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ANLS-330 Process Analyzers

  • Environmental Monitoring and Standards

Global best-practice in regulating associated gas processing and treatment

Module 3

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Summary description of module ��

An overview of global and local standards for treating associated gas

 

  • Discuss global standards for associated gas treatment and oil and gas industry in general, with country examples
  • Discuss national standards and regulatory practices and identify potential areas for improvement

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Best-practice in Alberta, Canada�Alberta CEMS Code: Continuous Emission Measurement Systems for stationary sources

  • The code by which the CEM is designed, installed, operated and maintained
    • A proper QA (Quality Assurance) / QC (Quality Control) plan is required
    • Daily validations, regular inspection and maintenance, and audits
  • Considerations include the need for a representative sample that is homogenous (i.e., well mixed) and is readily accessible for maintenance

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  • Depending on the industry and plant permit, a CEMS may measure SO2, NOx, CO, TRS (Total Reduced Sulfurs), CO2 and PM (Particulate Matter)
  • The permit also determines reporting requirements
    • Emission rates reported in tons (1000 kg) per day are common
  • A CEMS will typically not measure wind speed and direction nor the low concentration levels that an ambient station does
  • A CEMS must pass a third-party audit or manual stack survey conducted in accordance with the Alberta Stack Sampling Code

Best-practice in Alberta, Canada�Alberta CEMS Code: Continuous Emission Measurement Systems for stationary sources – continued

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CEM typical methods of measurement – common but not exclusive

  • SO2 – UV absorption
  • NOx – UV absorption or Chemiluminescence
  • CO and CO2 – NDIR
  • Particulate Matter – Opacity

Best-practice in Alberta, Canada�Alberta CEMS Code: Continuous Emission Measurement Systems for stationary sources – continued

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CEM sampling methods – to extract a sample or not

  • In-situ measurement
    • Measurement “in the natural or original position”
    • Across the stack design is most common
    • Opacity is a common example
  • Extractive
    • Sample is removed (extracted) from the stack
      1. Hot / wet sample
      2. Cool / dry sample
      3. Diluted sample

Best-practice in Alberta, Canada�Alberta CEMS Code: Continuous Emission Measurement Systems for stationary sources – continued

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In-situ vs extractive CEMS sampling

Figure 1. Types of CEM technology. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

In-situ analyzers seem the obvious choice for simplicity but keep in mind doing maintenance at 40m in January

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Opacity measurement

    • Based on transmittance of light across the stack
    • Percent opacity is reported in percent of light not transmitting across the stack

% Opacity = 100 - %T

E.g. 30% Opacity = 100 - 70%T

Where:

%T = percentage of light transmitting across the stack

Figure 2. In-situ stack opacity measurement. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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Extractive systems: cool-dry or hot-wet

A sample dryer is not shown but is required for a cool/dry sample.

Think of the CEMS in the lab

An aspirator / eductor can be used in place of a pump. Again, think of the CEM in the lab. It has an aspirator integral to its design.

A heated sample bundle is common to both designs

Figure 3. Cool dry extractive CEM. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

Figure 4. Hot wet extractive CEM. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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Extractive dilution systems

  • Dilute sample at controlled dilution ratio
    • Dilution lowers dew point to accommodate dry measurement analyzers
    • The target gas concentrations are also reduced
  • Use highly sensitive analyzers to measure the resulting lower concentrations

Figure 5. Diluted gas CEM system. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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CEMS Code: �Continuous Emission Measurement Systems for stationary sources

  • The code by which the CEM is designed, installed, operated and maintained [2]
    • A proper QA (Quality Assurance) / QC (Quality Control) plan is required
    • Daily validations, regular inspection and maintenance, and audits
  • Considerations include the need for a representative sample that is homogenous (i.e., well mixed) and is readily accessible for maintenance

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CEMS Code – continued

  • Performance Specifications evaluate the acceptability of the CEMS at the time of or soon after installation:
    • Linearity
    • Relative accuracy
    • Bias
    • Zero drift – 24 hr
    • Span drift – 24 hr
    • Availability per month

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Performance specifications excerpt

Analyzer

Linearity

Relative accuracy

Bias

Zero drift-24 hr

Span drift-24 hr

Availability

Sulfur dioxide

≤ ± 2.0% of span

≤ ± 10.0% of RM

≤ ± 5.0% of FS

≤ ± 2.5% of span

≤ ± 2.5% of span

≥ 90.0%

Nitrogen oxides

≤ ± 2.0% of span

≤ ± 10.0% of RM

≤ ± 5.0% of FS

≤ ± 2.5% of span

≤ ± 2.5% of span

≥ 90.0%

Table1. Performance specifications. Adapted from Government of Alberta CEMS Code – Draft Version, (2018)

What is the same from your government?

CEMS Code – continued

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  • Figure 6. Air quality monitoring station (Warren 2018).

CEMS Code – continued

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Airshed zones: ambient air quality measurement

Figure 7. Alberta’s airshed zones. Adapted from Instrument Technician ILM, Environmental Monitoring – Part B, 310404cB, (2019)

What is in your country?

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Ambient typical methods of measurement

  • H2S and SO2 – UV Fluorescence
  • NOx – Chemiluminescence
  • CO and CO2 – NDIR
  • Ozone – UV Absorption
  • THC (total hydrocarbons) – Flame Ionization Detector
  • VOC – GC or Mass Spectrometry
  • Particulate Matter – Tapered Element Oscillating Microbalance
  • Total Suspended Particulate – High Volume Sampler c/w a weight analysis

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Wind speed and direction

  • Figure 8. Wind speed and direction (Warren 2018).

Cup anemometer

Wind vane

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Fugitive emissions – unwanted escape

  • Pollutants released by leaks from pressurized process equipment
    • VOCs (volatile organic compounds) are commonly monitored fugitive emissions
  • Measure at multiple sample points near high-risk sources
  • Possible measuring techniques
    • Mass spectrometer
    • Open-path devices

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Acid rain formation

Figure 9. Acid Rain. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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Acid rain – SO2, NOx and H2S + water

  • SO2, NOx, H2S react with water vapor in the atmosphere to form acid rain
  • A pH of less than 5 defines acid rain

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Sulfur emissions – think acid rain

  • Sulfuric acid formation in the atmosphere contributes to acid rain
    • S + O2 SO2
    • SO2 + H2O H2SO3 (sulfurous acid)
    • SO2 + oxidize SO3 + H2O H2SO4 (sulfuric acid)

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Sulfur emission harmful effects – continued

  • Physiological
    • E.g., tiny sulphate particles penetrate the lungs which can aggravate respiratory conditions or diseases
  • Defoliation and other harmful effects to plants
  • Corrosion

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Nitrogen oxides (NOx) – acid rain and smog contributor

  • A product of high temperature combustion
    • Consider temperatures in excess of 1200 °C
    • Internal combustion engines a major source
  • Reacts with oxygen to create ground-level ozone
    • Ozone contributes to smog

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Smog formation – remember the Calgary photo?

Figure 10. Smog. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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Smog: air pollutants + particulates

  • Originally coined from a contraction of the words “smoke” and “fog”
  • Composed of nitrogen oxides, sulfur oxides, ozone and particulates
  • Particulate matter size is very important when assessing risk to human health
    • PM10 and PM2.5 refer to the particulate diameter size in µm
    • PM2.5 is the more dangerous particulate because it refers to particulate size 2.5 µm or less, which is more easily lodged in the lungs when inhaled

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Fine particulate matter PM10 vs PM2.5 vs human hair

  • Figure 11. PM2.5 (Warren 2018).

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Greenhouse effect

Figure 12. Greenhouse effect. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

Beyond CO2, GHG’s also include water vapour, CH4 (methane), N2O (nitrous oxide) and ozone (O3)

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Greenhouse gases (GHGs)

  • Major GHGs are water vapour, CO2, CH4 (methane), N2O (nitrous oxide) and ozone (O3)
  • Abnormal amounts of GHGs absorb IR energy emitted from earth’s surface, resulting in a warming of the atmosphere
  • Acidification of the oceans (i.e. absorption of CO2 forms carbonic acid) is also a huge concern

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Ambient water quality measurement

  • Two sources include:
    • Surface water
    • Ground water – water below the surface accessible by wells
  • Water-effluent contaminants and conditions needing measurement include:
    • Dissolved oxygen
    • pH
    • Temperature
    • Turbidity

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Water quality measurement categories

“I’m not getting a lot of propulsion”

Figure 13. Water quality measurements for fish. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

Figure 6. Water quality measurement categories. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

What is 2 mg/L dissolved O2 in ppm?

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Industrial air quality management

  • Management accomplished through:
    • Regulation
    • Environmental assessment
    • Approvals
    • Enforcement

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Government regulation

  • Through one type of body:
    • Government ministries
      1. Part of the whole country‘s government

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Government roles

  • Government’s bodies
    • Ministries include
      1. Environment
      2. Agriculture
      3. Health
      4. Transport
    • Independent agencies
      • Environmental Assessment Agency
      • National Energy Board (e.g. Energy East Pipeline assessment)
      • Regulating agencies

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Country’s key acts – acts are laws

  • Environmental Protection and Enhancement Act
  • Water Act
  • Climate Change Emissions Management Act

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Regulatory compliance

  • The government's bodies enforce regulatory compliance under the Environmental Protection and Enhancement Act
  • Compliance program consists of:
    • Inspection
    • Investigation
    • Compulsory monitoring
    • Reclamation programs

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Case study: Alberta ESRD (AEP) – key acts are laws

  • Environmental Protection and Enhancement Act
  • Water Act
  • Climate Change Emissions Management Act

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Case study: regulatory compliance – continued

  • The ESRD (AEP) enforces regulatory compliance under the Environmental Protection and Enhancement Act
  • Compliance program consists of:
    • Inspection
    • Investigation
    • Compulsory monitoring
    • Reclamation programs

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Case study: regulatory compliance – continued�Government roles

    • Environmental protection enacted through by-laws
    • Examples:
      1. Regulate drainage in storm sewers
      2. Transportation of dangerous goods
      3. Waste management
      4. Wastewater disposal
      5. Water utility system protection

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Air Monitoring Directive (AMD): it starts here

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Applicable standards and codes for CEMS and ambient stations

  • Follow these codes and guidelines when working on air pollution monitoring equipment
    • Air Monitoring Directive
      1. General document addressing all major air pollutants
      2. Procedures for following proper monitoring and reporting protocol for both source (CEM) and ambient stations
    • Continuous Emission Monitoring System (CEMS) Code
      • Installation, operation, maintenance and certification of the CEM
    • Ambient Air Quality Objectives and Guidelines
      • Maximum acceptable ambient air concentrations

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Management framework�Approvals are at the centre of most tasks

Figure 1. Industrial air quality management. Adapted from Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA, (2019)

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Main take-aways

  • Compare standards in your country to standards that Alberta, Canada is adopting
  • Suggest an addition to current regulatory measures in your country
  • Apply the BAT mentioned in Module 2 to current local standards
  • Consider safety and mitigation SOPs in the local standard proposed “suggested” changes as mentioned in Module 2

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References

  • 1. Buracas, Ted. (2008). Smoggy Calgary-800x600[Image file.] Retrieved from: https://www.flickr.com/photos/teddyboy/412721365/in/photolist-2iCj8ui-H4cBEd-HyB495-4QLc1x-CtiFB-4oi76c-5zScLo-5zMUSM-5zSe9s-5zMV3H-hM9iy9
  • 2. Government of Alberta – Environment and Parks (Draft Version, 2018). Alberta Continuous Emission Monitoring System (CEMS) Code.
  • 3. Government of Alberta – Advanced Education (2019). Instrument Technician ILM, Environmental Monitoring – Part A, 310404cA
  • 4. Government of Alberta – Advanced Education (2019). Instrument Technician ILM, Environmental Monitoring – Part B, 310404cB
  • 5. United States Environmental Protection Agency – Acid Rain Division (1994). An Operator’s Guide to Eliminating Bias in CEM Systems.
  • 6. Warren, Kevin – AMAROK Consulting (2018). Parkland Airshed Management Zone (PAMZ) [PowerPoint slides]

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