Université de Bordeaux, UMR 5805 EPOC-TGM, av. des Facultés, 33405 Talence Cedex, France.
Sci Total Environ. 2011 Mar 15;409(8):1539-49. doi: 10.1016/j.scitotenv.2011.01.022.
This study reports on the relationship between copper (Cu) behavior and organic matter (OM) transformation along the turbidity gradient in the freshwater reaches of the Gironde Estuary. During a one-year survey, surface water and suspended particulate matter (SPM) were sampled at least monthly at three sites along the Garonne Branch, representing the main fluvial branch of the Gironde Estuary. Additionally, a longitudinal high resolution profile was sampled along the Garonne Branch, covering the turbidity gradient from the river water endmember to the maximum turbidity zone (MTZ). Seasonal variability and spatial distribution of Cu in both the dissolved phases (<0.2 μm, Cu(0.2) and <0.02 μm, Cu(0.02)) and particulate Cu (Cu(P)) clearly suggested Cu(0.2) addition during summer, that increased the Cu(0.2) concentrations by a factor ~2, mainly manifested by an increase in the Cu(0.02) fraction. At the annual timescale (2004), this internal Cu reactivity increased Cu(0.02) fluxes in the Garonne Branch by ~20% (3.6 t year(-1)), with the equivalent of ~2.9 t year(-1) derived from the Cu(P) fraction and ~0.7 t year(-1) from the colloidal (0.02-0.2 μm) fraction, without involving and/or affecting the Cu(C18) (hydrophobic metal-organic complexes) fraction. Combining data on Cu speciation with the results obtained by several independent techniques (DOC and POC measurements, 3D-fluorescence, and TEM) suggested close relationships between Cu behavior and OM transformation/restructuration along the turbidity gradient in the Garonne Branch. The observed Cu(0.02) addition was related to increasing humification (humification index HIX increased from 9 to 12, network formation) and labile OM degradation (Iγ/Iα ratio decreased from 0.70 to 0.44), going along with decreasing DOC and POC concentrations. Mass-balances suggest that in the studied system, degradation of OM may account for the release of ~25 μmol potentially bioaccessible Cu(0.02) per mole of particulate organic carbon mineralized.
本研究报告了在吉伦特河口淡水段浊度梯度范围内铜(Cu)行为与有机物(OM)转化之间的关系。在为期一年的调查中,至少每月在吉伦特河口加龙河支流的三个地点采集地表水和悬浮颗粒物(SPM)。此外,还在加龙河支流沿线采集了一个纵向高分辨率剖面,涵盖了从河水端元到最大浊度区(MTZ)的浊度梯度。Cu 在溶解相(<0.2 μm,Cu(0.2) 和 <0.02 μm,Cu(0.02)) 和颗粒 Cu (Cu(P)) 中的季节性变化和空间分布清楚地表明,Cu(0.2) 在夏季添加,这使 Cu(0.2) 浓度增加了约 2 倍,主要表现为 Cu(0.02) 分数增加。在年度时间尺度(2004 年),这种内部 Cu 反应性使加龙河支流的 Cu(0.02)通量增加了约 20%(3.6 t 年(-1)),其中相当于 2.9 t 年(-1)来自 Cu(P) 部分和 0.7 t 年(-1)来自胶体(0.02-0.2 μm)部分,而不涉及和/或影响 Cu(C18)(疏水性金属-有机配合物)部分。将 Cu 形态与几种独立技术(DOC 和 POC 测量、3D-荧光和 TEM)获得的结果结合起来表明,在加龙河支流的浊度梯度范围内,Cu 行为与 OM 转化/重构之间存在密切关系。观察到的 Cu(0.02) 添加与腐殖化的增加(腐殖化指数 HIX 从 9 增加到 12,网络形成)和易降解 OM 的降解(Iγ/Iα 比值从 0.70 降低到 0.44)有关,同时伴随着 DOC 和 POC 浓度的降低。质量平衡表明,在所研究的系统中,OM 的降解可能导致每摩尔颗粒有机碳矿化释放约 25 μmol 潜在生物可利用的 Cu(0.02)。