Instituto de Ciencias Marinas de Andalucía (CSIC), Campus Universitario Rio San Pedro, s/n 11519 Puerto Real, Cádiz, Spain.
Environ Sci Technol. 2013 Jul 2;47(13):7483-9. doi: 10.1021/es4009272. Epub 2013 Jun 21.
The pool of bioavailable metals in sediments is typically much smaller than the total metal concentration and is strongly influenced by metal-binding with acid-volatile sulfide (AVS), particulate organic carbon (OC), and iron and manganese oxide solid phases. We have investigated how the properties of relatively oxidized sediments influence the exposure and effects of copper on the survival and growth rate of the deposit-feeding benthic bivalve Tellina deltoidalis. Growth rate was a much more sensitive end point than survival. Toxic effects to growth were consistently observed in sediment where both pore water and overlying water copper concentrations were below the effect threshold for dissolved copper. Decreases in growth of the bivalve were largely attributable to dietary exposure to sediment-bound copper, as the organism was observed to actively feed on fine materials from the sediment surface. For sediments with the same total copper concentrations, effects were less for sediments with greater concentrations of fine particles (<63 μm sediment) or particulate organic carbon (OC). Based on the concentration-response relationship, a no-effect value of 5.5 mg <63 μm Cu g(-1) OC for growth of T. deltoidalis was calculated. The results confirm the appropriateness of using OC-normalized copper concentration in the <63 μm sediment fraction to develop sediment quality guidelines (SQGs) that vary with sediment properties. For sediments where the amount of AVS is not sufficient to bind metals in non bioavailable forms, the metal-binding capacity provided by OC and iron and manganese oxyhydroxides associated with the fine sediments considerably reduced metal bioavailability. These sediment properties should be considered when assessing the risks posed by metal-contaminated sediments.
沉积物中生物可利用金属的总量通常远小于总金属浓度,并强烈受到与酸挥发性硫(AVS)、颗粒有机碳(OC)以及铁和锰氧化物固相结合的金属的影响。我们研究了相对氧化沉积物的特性如何影响铜对滤食性底栖双壳贝类厚壳贻贝生存和生长速率的暴露和影响。生长速率是比存活率更敏感的终点。在孔隙水和上覆水铜浓度均低于溶解铜效应阈值的沉积物中,始终观察到对生长的毒性作用。双壳类动物的生长减少主要归因于对沉积物结合铜的饮食暴露,因为观察到该生物积极摄食来自沉积物表面的细物质。对于具有相同总铜浓度的沉积物,对于具有较高细颗粒(<63μm 沉积物)或颗粒有机碳(OC)浓度的沉积物,其影响较小。基于浓度-反应关系,计算出 T. deltoidalis 生长的无效应值为 5.5mg<63μmCu g(-1)OC。结果证实了使用 OC 归一化的 <63μm 沉积物部分中的铜浓度来制定随沉积物特性变化的沉积物质量指南(SQGs)是合适的。对于 AVS 量不足以将金属结合成非生物可利用形式的沉积物,与细沉积物相关的 OC 和铁锰氢氧化物提供的金属结合能力大大降低了金属的生物可利用性。在评估受金属污染沉积物带来的风险时,应考虑这些沉积物特性。