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CONCRETE DURABILITY IN TEMPERATE MARINE EXPOSURES: 17 AND 20-YEAR FIELD TRIALS OF BINDERS

机译:温带海洋暴露的混凝土耐用性:17和20年的粘合剂试验

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In 1982, a set of 24 reinforced concrete test beams were suspended in a temperate marine atmospheric/splash zone exposure beneath Berth 8 at the Port of Fremantle inner harbour. Three years later, in 1985, a further 68 beams were placed in a tidal marine exposure adjacent to a nearby slipway at the mouth of the Swan River. The concretes used in the exposure trials were based on local general purpose Portland (AS 1315 Type A, now typically AS 3972 Type GP) cement, along with various combinations of silica fume, iron blast furnace slag and fly ash. The effect of including a proprietary integral waterproofing admixture with the Type A and 65 percent slag blended cements was also assessed. During 2001 and 2002 the test beams beneath Berth 8 were recovered and subjected to resistivity, half-cell potential and LPR corrosion rate measurements. Samples of concrete were removed for determination of chloride penetration coefficients. The data was compared with results previously obtained at two and five years exposure. The tidal exposure beams have been left in-situ, however the beams at the upper and lower extents of the tidal range were tested and sampled in the same manner as the Berth 8 beams. Chloride ingress results were compared with data obtained at early age from duplicate specimens after one year of laboratory exposure in a wet/dry cycle salt-spray tank. From the results obtained so far, it has been concluded that: The "reference" concrete, well cured Type A cement at 400 kg/m~3 and w/cm ratio 0.4, did not provide adequate long-term corrosion protection to reinforcement under the exposure conditions. Supplementary cementitious materials (SCM's) increased protection to reinforcement. The effect was greatest for silica fume, followed by blast furnace slag and then fly ash. The hydrophobic admixture increased resistivity and reduced surface chloride concentrations. SCM's increased the surface chloride concentrations, but reduced the rate of chloride penetration. This paper presents and discusses the above data, and briefly outlines an ongoing program of further work utilising the test beams.
机译:1982年,在FrEmantle Inner Harbor港口的温带船舶80个温带海洋大气/飞溅区暴露中悬挂了一组24个钢筋混凝土测试梁。三年后,1985年,将另外68个梁放置在天鹅河口的附近滑道附近的潮汐海洋曝光中。在曝光试验中使用的混凝土基于局部通用波特兰(AS 1315 A型,现在通常为3972型GP)水泥,以及二氧化硅烟雾,铁高炉炉渣和粉煤灰的各种组合。还评估了包括A和65%炉渣混合水泥的专有整体防水混合物的效果。在2001和2002期间,泊位8下面的测试梁被回收并进行电阻率,半电池潜力和LPR腐蚀速率测量。除去混凝土样品以测定氯化物渗透系数。将数据与先前在两年和五年的曝光中获得的结果进行比较。潮汐曝光梁已经留在原位,然而,以与泊位8梁相同的方式测试潮汐范围的上部和下部范围的光束。将氯化物入口结果与在湿/干循环盐雾罐中的实验室暴露一年后从重复标本获得的数据获得的数据进行比较。从迄今获得的结果,已经得出以下结论:“参考”混凝土,以及固化在类型A水泥400公斤/米〜3且w /厘米比0.4,没有提供下足够长期的腐蚀防护加固暴露条件。补充水泥材料(SCM)增加了对加固的保护。硅胶烟雾的效果最大,其次是高炉炉渣然后飞灰。疏水混合物增加电阻率和降低的表面氯化物浓度。 SCM增加了表面氯化物浓度,但降低了氯化物渗透率。本文提出并讨论了上述数据,并简要概述了利用测试梁的进一步工作的持续计划。

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