Aqua Lux Lucis, Inc., 8411 NW 55th Place, Gainesville, FL USA.
Sci Total Environ. 2014 Nov 15;499:62-73. doi: 10.1016/j.scitotenv.2014.08.036. Epub 2014 Aug 29.
Structural equation modeling (SEM) provides a framework that can more properly handle complex variable interactions inherent in mercury cycling and its bioaccumulation compared to more traditional regression-based methods. SEM was applied to regional data sets for three different types of aquatic ecosystems within Florida, USA--lakes, streams, and the Everglades--to evaluate the underlying nature (i.e., indirect and direct) of the relationships between fish mercury concentrations and trophic state related variables such as nutrients, dissolved organic carbon (DOC), sulfate, and alkalinity. The modeling results indicated some differences in key variable relationships--for example, the effect of nutrients on fish mercury in lakes and streams was uniformly negative through direct and indirect pathways consistent with biodilution or eutrophication-associated effects on food web structure. Somewhat surprisingly, however, was that total phosphorus did not serve as a meaningful variable in the Everglades model, apparently because its effects were masked or secondary to the effects of DOC. What is perhaps a more important result were two key similarities across the three systems. First, the modeling clearly indicates that the dominant influence on fish tissue mercury concentrations in all three systems is related to variations in the methylmercury signal. Second, the modeling demonstrated that the effect of DOC on fish mercury concentrations was exerted through multiple and antagonistic pathways, including facilitated transport of total mercury and methylmercury, enhanced rates of methylation, and limitations imposed on bioavailability. Indeed, while the individual DOC pathways in the models were all highly significant (generally p<0.001), the net effect of DOC in each model was greatly reduced or insignificant. These results can help explain contradictory results obtained previously by other researchers in other systems, and illustrate the importance of SEM as a modeling tool when studying systems with complex interactions such as the aquatic mercury cycle.
结构方程模型(SEM)提供了一个框架,可以比传统的基于回归的方法更恰当地处理汞循环及其生物累积中固有的复杂变量相互作用。SEM 被应用于美国佛罗里达州三种不同类型的水生生态系统的区域数据集——湖泊、溪流和大沼泽地——以评估鱼类汞浓度与营养物、溶解有机碳(DOC)、硫酸盐和碱度等与营养状态相关的变量之间的关系的潜在性质(即间接和直接)。建模结果表明,关键变量关系存在一些差异——例如,营养物质对湖泊和溪流中鱼类汞的影响通过直接和间接途径都是一致的负面,这与食物网结构的生物稀释或富营养化相关效应一致。然而,有些出乎意料的是,总磷在大沼泽地模型中并不是一个有意义的变量,显然是因为它的作用被 DOC 的作用所掩盖或次要。也许更重要的结果是三个系统中有两个关键的相似之处。首先,模型清楚地表明,对所有三个系统中鱼类组织汞浓度的主要影响与甲基汞信号的变化有关。其次,模型表明,DOC 对鱼类汞浓度的影响是通过多种拮抗途径发挥的,包括总汞和甲基汞的易位运输、甲基化速率的提高以及生物利用度的限制。事实上,虽然模型中的单个 DOC 途径都非常显著(通常 p<0.001),但每个模型中 DOC 的净效应大大降低或不显著。这些结果可以帮助解释其他研究人员在其他系统中得到的矛盾结果,并说明了 SEM 作为一种建模工具在研究具有复杂相互作用的系统(如水生汞循环)时的重要性。