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Production of Nitric Acid

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Nitric Acid (HNO3) Nitric Oxide (NO) Nitrogen Dioxide (NO2) Nitrous Oxide (N2O) ... Oxide. n/a. 0.037 mg/m3 (NAAQS) Nitrogen Dioxide. n/a. n/a. Nitric Oxide. n ... – PowerPoint PPT presentation

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Title: Production of Nitric Acid


1
Production of Nitric Acid Environmental Impact
Assessment
Erik Tolonen
Nick Poulin
Environmental Engineering Environmental Planning
and Decision Making ENVE4104
2
Contents
Introduction Risk Assessment Fault Tree Event Tree
3
Introduction
  • Chemicals of Interest
  • Ammonia (NH3)
  • Nitric Acid (HNO3)
  • Nitric Oxide (NO)
  • Nitrogen Dioxide (NO2)
  • Nitrous Oxide (N2O)

Ammonia was determined to be the most hazardous
chemical present in the process
4
Hazard Identification
All chemicals are non-carcinogenic
5
Hazard IdentificationNH3
Ammonia is considered to be toxic by the Canadian
Environmental Protection Act
  • Human Health Effects
  • Causes irritation of the eyes, skin and
    respiratory system
  • No Observed Adverse Effect Level (NOAEL) 6.4
    mg/m3
  • Lowest Observed Adverse Effect Level (LOAEL)
    17.4 mg/m3
  • Respiratory lesions increase the severity of
    pneumonia and rhinitis
  • Environmental Effects
  • Impact on certain types of plants and trees
    (reduced ability to retain water)

6
Exposure Assessment
7
Transport Media
Transport Mechanism
Exposure Mechanism
Population at Risk
8
Air Transport Model
Assumptions - Transport by advection and
dispersion only - Ammonia is released from a 20 m
height stack with a 10 m plumb rise - Wind
direction is directly towards the city (Worst
Case Scenario) - No density or buoyancy effects
Gaussian Model Parameters - Atmosphere Stability
Class D - Rate of Emission 0.062 kg/s (223.2
kg/hr) over 30 hours - Total Amount of Ammonia
Released 6696 kg - Inhalation Reference Exposure
Level 0.3 ppm
9
(No Transcript)
10
City
11
Air Transport Model
Results - Ammonia levels in the city will reach
0.3 ppm when emission rate reaches 80311.7 kg/s
(80.3 tonnes/s). - Amount required is much
greater then current release at plant
12
Water/Ground Water Transport Model
Assumptions -Transport by advection
only -Thoroughly mixed with river water -No
retardation or attenuation present in soil
Advection -Flow time to reach city 84.3
yrs -Flow time to reach river 28.2 yrs
  • Solubility
  • 42.8 wt at 0 OC
  • - Amount of Ammonia entering groundwater
    insignificant

13
Exposure Assessment
  • Intake Dose
  • I CxCRxEFxED/BWxAT
  • C Conc. at exposure point 0.00008 ppm
    (0.00011mg/m3)
  • CR Contact Rate 289.5 m3/hr 6947 m3/day
  • EF Exposure Frequency 1.25 days/year
  • ED Exposure Duration 30 hrs 0.003 year
  • BW Body Weight 70 kg
  • AT 1.25 days
  • I 0.00003 mg/kg-day

14
Toxicity Assessment
  • Case Studies
  • (1) Soda Ash Facility Workers Exposed to Ammonia
  • No Observed Adverse Effect Level (NOAEL) 9.2
    ppm (6.4 mg/m3)
  • (2) 344 Rats Exposed to Ammonia
  • Lowest Observed Adverse Effect Level (LOAEL)
    17.4 mg/m3

15
Risk Characterization
  • Hazard Index for Ammonia
  • HI CDI/RfC
  • CDI chronic daily intake
  • RfC reference dose 0.3 ppm

16
Fault Tree
17
Event Tree
18
Conclusions
  • Conclusions
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