TY - GEN
T1 - How Squeeze Management Differs during Field Redevelopment
AU - Wang, Xu
AU - Mackay, Eric James
AU - Jordan, Myles Martin
N1 - Funding Information:
in early 1996. Two wells from this early production period are selected for comparison discussions in this paper – Well E1 and Well E2. All the producers were supported by seawater injection during this period. Then there was a shut-in period that started in early 2006, and a redevelopment plan was established with first oil to be produced in early 2020. This redevelopment phase included four production wells (Well R1, Well R2, Well R3 and Well R4) supported by two injectors in the eastern sector, and two production wells in the western sector (Well R5 and Well R6) supported by one injector. All injectors in the redevelopment plan were to use PWRI (Produced Water Re-Injection), with no further seawater being injected, and the scaling risk would thus be due to carbonate scales only.
Publisher Copyright:
Copyright 2022, Society of Petroleum Engineers
PY - 2022/5/25
Y1 - 2022/5/25
N2 - Scaling risk may be insignificant during the early stages of well life due to delayed seawater breakthrough; however, during the latter stages of production inhibitor chemical application by squeezes may be required to prevent scale deposition (Chen et al., 2013). This raises the question of what behaviour should be expected during the redevelopment of a previously seawater flooded reservoir. Should the planning and design of squeeze treatments in a brown field project be the same or different to a green field development? This paper discusses this issue by reference to a case study in a field located in the Norwegian Sector of the North Sea. The field in question is produced by horizontal wells, and these wells will require scale inhibitor placement via bullhead squeezes deployed at appropriate pump rates to ensure effective placement to provide adequate protection. The timing and extent of seawater breakthrough have been calculated using a reservoir simulation model that accounts for the original development phase, a multi-year period during which the field was shut in - but during which fluid redistribution could still occur - and then the redevelopment phase. These calculations have been used to identify the required timing for squeeze treatments, and to investigate what bullhead pump rates are required for adequate placement during both phases of field life. Two wells are considered during the first production period and six wells are studied during the redevelopment stage. In each case four pump rates are assessed: 2.5, 5, 7.5 and 10 barrels per minute. The main finding is that while adequate placement can be achieved using the same pump rates in both phases of field life, during the redevelopment stage the treatments will need to be deployed earlier in the redeveloped wells life, since there may not be a long time period between (formation) water breakthrough and seawater breakthrough, as there generally is during conventional green field developments. This paper delivers a comprehensive water breakthrough and squeeze placement profile comparison between early and redevelopment stages. It presents an assessment of the scaling risk in different production wells, the timing of the first and later squeeze treatments in each production well, and the ability to mitigate that scaling risk by bullhead squeeze treatments.
AB - Scaling risk may be insignificant during the early stages of well life due to delayed seawater breakthrough; however, during the latter stages of production inhibitor chemical application by squeezes may be required to prevent scale deposition (Chen et al., 2013). This raises the question of what behaviour should be expected during the redevelopment of a previously seawater flooded reservoir. Should the planning and design of squeeze treatments in a brown field project be the same or different to a green field development? This paper discusses this issue by reference to a case study in a field located in the Norwegian Sector of the North Sea. The field in question is produced by horizontal wells, and these wells will require scale inhibitor placement via bullhead squeezes deployed at appropriate pump rates to ensure effective placement to provide adequate protection. The timing and extent of seawater breakthrough have been calculated using a reservoir simulation model that accounts for the original development phase, a multi-year period during which the field was shut in - but during which fluid redistribution could still occur - and then the redevelopment phase. These calculations have been used to identify the required timing for squeeze treatments, and to investigate what bullhead pump rates are required for adequate placement during both phases of field life. Two wells are considered during the first production period and six wells are studied during the redevelopment stage. In each case four pump rates are assessed: 2.5, 5, 7.5 and 10 barrels per minute. The main finding is that while adequate placement can be achieved using the same pump rates in both phases of field life, during the redevelopment stage the treatments will need to be deployed earlier in the redeveloped wells life, since there may not be a long time period between (formation) water breakthrough and seawater breakthrough, as there generally is during conventional green field developments. This paper delivers a comprehensive water breakthrough and squeeze placement profile comparison between early and redevelopment stages. It presents an assessment of the scaling risk in different production wells, the timing of the first and later squeeze treatments in each production well, and the ability to mitigate that scaling risk by bullhead squeeze treatments.
UR - http://www.scopus.com/inward/record.url?scp=85132042711&partnerID=8YFLogxK
U2 - 10.2118/209502-MS
DO - 10.2118/209502-MS
M3 - Conference contribution
AN - SCOPUS:85132042711
BT - SPE International Oilfield Scale Conference and Exhibition 2022
PB - Society of Petroleum Engineers
T2 - 2022 SPE International Oilfield Scale Conference and Exhibition
Y2 - 25 May 2022 through 26 May 2022
ER -