| Authors |
R. Mireault, SPE, R. Stocker, D. Dunn, SPE, M. Pooladi-Darvish, SPE, Fekete
Associates
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| Source |
SPE International Conference on CO2 Capture, Storage, and Utilization,
10-12 November 2010,
New Orleans, Louisiana, USA
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| Preview |
Abstract
This paper uses the experience gained over the past 13 years in analyzing
and modeling wells that inject mixtures of hydrogen sulphide and carbon dioxide
from sour gas plants to model the operating performance of injection wells for
long term CO2 sequestration from electrical power plants. To predict wellhead
pressures, a numerical simulation model integrates a modified Peng-Robinson
equation-of-state for fluid phase behavior with a wellbore model and a
multi-step adaptation of the Cullender and Smith method to account for the
friction and hydrostatic pressure changes associated with flow in the
wellbore.
As the world embarks on large scale capture and injection of CO2 emissions from
electrical power plants, understanding the operating characteristics of the
injection well(s) will be critical to the design, construction and operation of
these systems. Unlike water injection wells, increasing the injection rate for
a CO2 well does not necessarily increase its wellhead operating pressure. A
methodology to estimate wellhead operating pressures is a key requirement for
the proper design of the injection wells and the CO2 surface facilities. It may
also help engineering and operations personnel, as well as regulatory agencies
to understand the complex behavior of CO2 injection wells.
Pressure gradients in aquifers or reservoirs suitable for CO2 sequestration may
range from a normal hydrostatic gradient to extremely sub-normal in depleted
hydrocarbon reservoirs. Two injection cases present wellbore pressure profiles
for injection into a depleted and a normally pressured reservoir at rates of
20, 100 and 280 103m3/d. Three sensitivity studies illustrate the impact of
bottomhole sandface pressure, CO2 stream composition and wellhead temperature
on wellhead pressure. Depending on conditions, the CO2 stream may undergo phase
transitions from a gas or liquid at the wellhead to dense phase fluid in the
wellbore and back to gaseous or supercritical out in the reservoir. The complex
interactions between phase behavior, fluid density and pressure can lead to
unexpected operating characteristics, including an increase in injection rate
or sandface pressure with little or no change in wellhead injection
pressure.
Introduction
Underground injection and storage is a highly specialized method of dealing
with the hydrogen sulphide (H2S) and carbon dioxide (CO2) “acid gas”
by-products from a sour gas processing plant. Underground injection was
initially developed for small “nuisance” volumes of acid gas, typically less
than 14 103m3/d (500 Mscfd), that were too large to vent directly to atmosphere
but were too small to justify processing through a Claus sulphur plant; the
conventional method of treating H2S.
However, since the 1990’s a worldwide increase in sulphur supply and ongoing
market volatility has increasingly led to investigation of acid gas injection
and storage as an alternative to all sizes of Claus plants and long-term
surface stockpiling of elemental sulphur. Wall and Kenefake (2005) describe a
1,845 103m3/d (65 MMscfd) acid gas injection facility in Southwestern Wyoming,
United States that commenced operation in 2005 to replace aging Claus sulphur
recovery units.
Sourisseau et al. (2000) discuss acid gas injection trains sized for 2,310
103m3/d (84 MMscfd) that are part of a new 22,500 103m3/d (866 MMscfd) sour gas
development in Abu Dhabi.
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