P C Blersch, W van Wyk , R Steenkamp
Construction of the partially completed Calueque Dam on the Cunene River in Angola was abandoned in 1976 due to the hostilities in Angola. In 1988 the dam was bombed, causing significant damage to the bridge deck, other structures and equipment. Work to complete and rehabilitate the dam commenced in late 2012 and included major earthworks, extensive concrete repairs and refurbishment and installation of mechanical equipment, including ten spillway radial gates and two outlet gates with lifting equipment, emergency gates and cranes, including electrical and control systems. A number of challenges were encountered in planning and executing the project but were overcome largely as a result of detailed historical project information having been retained well beyond the norm and through the involvement of a key member of the original project team in the current project.
Keywords: Dam rehabilitation, radial gates, zoned earthfill embankment
The enlargement of the Cotter Dam is being undertaken by ACTEW to provide a greater security of water supply to Canberra. The project involves constructing a larger, higher new dam wall immediately downstream of the existing Cotter Dam, to allow the present dam to continue functioning and supplying water while construction is underway. The project raised a number of environmental issues partly because the Cotter Dam currently supports a self-sustaining population of (endangered) Macquarie Perch, and because the Bendora Dam, upstream of Cotter Dam, contains a breeding population of (endangered) Trout Cod. Bendora Dam will not be physically affected by the works on Cotter Dam, but its operations may be altered. An ecological risk analysis was conducted to identify critical environmental risks that would need to be investigated and managed or ameliorated and management strategies were put in place to reduce risks. ACTEW have adopted an adaptive management approach to the project, but in order to implement that approach it is necessary to conduct effective monitoring of the fish populations of concern. These potentially include the two endangered species, as well as potential predators (such as cormorants) and competitors (such as trout). Power analysis has been used as a tool to evaluate whether it is feasible to monitor key populations sufficiently rigorously to be able to confidently detect a change (either an increase or decrease in a population). For Macquarie Perch and trout it should be possible to detect population changes statistically with a logistically feasible monitoring program.
2011 – Using risk analysis, power analysis and adaptive management to minimise ecological impacts of the Cotter Dam enlargement
Bruce Brown, Mark Coghill
Tailings management practices have evolved significantly over the last 30 to 40 years with emphasis on long term geotechnical and geochemical stability to meet community expectations and company liabilities. The main drivers have been environmental protection both during operations and post closure, public safety and water conservation. Mining companies have become aware of the significant risks resulting from the operation of tailings facilities with a number of high profile failures occurring in recent times. The common practice of building a containment structure and depositing tailings as unthickened slurry is being challenged and tested against alternative tailings treatment technologies. These include high rate thickening, paste thickening and filtration. The potential benefits of these technologies include significant reduction in process water losses, reduced design duties for the confinement structures and improved conditions for closure. Notwithstanding these potential benefits, very few facilities have implemented the new technologies due to economic constraints imposed by the evaluation methods used by the mining industry. This paper summarises the available tailings treatment technologies and the resulting implications for tailings facility design. It reviews the benefits and critiques the economic evaluation method currently in use and recommends that the industry changes its evaluation methodology to drive future trends.
Tailings Storage, Current and Future Trends
Rob Campbell, Tom Kolbe, Ron Fleming, Christopher Dann
Hinze Dam is an Extreme hazard category water supply dam situated in the Queensland Gold Coast hinterland, owned and operated by Seqwater (formerly owned by Gold Coast City Council). The Hinze Dam Stage 3 works involved raising the previously 65m high central core earth and rockfill embankment approximately 15m to a maximum height of approximately 80m.
The Stage 3 works included a program of foundation curtain grouting, consisting of six discrete grout panels, five of those beneath areas where the embankment was extended and one beneath part of the spillway enhancement works. Five of the six grout panels were essentially single row panels, with one or more partial rows added in specific areas of high grout take. The remaining grout panel (Panel 4) was constructed as a triple row panel.
A number of challenges were encountered and overcome during the Stage 3 foundation grouting works due to highly variable foundation conditions, ranging from extremely low strength residual soil to highly fractured and permeable high strength rock.
The grouting works were undertaken using downstage grouting techniques, with manual recording of data, manual control of grout pressures and injection rates and use of predominantly neat cement grout mixes.
A key issue in the execution of the foundation grouting works was the maximum grout pressures applied to the foundation and this was discussed in detail between the project design team and external review panel. This paper presents the results from project specific grout trials and production grouting to demonstrate that closure of the foundation was consistently achieved (with one exception discussed herein), which supports the grouting approach employed and the adopted grout pressures.
This paper presents a case study description of the Stage 3 foundation curtain grouting works, including a summary of key learnings which may be of benefit to future dam foundation curtain grouting projects.
Conrad Ginther, Colleen Stratford
The Wyaralong Dam Alliance (WDA), a consortium of seven engineering and contracting companies, was contracted to design and construct the Wyaralong Dam, which impounds the Teviot Brook 14 km from Beaudesert in Queensland, Australia. The dam is an approximately 500 metre long, 48 metre high Roller Compacted Concrete (RCC) structure built on a foundation generally consisting of massive sandstone with intermittent conglomerate zones consisting of cemented gravels, mudclasts and sands. Geologic features of note with regard to dam stability and long term seepage at the site are dominated by downstream sloping bedding features and conglomerate zones. In addition to the bedding-related features, two predominant vertical to subvertical fracture sets exist. The condition of the vertical fractures ranges from tight and fresh at depth to highly weathered and filled with dispersive clay and gravels near the foundation surface. To provide a durable and effective long term seepage barrier for the dam, an extensive foundation cleaning and treatment operation was undertaken. This comprised drilling, blasting, and excavation of the majority of the highly weathered rock and dispersive materials supplemented by localized installation of small cut-offs and dental concrete and the construction of a double-line grout curtain installed using real time computer monitoring, the GIN methodology, and balanced, stable grout mixes.
Foundation Preparation and Seepage Barrier Installation at Wyaralong Dam Construction Project