Study and Treatment on Carbonate/Bicarbonate Pollution in Shale Gas Wells in Sichuan
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摘要: 四川页岩气井随着施工区块由威202向威204区块转移,水基钻井液在二开普遍出现了CO32−和HCO3−污染问题。污染发生地层主要为长兴组、龙潭组、茅口组,表现为黏度和切力快速上升且难以控制。针对这一问题,首先对污染来源进行了探讨,分析认为CO2侵入长兴组、龙潭组地层钻井用钻井液,部分井浆中含有大量HCO3−(大于10 000 mg/L)。对预防措施和2种处理方案进行了讨论,提出用CaCl2处理更适合该区块钻井液。最后对威204H23-5井和黄206井钻井液CO2污染的处理工艺进行探索。2口井在采用CaO处理不理想情况下,改用CaCl2方案处理。威204H23-5井钻井液中HCO3−含量由15 420 mg/L降低至1120 mg/L,黏度大于300 s降低至污染前状态的54 s;黄206井钻井液受污染后黏度为180 s,处理后黏度降至污染前状态的57 s。该方法具有高效、经济、针对性强等优点,但应落实好技术措施,避免钻井液受Ca2+和HCO3−双重污染。Abstract: Shale gas drilling in Sichuan basin is moving from the block Wei-202 to block Wei-204, where the water based drilling fluids used in the second interval were generally contaminated with CO32- and HCO3-. The source of the contamination is the Changxing, Longtan and Maokou formations. Contamination of the drilling fluids resulted in fast increase in viscosity and gel strengths, and it was difficult to bring under control the increase in viscosity and gel strengths. To deal with this problem, the source of CO32- and HCO3- was first analyzed. It was believed that CO2 invasion took place in drilling the Changxing and Longtan formations, and some mud materials contain high concentration of HCO3- (>10,000 mg/L). Measures have been taken to prevent the contamination from mud materials. Using pH meter, the concentrations of CO32- and HCO3- can be accurately measured. Preventing measures and two treatment methods (CaO and CaCl2) were discussed, and it was concluded that CaCl2 is the best additive to deal with the contamination. Previously CaO had been used to treat out the CO2 contamination on well Wei-204H23-5 and well Huang-206, but the results were not satisfactory. After using CaCl2 to treat out the CO2 contamination, the concentration of HCO3- was reduced from 15,420 mg/L to 1120 mg/L, and the viscosity of the mud was reduced from above 300 sec to 54 sec, which was the viscosity of the mud before HCO3- contamination. The viscosity of the mud in well Huang-206 was 180 sec after HCO3- contamination, and was reduced to 57 sec, as that before the contamination. This method of eliminating CO2 contamination has the advantages of is high efficiency, cost-effective and strong pertinence. Keep in mind that the technical measures should be well prepared to avoid contamination of the mud by both Ca2+ and HCO3-.n recent years, with the transfer of the construction block from Wei202 to Wei204, the pollution problem of carbonate/bicarbonate in the water base drilling fluid was widely encountered. The pollution occurred mainly in Changxing, Longtan and Maokou, and the viscosity/shear increased rapidly and was difficult to control. In view of this problem, the sources of pollution were firstly discussed, and the analysis showed that CO2 intrusion and coal interlayer in Changxing and Longtan were important pollution sources of carbonate/bicarbonate. Some materials contained a large amount of bicarbonate (>10 000 mg/L), and measures had been taken at present. The accurate test of carbonate/bicarbonate can be achieved by using a pH meter. Secondly, preventive measures and two treatment schemes are discussed, and it is suggested that CaCl2 treatment is more suitable for this block.Finally, the CO2 pollution treatment technology of Wei 204H23-5 and Huang 206 was explored. Two wells were treated with the CaCl2 solution when the CaO treatment was not ideal. HCO3− in Wei 204H23-5 decreased from 15,420 mg/L to 1120 mg/L, FV >300 s decreased to 54 s as pre-pollution state. After the pollution, the FV of Huang 206 well was up to 180 s, and after the treatment, the FV was reduced to 57 s as pre-pollution state. This method has the advantages of high efficiency, economy and strong pertinence, but technical measures should be implemented to avoid the double contamination of drilling fluid by Ca2+ and HCO3−.
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Key words:
- Water based drilling fluid /
- Shale gas /
- Carbonate /
- Biocarbonate
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表 1 威204区块H21、23前期施工井钻井液的性能
井
号井深/
mρ/
g·cm−3FV/
sFLAPI/
mLFLHTHP/
mLφ6/φ3 膨润土/
g·L−1CO32−/
mg·L−1HCO3−/
mg·L−1层位 23-8 2300 1.60 48 4.2 14.0 3/2 22.0 飞仙关 2741 2.06 57 5.2 16.5 8/9 21.0 2520 3340 龙潭 2835 2.01 98 6.8 21.1 39/37 21.0 3760 11 340 龙潭 23-6 2244 1.58 51 3.8 11.0 4/3 19.0 飞仙关 2915 1.79 82 4.8 16.8 18/19 19.5 4380 5734 茅口 3148 2.00 93 5.4 19.2 29/27 19.0 3910 8920 龙马溪 21-2 2600 1.70 62 4.6 13.0 3/4 21.0 飞仙关 2813 1.84 93 5.0 18.5 10/12 20.0 880 3780 龙潭 3092 1.85 81 4.0 20.0 22/20 19.0 2560 9394 茅口 表 2 威204H14-X井钻井液受地层煤/地层水中CO32−和HCO3−污染后的基本性能
井深/
mρ/
g·cm−3FV/
sφ6/φ3 Gel/
Pa/PaCa2+/
mg·L−1OH−/
mg·L−1CO32−/
mg·L−1HCO3−/
mg·L−1层位 CaO/
kg2665 1.73 50 3/2 2.5/4.5 1400 540 25 0 飞仙关 0 2740 1.80 65 9/8 2.5/16.0 0 0 1150 3140 长兴 300 2780 1.81 71 12/10 5.0/22.5 800 0 300 3355 龙潭 150 2824 1.85 75 13/12 5.0/24.0 600 0 260 3416 茅口 0 表 3 主要材料水溶液滤液中CO32−/HCO3−的检测
材料 OH−/(mg·L−1) CO32−/(mg·L−1) HCO3−/(mg·L−1) A 0 1272 1171 B 0 0 7930 C 0 1200 10 980 注:采用高速搅拌20 min配制5%水溶液,C在高速搅拌后起泡严重,膨胀体积约为150%~200% 表 4 威204H23-5井受CO2污染处理前后钻井液的基本性能
时间点 ρ/
g·cm−3FV/
sφ600 φ300 φ6 φ3 PV/
mPa·sYP/
PaGel/
Pa/PaCa2+/
mg·L−1CaCl2/
t受污染前 1.88 54 118 73 7 5 45 14.0 3.0/12 350 0 第1次污染处理前 1.85 150 217 162 46 46 55 53.5 0 0 第2次污染处理前 1.85 >300 0 0 处理1个循环周 1.90 95 156 103 21 19 53 25.0 7.5/38 0 1.0 处理2个循环周 1.93 75 142 90 10 9 52 19.0 5.0/21 0 2.0 48 h 1.95 54 124 76 8 6 48 14.0 3.5/16 600 3.5 -
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