Denitrification and energy conservation study at Hutchinson - - PowerPoint PPT Presentation

β–Ά
denitrification and energy conservation study
SMART_READER_LITE
LIVE PREVIEW

Denitrification and energy conservation study at Hutchinson - - PowerPoint PPT Presentation

Denitrification and energy conservation study at Hutchinson Wastewater Treatment Facility Yulin Ye MnTAP Advisor: Karl DeWahl On-site supervisor: Brian Mehr Facility Overview Hutchinson Wastewater Treatment Facility Year in service:


slide-1
SLIDE 1

Denitrification and energy conservation study at Hutchinson Wastewater Treatment Facility

Yulin Ye MnTAP Advisor: Karl DeWahl On-site supervisor: Brian Mehr

slide-2
SLIDE 2

Facility Overview

  • Year in service: 1988
  • Designed flow rate: 3.67 million gallon

per day

  • Treatment capacity: 7,000 lbs

Biological Oxygen Demand (BOD) per day

  • Energy consumption: ~100,000 kWh

per month

Hutchinson Wastewater Treatment Facility

slide-3
SLIDE 3

Facility Overview (cont.)

slide-4
SLIDE 4

Motivations for Change

  • Process modification for nitrate removal
  • Opportunity in energy conservation

through aeration control

slide-5
SLIDE 5

Approach

  • Literature review
  • Bench study of Denitrification rate
  • Monitoring the power of aeration device
  • Plant trials and data collection
slide-6
SLIDE 6

Background of denitrification

2 𝑂𝑃

3 βˆ’

+ 10 𝑓

βˆ’

+ 12 𝐼

+

β†’ 𝑂

2 ↑ + 6 𝐼 2𝑃

Denitrification: the biological process that convert nitrate to harmless nitrogen gas Process requirement:

  • Absent of oxygen (anoxic condition)
  • Present of Microorganism (facultative aerobes) and

readily biodegradable organics

slide-7
SLIDE 7

Denitrification rate study

𝑠

𝐸 = βˆ’ 𝑒𝑇 𝑒𝑒 = 𝑦𝐿𝑑

rD: denitrification rate, mg NO3

β€”N/Lβˆ™h

S: nitrate concentration, mg NO3

β€”N/L

x: denitrification bacteria concentration expressed as mixed liquor volatile suspended solid (MLVSS), mg MLVSS/L Ks: specific denitrification rate, mg NO3

β€”N/mg MLVSSβˆ™h

slide-8
SLIDE 8

Denitrification rate study

0.2 0.4 0.6 0.8 1 5 10 15 20 25 specific denitrification rate, mg N/g MLVSS/h Temperature, Celsius

Denitrification rate V.S temperature

slide-9
SLIDE 9

Modification I

West ditch East ditch Number of aeration rotors 1 2 D.O maintaining point 0.5 mg/L 2.0 mg/L

slide-10
SLIDE 10

Modification I (cont.)

  • An anoxic zone which is approx. 50% of total activated

sludge reactor volume was developed

  • The modification removed 15-20mg/L more nitrate than

the experiment control

  • System instability caused by inadequate mixing was
  • bserved by the end of the test
  • No significant energy saving
slide-11
SLIDE 11

Modification II

Single-ditch operation

  • West ditch was shut down
  • DO maintaining point was lowered from 2mg/L

to 1mg/L

slide-12
SLIDE 12

Modification II (cont.)

  • No degradation in treatment quality
  • Energy consumption was reduced by nearly a

half, resulting in $3,500 in monthly electricity bill

  • Small anoxic zone was developed but

improvement on denitrification was not significant

slide-13
SLIDE 13

Successful Process Changes

Nitrate concentration, mg/L Energy saved per month, kWh Savings in monthly electricity bill Baseline 26 Β±7

  • Modification I

12 Β±4 3,263 $424.88 Modification II

  • 40,089

$3,480.08

  • Modification I enhances nitrate removal of the activated

sludge system and slightly reduces energy usage

  • Modification II cut energy usage by a half while have

limited improvement on nitrate removal

slide-14
SLIDE 14

Recommended Future Projects

  • To find a optimized mixing strategy for

Modification I

  • To test methanol as external carbon

source for complete nitrate removal

slide-15
SLIDE 15

Personal Benefits

  • Understanding in process control
  • Industrial environment exposure
  • Project management
  • Communication skill
slide-16
SLIDE 16

Thank you!