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利用镧改性膨润土(Phoslock(®))处理的 18 个湖泊的水质和水生大型植物响应的荟萃分析。

A meta-analysis of water quality and aquatic macrophyte responses in 18 lakes treated with lanthanum modified bentonite (Phoslock(®)).

机构信息

Centre for Ecology & Hydrology, Penicuik, Midlothian, EH26 0QB, UK.

Centre for Ecology & Hydrology, Lancaster Environment Centre, Library Avenue, Bailrigg, Lancaster, LA1 4AP, UK.

出版信息

Water Res. 2016 Jun 15;97:111-21. doi: 10.1016/j.watres.2015.08.020. Epub 2015 Aug 13.

Abstract

Lanthanum (La) modified bentonite is being increasingly used as a geo-engineering tool for the control of phosphorus (P) release from lake bed sediments to overlying waters. However, little is known about its effectiveness in controlling P across a wide range of lake conditions or of its potential to promote rapid ecological recovery. We combined data from 18 treated lakes to examine the lake population responses in the 24 months following La-bentonite application (range of La-bentonite loads: 1.4-6.7 tonnes ha(-1)) in concentrations of surface water total phosphorus (TP; data available from 15 lakes), soluble reactive phosphorus (SRP; 14 lakes), and chlorophyll a (15 lakes), and in Secchi disk depths (15 lakes), aquatic macrophyte species numbers (6 lakes) and aquatic macrophyte maximum colonisation depths (4 lakes) across the treated lakes. Data availability varied across the lakes and variables, and in general monitoring was more frequent closer to the application dates. Median annual TP concentrations decreased significantly across the lakes, following the La-bentonite applications (from 0.08 mg L(-1) in the 24 months pre-application to 0.03 mg L(-1) in the 24 months post-application), particularly in autumn (0.08 mg L(-1) to 0.03 mg L(-1)) and winter (0.08 mg L(-1) to 0.02 mg L(-1)). Significant decreases in SRP concentrations over annual (0.019 mg L(-1) to 0.005 mg L(-1)), summer (0.018 mg L(-1) to 0.004 mg L(-1)), autumn (0.019 mg L(-1) to 0.005 mg L(-1)) and winter (0.033 mg L(-1) to 0.005 mg L(-1)) periods were also reported. P concentrations following La-bentonite application varied across the lakes and were correlated positively with dissolved organic carbon concentrations. Relatively weak, but significant responses were reported for summer chlorophyll a concentrations and Secchi disk depths following La-bentonite applications, the 75th percentile values decreasing from 119 μg L(-1) to 74 μg L(-1) and increasing from 398 cm to 506 cm, respectively. Aquatic macrophyte species numbers and maximum colonisation depths increased following La-bentonite application from a median of 5.5 species to 7.0 species and a median of 1.8 m to 2.5 m, respectively. The aquatic macrophyte responses varied significantly between lakes. La-bentonite application resulted in a general improvement in water quality leading to an improvement in the aquatic macrophyte community within 24 months. However, because, the responses were highly site-specific, we stress the need for comprehensive pre- and post-application assessments of processes driving ecological structure and function in candidate lakes to inform future use of this and similar products.

摘要

镧(La)改性膨润土作为一种地球工程工具,越来越多地用于控制湖底沉积物中磷(P)向覆盖水的释放。然而,人们对其在广泛的湖泊条件下控制 P 的有效性或促进快速生态恢复的潜力知之甚少。我们结合了来自 18 个处理过的湖泊的数据,研究了 La-膨润土处理后 24 个月内湖泊种群的响应(La-膨润土负荷范围:1.4-6.7 吨/公顷),包括地表水总磷(TP;来自 15 个湖泊的数据)、可溶性反应磷(SRP;14 个湖泊)、叶绿素 a(15 个湖泊)和透明度(15 个湖泊),以及水生大型植物物种数量(6 个湖泊)和水生大型植物最大定植深度(4 个湖泊)。湖泊之间的数据可用性和变量各不相同,一般来说,监测在接近应用日期时更为频繁。La-膨润土处理后,湖泊中的年平均 TP 浓度显著下降(从应用前 24 个月的 0.08mg/L 降至应用后 24 个月的 0.03mg/L),特别是在秋季(0.08mg/L 至 0.03mg/L)和冬季(0.08mg/L 至 0.02mg/L)。SRP 浓度的年平均(0.019mg/L 至 0.005mg/L)、夏季(0.018mg/L 至 0.004mg/L)、秋季(0.019mg/L 至 0.005mg/L)和冬季(0.033mg/L 至 0.005mg/L)也有显著下降。La-膨润土处理后,湖泊之间的 P 浓度差异很大,与溶解有机碳浓度呈正相关。La-膨润土处理后,夏季叶绿素 a 浓度和透明度的响应相对较弱,但仍具有统计学意义,第 75 百分位数值分别从 119μg/L 降至 74μg/L 和从 398cm 增至 506cm。水生大型植物物种数量和最大定植深度分别从 5.5 种增加到 7.0 种和 1.8m 增加到 2.5m。水生大型植物的反应在湖泊之间差异显著。La-膨润土处理后,水生大型植物群落的水质普遍改善,水生大型植物的数量和最大定植深度分别增加了 7 种和 2.5m。然而,由于响应具有高度的特定地点特征,我们强调需要在候选湖泊中对驱动生态结构和功能的过程进行全面的应用前和应用后评估,以告知未来对这种和类似产品的使用。

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