University of Toronto Scarborough, Department of Physical and Environmental Sciences, 1265 Military Trail, Toronto, ON M1C 1A4, Canada.
University of Toronto Scarborough, Department of Physical and Environmental Sciences, 1265 Military Trail, Toronto, ON M1C 1A4, Canada.
Sci Total Environ. 2014 Oct 15;496:678-687. doi: 10.1016/j.scitotenv.2014.06.058. Epub 2014 Jun 30.
Forest harvesting leads to changes in soil moisture, temperature and incident solar radiation, all strong environmental drivers of soil-air mercury (Hg) fluxes. Whether different forest harvesting practices significantly alter Hg fluxes from forest soils is unknown. We conducted a field-scale experiment in a northern Minnesota deciduous forest wherein gaseous Hg emissions from the forest floor were monitored after two forest harvesting prescriptions, a traditional clear-cut and a clearcut followed by biomass harvest, and compared to an un-harvested reference plot. Gaseous Hg emissions were measured in quadruplicate at four different times between March and November 2012 using Teflon dynamic flux chambers. We also applied enriched Hg isotope tracers and separately monitored their emission in triplicate at the same times as ambient measurements. Clearcut followed by biomass harvesting increased ambient Hg emissions the most. While significant intra-site spatial variability was observed, Hg emissions from the biomass harvested plot (180 ± 170 ng m(-2)d(-1)) were significantly greater than both the traditional clearcut plot (-40 ± 60 ng m(-2)d(-1)) and the un-harvested reference plot (-180 ± 115 ng m(-2)d(-1)) during July. This difference was likely a result of enhanced Hg(2+) photoreduction due to canopy removal and less shading from downed woody debris in the biomass harvested plot. Gaseous Hg emissions from more recently deposited Hg, as presumably representative of isotope tracer measurements, were not significantly influenced by harvesting. Most of the Hg tracer applied to the forest floor became sequestered within the ground vegetation and debris, leaf litter, and soil. We observed a dramatic lessening of tracer Hg emissions to near detection levels within 6 months. As post-clearcutting residues are increasingly used as a fuel or fiber resource, our observations suggest that gaseous Hg emissions from forest soils will increase, although it is not yet clear for how long such an effect will persist.
森林采伐导致土壤水分、温度和入射太阳辐射发生变化,所有这些都是土壤-空气汞(Hg)通量的重要环境驱动因素。不同的森林采伐作业是否会显著改变森林土壤的 Hg 通量尚不清楚。我们在明尼苏达州北部的一个落叶林进行了一项野外尺度的实验,其中在两种森林采伐方案(传统皆伐和皆伐后生物质收获)之后,监测了森林地表的气态 Hg 排放,并与未采伐的对照样地进行了比较。使用 Teflon 动态通量室在 2012 年 3 月至 11 月的四个不同时间点重复测量了四次气态 Hg 排放。我们还应用了富集的 Hg 同位素示踪剂,并在与环境测量相同的时间重复测量了三次其排放。皆伐后生物质收获增加了大气 Hg 的排放。虽然观察到显著的场内空间变异性,但生物质收获区的 Hg 排放(180±170ngm(-2)d(-1))显著高于传统皆伐区(-40±60ngm(-2)d(-1))和未采伐对照样地(-180±115ngm(-2)d(-1))。这一差异可能是由于采伐去除了树冠,并减少了生物质收获区倒下的木质残体的遮荫,从而增强了 Hg(2+)的光还原作用。作为同位素示踪剂测量的代表,最近沉积的 Hg 的气态 Hg 排放没有受到采伐的显著影响。施加到林地表层的大部分 Hg 示踪剂被封存于地被植被和碎屑、凋落物和土壤中。我们观察到示踪 Hg 排放在 6 个月内急剧减少至接近检测水平。随着采伐后残留物越来越多地被用作燃料或纤维资源,我们的观察结果表明,森林土壤的气态 Hg 排放将会增加,尽管尚不清楚这种效应会持续多久。