see section ‘CIV912’; user and password both cassie
Nutrient Removal Introduction Chemical Methods Principle of Biological Nitrogen Removal Biological Nitrogen Removal Processes Principle of Biological Phosphorus Removal Biological Phosphorus Removal Processes Combined Biological N & P Removal Processes
Nutrient levels in a Conventional Aerobic Treatment Plant Final Effluent BOD <20 SS <30 TKN >20 PO4 >10 Aerobic Biological Process Sed Tank Sed Tank Pretreatment Influent BOD 300 SS 300 TKN 50 PO4 15 Primary Sludge Secondary Sludge
Nutrient Cycles • Eutrophication potential • Nutrient balance C:N:P (100:5:1) 10,000 pe x 200 l/d x 15mgN/l 500kg algae/d 10,000 pe x 200 l/d x 5mgP/l 1200kg algae/d
Nutrient Removal - Standards - UWWT Directive (1991): Pop >10,000 N<15mg/l P<2mg/l Pop >100,000 N<10mg/l P<1mg/l or 80% removal of Total P 70 - 80% removal of Total N (The above applies to “sensitive waters”)
Chemical Methods • Nitrogen • Ammonia stripping at high pH (Lime, CaO) NH4+ + OH- NH3 + H2O • Phosphorus • Precipitation by metal ions Ca(OH)2 + HPO42- Ca5(OH)(PO4)3 Al2(SO4)3 + PO43- AlPO4 + SO42-
Biological Nutrient Removal • Assimilation • C, N, P, S etc uptake for synthesis of new cells • Dissimilation • C, N, S, oxidized/reduced to provide energy • Aerobic (oxic) • in the presence of molecular oxygen (O2) • Anoxic • very low concentration of molecular oxygen (O2) • significant levels of electron acceptors (NO3-, SO4-) • Anaerobic • no oxygen, lack of electron acceptors (only CO2)
Biological Nitrogen Removal • Wastewaters contain: Org-N, ammonia, (nitrate) • Dissimilatory metabolism • Nitrification 1. NH4+ + 1.5 O2 NO2- + 2H+ + H2O Nitrosomonas 2. NO2- + 0.5 O2 NO3-(nitrified effluent) Nitrobacter • Denitrification NO3- + CH2 + H+ N2 + CO2 + H2O denitrifying bacteria (many)
Basic Nitrogen Removal System (Ludzak-Ettinger Process) Effluent N2 Influent Anoxic (denitrification) Aerobic QR RAS Modified L-E Process has recycle (QR) Sedimentation Tank
Alternative Nitrogen Removal System Effluent Influent N2 Methanol Aerobic + Nitrification Anoxic (denitrification) Aerobic RAS RAS Re-aeration for Excess Methanol Removal Sedimentation Tank
Biological Phosphorus Removal • Selection of Bacteria in Sludge • Luxury uptake of Phosphorus • (Acinetobacter, Pseudomonas) • Cyclic Environmental Conditions • High BOD when anaerobic • Low BOD when aerobic • Sidestream • P is stripped from sludge in separate unit process • Mainstream • P is concentrated to high levels in the sludge (biomass)
Selection of Bacteria Anaerobic High BOD Carbon uptake (fatty acids stored as poly hydroxy alkanoates PHA)* Phosphate released from cells (polyP PO4, energy released) Aerobic Low BOD Carbon Oxidation (PHA oxidised to CO2, releases energy) Phosphate uptake (Luxury) (PO4 polyP)* * These processes need energy to drive them
PhoStrip Process (Sidestream) Aeration Tank Sed. Tank Influent Effluent RAS Waste Sludge Anaerobic Stripper Phosphorus Stripped Sludge Primary Effluent (BOD, Elutriation) Supernatant Return P Waste Chemical Sludge (P) Lime
N2 Combined N & P Removal Methanol Aeration BOD Rem Nitrific -ation Denitrification RAS PhoStrip Phosphorus Free Sludge P Final Effluent Waste Chemical Sludge (P) Aerobic Anoxic Sedimentation Anaerobic
Anaerobic Settling Tank Anoxic Aerobic N2 Combined N & P Removal (Mainstream) (UNIVERSITY OF CAPE TOWN PROCESS , UCT) Anoxic Re-cycle Nitrified Re-cycle (100-200%Q) (100%Q) NH3 to NO3 HRT= 3-6 h HRT= 0.5-1.0h HRT= 0.5-1.0h Q WAS (P) RAS (50-100%Q) (= 6% P)
Operational Considerations • Maintain discrete environments • excess recycle rate gives completely mixed system • Limitations • Combined System optimized for N (denitrification), biological P removal non-optimized (requires chemical supplementation) • Efficiency • denitrification re-uses Oxygen bound in the nitrate • Contingency • provide P removal by chemical means (when biological process fails)