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Landfill
gas flare systems often seem like a large “black
box” just waiting for something to go wrong, with
few people willing to understand the fundamentals of
flare design and operation.
By Tim Locke
With some
basic knowledge, you can learn simple, easy ways to
minimize O&M time, stay in compliance, and minimize
complaints about the flare. There are three common operational
questions engineers and operators continue to ask. How
can I get a greater turndown with my flare? How do I
deal with low methane concentrations? And, how can I
effectively control landfill gas to a third party user?
People from
all aspects of the landfill industry have questions
on how to minimize time and effort with landfill gas
flare systems. Low flow rates, low methane concentrations,
high oxygen concentrations, and third-party users can
wreak havoc with the operation of flare systems. Understanding
how these key elements affect the combustion process
through landfill gas burner flow distribution and the
flow of combustion air are critical to ease of operation
and maintenance of the system.
Combustion
101
Combustion of landfill gas is primarily limited
to the oxidation of methane (CH4), or in other words,
the combination of methane, oxygen, and heat. This can
be shown as the following equation:
CH4 + 2O4→ CO2 + 2H2O
The products
of the above stoichiometric reaction are merely carbon
dioxide and water. This reaction is very simple when
looking at only the reactants on the left of the arrow
and the products on the right. In reality, each molecule
of methane and oxygen is broken down into individual
atoms before they recombine into the product molecules.
Very simplistically, the above reaction can be rewritten
as follows:
CH4+2O2→C+H+H+H+H+O+O+O+O→CO2 + 2H2O
In order
to make this reaction happen, heat is required to start
the process. Once the methane molecule has been brought
up to its autoignition temperature, enough heat is generated
from the molecular bonds breaking to continue the process
as long as methane and oxygen are present. After each
molecule has been broken down into its individual atoms,
those atoms then recombine into different molecules,
in this case carbon dioxide and water.
The amount
of oxygen required to oxidize methane has been determined
and is defined as the Lower Explosive Limit (LEL) and
the Upper Explosive Limit (UEL), otherwise known as
Flammability Limits. Since the oxygen required for this
process is derived from atmospheric air, the UEL and
LEL are stated as a function of the compound to be oxidized
and air. For example, the flammability limits for methane
are 5% to 15%. This means that a volume of air that
contains between 5% and 15% methane is flammable.
| Figure 1 |
 |
Maintaining
this mixture of methane and air is critical to the combustion
process; if the mixture goes below the LEL or above
the UEL, the combustion process ceases. This is precisely
what happens when flares “rumble” or “vibrate.”
Once the
proper amount of air and methane mix, the autoignition
temperature has been reached, the combustion process
is stable, and now the temperature must be controlled.
This is done by modulating air dampers at the base of
an enclosed flare (Figure 1).
Flare
Turndown
The amount of turndown capable for a given
enclosed flare is primarily based on the amount of combustion
air entering the stack. As indicated in the operating
temperature vs. combustion air graph (Graph 1), the
larger amounts of combustion air correlate to decreasing
operating temperatures. Therefore, the key to maintaining
the desired operating temperature inside an enclosed
flare at low landfill gas flow rates is to minimize
the amount of combustion air entering the stack. This
can be accomplished by the following:
- Fully
closing both the manual and automatic air dampers;
- Removing
one or more of the air dampers and replacing them
with a steel blind plate;
- Replacing
an air damper with a partial blind plate and a smaller
air damper, generally 15% to 30% in size;
- Any combination
of the above.
| Graph 1 |
 |
While decreasing
the air flow into the stack will increase the operating
temperature of the enclosed flare, the lower flow rates
of the landfill gas will also have impacts on other
aspects of normal flare operation. These issues are
the initial burner ignition at a low flow rate, poor
air and gas distribution, and a lower heat profile.
At extremely
low flow rates, the landfill gas is not distributed
evenly between the existing burners. Because of this,
it becomes difficult to “cross light” from
burner to burner to establish a stable flame during
the initial start-up. Small amounts of landfill gas
can flow unburned through certain burners, allowing
gas to build up in the stack. When the light-off eventually
takes place, it happens suddenly, with a contained explosion.
In order to prevent this low-flow distribution issue,
some of the burners can be replaced with blind flanges
or in some cases the burner holes can be plugged in
order to divert the gas flow to the remaining burners.
If the goal is to have the original maximum design flow
rate on the enclosed flare, it will not be possible
to remove and blind burners.
Just as
low landfill gas flow has poor distribution through
the burners, the same is true with the required combustion
air. The most critical factor in the combustion process
is having the appropriate amount of air-to-landfill
gas ratio for each burner. If burner tips are removed
for proper gas flow distribution, the corresponding
air flow around the removed burners should also be blocked.
This can be accomplished by adding an insulated cover
in the annular space of the removed or plugged burner
tip. The cover should be installed so that combustion
air can no longer enter the enclosed flare around the
removed burner. With this cover in place, the air flow
is now diverted to the burner(s) that require the combustion
air.
Under extreme
turndown conditions, it is impossible to maintain the
normal operating temperature without modifications,
even at the lowest standard thermocouple in the stack.
Because of this, a new thermocouple must be added. There
are two criteria for this: proper orientation and proper
elevation. The most effective orientation for the new
lower thermocouple is to place it directly over a burner,
preferably a burner symmetrically placed in the middle
of the remaining burners. The applicable requirements
for retention time will govern over the proper elevation.
Most air permits for enclosed flares require a 0.6 second
retention time at the permitted operating temperature.
For the lower stack thermocouple elevation, at least
0.6 seconds must be achieved at this elevation for the
desired turndown. When the gas flow rate increases and
the retention time drops below 0.6 seconds, the next
higher thermocouple in the stack must be selected to
control the operating temperature.
Low
Methane Levels
Low methane concentrations in landfill gas
are another common concern regarding the performance
of a flare system. In general, most flare systems are
capable of operating with methane concentrations as
low as 25 to 30%. At this point, they will start to
experience instability and eventually flame lift-off.
Typical scenarios that can result in low methane concentrations
are:
- Older,
closed landfills
- Perimeter
gas collection
- Collection
system leaks
Older
Landfills
Older, closed landfills progressively experience
lower methane concentrations and gas flow rates over
time. This creates two issues regarding flare operation.
One is maintaining enough flow in order to achieve the
operating temperature inside an enclosed stack, and
the other is having enough methane to burn. The low
flow rate turndown issue has already been discussed,
but the flare can also be modified to operate with low
methane concentrations. Since flame stability is a function
of the flame propagation speed, the burner exit velocity
can be reduced to maintain the operation of the flare.
Flares are in operation today with methane concentrations
as low as 15 to 18% using this technique. As the concentrations
start to fall below 15%, flare systems can be set up
to operate on timed cycles, allowing the methane to
build up during down periods.
Perimeter
Gas Collection
Perimeter gas collection can also lead to
low methane concentrations, especially when it is primarily
used to keep gas from migrating offsite. In addition
to the lower methane concentrations, it is common to
experience higher levels of oxygen in the gas due to
the perimeter gas wells being on the boundary of the
landfill, thus pulling in ambient air. From the standpoint
of the flare, the higher oxygen concentrations will
generally help the combustion process, although it has
been known to cause rumbling and vibrations in some
instances. Otherwise, flare turndown in this scenario
should be handled in the same manner as indicated for
closed landfills.
Collection
System Leaks
System leaks from the gas wells, collection headers,
and sumps can create an influx of air into the landfill
gas. A small influx of ambient air due to a leaking
point in the collection system will create an oxygen-laden
gas very similar to that of a perimeter gas system.
In this case, the flare can handle the lower methane
concentrations in the same manner. However, if a substantial
collection system breach occurs allowing the oxygen
concentration to exceed 15%, then a combustible mixture
is likely present. At low flow rates and during shutdowns,
burnback can occur in the burner manifold or stack in
the case of a candlestick flare, and cause material
or structural damage.
Gas
To A Third-Party User
Whether you have an existing landfill gas
flare system or require a backup for a gas utilization
project, interfacing with a primary user can be difficult.
In addition to the critical communication required between
the flare control panel and the gas utilization source,
it is important to optimize the performance of the overall
system.
A gas utilization
project is normally designed to accept a preset, not-to-exceed
amount of landfill gas where the flare system is designed
to accept all the gas a landfill can generate. Because
of this flow rate difference, one of two things generally
occurs. Either the flare system acts as a backup and
burns gas that the utilization project does not require,
or the flare is not utilized properly and the gas is
not fully extracted from the landfill. In order to design
a proper interfacing system, the following three items
need to be addressed:
- Supplying
gas to the utilization project
- Flare
turndown
- Communication
between the flare and the utilization project
Gas
From the Landfill
A gas project usually requires a positive
displacement compressor to pressurize the landfill gas
in order to meet the requirements of the internal combustion
engine, turbine, pipeline, etc. While it is possible
that this same compressor could pull directly from the
landfill, it is more effective to send gas to the compressor
from the landfill gas blowers, unless an elaborate control
scheme is put into place.
If the compressor
were to extract gas directly from the landfill, the
vacuum generated on the collection system must always
be less than the capability of the landfill gas flare
blowers. This is possible under ideal conditions; however,
since the compressor is likely to be a positive displacement
device, it will get the flow it wants or keep increasing
the vacuum until it does. If the vacuum increases to
the limit of the landfill gas blowers, then it becomes
impossible to extract all the available gas from the
landfill. Even a slight increase in the vacuum from
the compressor can change the dynamics of the collection
system.
A more common
approach is to let the flare system blowers extract
gas from the landfill as shown in Fig. 2. In this case,
a vacuum transmitter on the collection system sends
a signal to a variable frequency drive (VFD) on the
gas blower motor. A pressure controller then maintains
a constant vacuum on the system to allow all of the
gas to be extracted, regardless of the condition. Once
all the gas is collected, it can then be sent either
to the gas utilization project, the flare, or both.
This is done by adding a pressure transmitter in the
gas utilization header and a pressure control valve.
The pressure controller in this scenario maintains a
constant pressure to the compressor to meet its demand.
Any excess gas will go automatically to the flare. This
simple control system will also require less maintenance
and is easier to operate than the alternative.
Flare
Turndown
In instances where the gas utilization facility
uses almost all the landfill gas available, the flare
must be capable of turndowns in excess of the original
design. The turndown modification in this case is more
critical, because the flare must also be capable of
operation at the maximum flow rate. With this criterion,
the most common solution is to add a thermocouple at
an elevation of approximately 8 feet to 10 feet for
use only at extremely low flow rates. This additional
thermocouple will allow the flare to maintain the operating
temperature at a lower flow rate than the original design.
If the air permit for the flare does not specify a minimum
operating temperature, then the flow rate can easily
be decreased further.
 |
PHOTO: PERENNIAL ENERGY |
| The key to maintaining desired temperatures inside an enclosed flare is to minimize the amount of combustion air entering the stack. |
In extreme
turndown conditions, the minimum flow rate to the flare
must be maintained or the operating temperature cannot
be controlled. This can easily be achieved with either
a mechanical or a software minimum stop placed on the
pressure control valve. The minimum stop set point for
the control valve must be configured in the field and
should not allow the valve to close past what is required
for the minimum flow condition. If the minimum stop
is not incorporated into the pressure control valve,
then the flare will automatically shut down on low operating
temperature or flame failure, unless this shutdown is
disabled.
Communication
Communication between the flare system and
the gas utilization project can be critical to both
operations. The main items that need to be incorporated
into the flare control panel to maximize the operation
of the overall system are:
Blower Operation. Landfill gas blowers normally shut down when the flare
shuts down. Under the gas utilization scenario, the
blowers must remain in operation even if the flare shuts
down. Therefore, logic must be added to the flare control
panel such that both the flare and gas compressor must
shut down in order to shut down flare blowers.
| Figure 2. |
 |
In addition
to changing the blower shutdown logic, the logic for
the pressure control valve must also be incorporated.
For example, in the case of a flare shutdown, the pressure
control valve will close, fully diverting all the gas
to the compressor. Since the compressor cannot take
all the gas available, the pressure control loop of
the blower must now be changed from vacuum-control to
pressure-control based on the discharge header pressure
transmitter.
Pressure
Control. Since the compressor for the gas utilization
project is likely a positive displacement machine, it
can easily overcome the incoming header pressure if
its flow demand increases. If this does happen, it is
possible to pull landfill gas out of the flare—and
possibly even air into the system—before it has
a chance to shut down. In addition, if the compressor
demand is greater than the amount of gas available,
it will pull through the landfill gas blowers, causing
an over-extraction on the landfill.
In order
to compensate for the scenario described above, a low-pressure
alarm and low-pressure shutdown should be added to the
flare control logic. Therefore, if the pressure in the
blower discharge header decreases to a certain level
below the operating set point, an alarm signal is sent
to the gas utilization facility.
If the pressure
continues to decrease below the pressure set point,
the landfill gas blowers will shut down.
Status of
Operation. The gas utilization project will require
trained operating technicians for the facility. Since
the flare system will not have this type of operating
personnel, it is important that the flare-control panel
report all the required status back to the gas facility.
Also, just as important, the gas facility must provide
certain information to the flare-control panel.
The flare-control
panel, as a minimum, must receive a signal from the
gas facility that it is ready to begin operation. This
will allow the actuation of the pressure control valve.
While other status signals can be received from the
gas facility, they are not required for a fully functional
system.
As for the
gas facility, it can retrieve any status available from
the control panel, including flare status, flow rate,
pressure, temperature, or vacuum.
Conclusion
By understanding the basic design concepts
of landfill flares and learning a few common fixes,
it is possible to make logical, step-by-step changes
to improve the performance of a landfill gas flare system.
Applying
this knowledge can minimize time spent on operation
and maintenance, help achieve compliance with environmental
regulations, and reduce downtime, saving time and money.
MSW
Management contributor Tim Locke is the manager of the
Biogas Control Group for John Zink Co., LLC.
MSW
- March/April 2006 |