H2S Emission Abatement
by Gary J Nagl
May 1, 2010
Controlling emissions keeps a geothermal power facility operating well after 15 years.
Wind comes and goes. Rivers flood. Biofuels take up farmland
that could otherwise feed people. The sun sets or hides behind clouds. So among
renewable energy sources, geothermal power plants are environmentally
attractive since their energy resource is continuous.
Unfortunately, geothermal steam often contains
varying amounts of non-condensable gases (NCGs) such as CO2,
H2S, mercury vapor and, in some cases, benzene, which if
not disposed of properly may cause environmental, health and safety problems.
Effective control of these emissions can make geothermal energy a viable
construct. This is evidenced by the operating history of three geothermal power
facilities that have been in service for 15 years while meeting strict
California emission regulations.
Facility history
Terra-Gen Power LLC operates a geothermal power facility on
the China Lake Naval Weapons Center in southeastern California. As illustrated
in Figure 1, hot brine is extracted from high-pressure,
underground wells. The brine is flashed and the produced steam is passed
through condensing turbine/generator sets, which produce approximately 250 MW
of electrical power. The electricity, enough power to service approximately
250,000 homes, is then sent into the local power grid.
The unflashed brine and condensate from the
turbine/generator sets are reinjected into the geothermal reservoir and the
NCGs, consisting mostly of CO 2, are sent to treatment
facilities. Initially, the NCGs were injected back into the reservoir. However,
over time this practice began to affect the performance of the reservoir and
the practice was stopped. It was then decided to remove the H 2S
and mercury from the NCG mixture, and exhaust the remaining gas, CO 2
and water vapor, to the atmosphere.
In 1993, a former owner of the facility began an
investigation into various H 2S and mercury removal
systems. He eventually decided on the Lo-Cat, an isothermal system from
Houston-based Merichem Chemicals & Refinery Services LLC. The process
involved a sulfided, activated carbon media upstream of the process for mercury
removal. These systems were initially installed at the Navy I and Navy II
facilities. A third system was later added at Navy II due to larger gas loading
than previously anticipated.
Thermal process
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| The treatment systems provided by Lo-Cat effectively removed the undesirable emissions from the geothermal operations at the China Lake Naval Weapons Center.
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The process accomplishes direct oxidation of H 2S
to elemental sulfur as depicted in the following equation:
Equation 1: H2S + 1/2 O2
<--> H2O + S0
This reaction is accomplished in an aqueous scrubbing system
by using a water-soluble metal ion. The metal is capable of oxidation in
ambient air or in the process gas stream, and has a suitable electropotential
for oxidizing the sulfide ion to elemental sulfur. Although there are many
metals that can perform these functions, iron was chosen for the process
because it is inexpensive, non-toxic and is a good oxidation catalyst.
The basic reactions of the process can be divided into the
absorption and regeneration portions as follows (aq = aqueous):
Absorption:
• Equation 2: H2S
absorption: H2S (gas) + H2O <--> H2S (aq) + H2O
• Equation 3: First Ionization: H2S
(aq) <--> H+
+ HS-
• Equation 4: Oxidation by ferric ions: HS- + 2Fe3+
<--> S0 (solid) + 2Fe2+
• Equation 5: Overall absorption reaction: H2S
(gas) + 2Fe3+ <-->
2H+ + So + 2Fe2+
Regeneration:
• Equation 6: 1/2 O2 (gas)
+ H2O <--> 1/2 O2 (aq) + H2O
• Equation 7: Regeneration of ferrous ions: 1/2 O2
(aq) + H2O + 2Fe2+ <--> 2OH-
+ 2Fe3+
• Equation 8: Overall regeneration reaction: 1/2 O2
(gas) + H2O + 2Fe2+ <-->
2OH- + 2Fe3+
Adding Equations 5 and 8 yields Equation 1.
System design
As previously mentioned, three units were installed at the
facility to handle gas streams from six geothermal power plants. The design
parameters for each of these units can be seen in Figure 2.
Since the treated NCGs from each unit could be exhausted to
the atmosphere in accordance with air permit requirements, an auto-circulation
unit was selected for these applications. In this process configuration ( Figure
1), the auto-circulation vessel contains a series of baffle and weir
combinations that separate the absorption sections from the regeneration
sections. The system also incorporates a series of natural hydraulic pumps
produced by the aerated liquid on one side of the baffle and the non-aerated
liquid on the other side of the baffle. This provides the motive force for
circulating the solution from one chamber to the next. The process flow diagram
for each unit is shown in Figure 3.
The discharge gas from the NCG compressors is initially
processed through a bed of pre-sulfided, activated carbon, in which the mercury
vapor is removed from the gas stream by adsorption onto the activated carbon.
The NCG is then directed into the auto-circulation vessel, where the H 2S
is absorbed into the solution and rapidly converted into solid, elemental sulfur,
which remains suspended in the circulating solution. The solution is then
contacted with air in a separate chamber (or chambers) and the iron is
re-oxidized. The spent air and sweet NCGs are combined and exhausted to the
atmosphere.
A small slipstream of solution is pumped from
the auto-circulation vessel and directed to a settler, where the sulfur is
allowed to settle into a concentrated slurry. This slurry is then directed to a
vacuum belt filter. The sulfur cake is washed with water on the filter, the
filtrate is returned to the unit, and the sulfur cake is sold as
fertilizer/fungicide at approximately 70-wt.-percent sulfur. The sulfur has
excellent soil absorption characteristics. In addition, residual surfactant,
which is employed in the process, enhances the hydrophilicity of the sulfur.
The chelated iron and thiosulfate contained in the process solution also add
micronutrients to the product sulfur.
Operating history
As required in the operating permits, the effluent gas
streams from each unit are continuously monitored via lead acetate type
monitors. Over the 15 years of operation, the three units have consistently
exceeded the H 2S removal efficiency required by the
operating permits, which equates to greater than 99.9 percent removal
efficiency.
In June 1996, Tom Mason, the president and chief operating
officer of CalEnergy Company Inc. – the owners of the facility at that time –
wrote in the Geothermic Resource Council's GRC Bulletin that "The
statistics clearly demonstrate the success of the company's efforts. CalEnergy
believes that the [H 2S abatement systems] currently in
place at Coso constitute the best available control technology."
Normally the units have fairly large solution inventories,
and for units processing CO 2, as in these cases, the
solution is well buffered with KHCO 3 and K 2CO 4.
Consequently, changes to the solution chemistry and the unit's performance are
never immediate but occur over a fairly long time period. This operating
characteristic results in minimum monitoring of the operations. Generally, the
only duties for the operator is to measure the pH and redox potential of the
solution on a daily basis, and the iron concentration on a weekly basis, and
then make the corresponding adjustments to the chemical addition pumps. This
takes no longer than two to three hours per day of an operator's time.
Maintenance
The original auto-circulation and settler vessels for all
three units have not experienced corrosion or had significant repair over the
15 years of operation. The original progressive cavity pumps, which were
employed to transfer the sulfur slurry from the auto-circulation vessel to the
settler, did experience stator erosion and were replaced with a gravity feed
system. The filter cloths on each vacuum belt filter have been regularly
replaced every three to six months. The rubber belt drive is replaced every two
to three years. The units were designed such that the filter cloth and belt can
be replaced while the unit continues to run.
The entire power trains are shut down for
maintenance once a year. During that shutdown period, the units are also
serviced. This service includes removal of the NCG and oxidizer air spargers
for inspection, cleaning and repair as necessary, as well as cleanout of the
vessels, and pump and equipment maintenance as required. Through detailed
planning by plant personnel, a complete turnaround of a unit can be conducted
in two days. PE
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