Wastewater Treatment Laboratory, Water Research and Technologies Centre, Route touristique de Soliman, Soliman, Tunisia.
Water Sci Technol. 2013;67(4):764-71. doi: 10.2166/wst.2012.630.
The 'Cap Bon' peninsula in Tunisia suffers from intensive tourist activities, high demographic increase and industrial development. As groundwater had been for a long time the main water source, aquifers had been subject to a severe depletion and seawater intrusion. Despite the measures taken prohibiting new drillings and water carrying by the construction of a waterway linking the region to the north-west region of Tunisia, the problem of water shortage persists. Artificial recharge of groundwater with treated wastewater has been decided as a technique to replenish the region aquifers. A pilot plant was constructed in the early 1980s in Souhil Wadi (Nabeul) area. Many experiments have been carried out on this plant and have led to controversial opinions about its performance and its impact on groundwater contamination. This contribution concerns the application of the procedure that we developed from the generalization and the formalization of the United States Environmental Protection Agency (US EPA) methodology for the design of treated wastewater aquifer recharge basins. This upgrading procedure implemented in a spreadsheet, has been used to retrofit the Souhil Wadi facility in order to improve its performance. This method highlighted the importance of the safety factor to estimate wastewater infiltration rate from clean water permeability measurements. It has, also, demonstrated the discordance between the initial design parameters of Souhil Wadi facility and their current status as they have changed with time and the infiltration capacity of the basins has been affected by clogging. Indeed, it has been demonstrated that with the current state of clogging of the basins, the design infiltration rate limited by the most restrictive layer (6.1 cm/hr) corresponds to 22% of the surface infiltration rate reached after a drying period of 10 d, which means that we need more basins to absorb the daily loading rate. The design method leads to the construct ion of five basins of 961 m(2) (31 × 31 m) each, with one basin being flooded for 3 d with 27 cm of water daily and rested for 10 d. The current status is completely different as only four basins are constructed with 324 m(2) each. Many actions in the short, medium and long term have been advised in order to improve the system performance.
突尼斯的“邦角”半岛遭受着密集的旅游活动、人口增长和工业发展的影响。由于地下水长期以来一直是主要水源,含水层已经受到严重的枯竭和海水入侵。尽管已经采取了禁止新钻探和通过修建一条将该地区与突尼斯西北部连接起来的水道来输送水的措施,但水资源短缺的问题仍然存在。人工回灌地下水处理后的废水已被确定为补充该地区含水层的技术。一个试点工厂于 20 世纪 80 年代初在苏希尔瓦迪(纳布勒)地区建成。该工厂进行了许多实验,这些实验导致了对其性能及其对地下水污染影响的争议性意见。本研究涉及应用我们从美国环境保护署(EPA)设计处理后废水回灌含水层盆地方法的概括和形式化中开发的程序。这个升级程序在电子表格中实现,已用于改造苏希尔瓦迪设施,以提高其性能。这种方法强调了安全系数的重要性,以便从清洁水渗透率测量中估计废水渗透率。它还表明了苏希尔瓦迪设施的初始设计参数与其当前状态之间的不匹配,因为随着时间的推移,它们已经发生了变化,并且盆地的渗透能力受到堵塞的影响。事实上,已经证明,由于盆地的当前堵塞状态,由最限制性层(6.1 厘米/小时)限制的设计渗透率仅对应于在 10 天干燥期后达到的表面渗透率的 22%,这意味着我们需要更多的盆地来吸收日负荷。设计方法导致建造五个 961 m(2)(31 × 31 m)的盆地,每个盆地每天用 27 厘米的水淹没 3 天,然后休息 10 天。目前的情况完全不同,因为只有四个盆地,每个盆地 324 m(2)。为了提高系统性能,建议在短期、中期和长期内采取许多行动。