Houser Jeffrey N, Mulholland Patrick J, Maloney Kelly O
Oak Ridge National Laboratory, Bethel Valley Road, P.O. Box 2008, Oak Ridge, TN 37831-6036, USA.
J Environ Qual. 2006 Jan 5;35(1):352-65. doi: 10.2134/jeq2005.0102. Print 2006 Jan-Feb.
Because catchment characteristics determine sediment and nutrient inputs to streams, upland disturbance can affect stream chemistry. Catchments at the Fort Benning Military Installation (near Columbus, Georgia) experience a range of upland disturbance intensities due to spatial variability in the intensity of military training. We used this disturbance gradient to investigate the effects of upland soil and vegetation disturbance on stream chemistry. During baseflow, mean total suspended sediment (TSS) concentration and mean inorganic suspended sediment (ISS) concentration increased with catchment disturbance intensity (TSS: R2= 0.7, p = 0.005, range = 4.0-10.1 mg L(-1); ISS: R2= 0.71, p = 0.004, range = 2.04-7.3 mg L(-1)); dissolved organic carbon (DOC) concentration (R2= 0.79, p = 0.001, range = 1.5-4.1 mg L(-1)) and soluble reactive phosphorus (SRP) concentration (R2= 0.75, p = 0.008, range = 1.9-6.2 microg L(-1)) decreased with increasing disturbance intensity; and ammonia (NH4+), nitrate (NO3-), and dissolved inorganic nitrogen (DIN) concentrations were unrelated to disturbance intensity. The increase in TSS and ISS during storms was positively correlated with disturbance (R2= 0.78 and 0.78, p = 0.01 and 0.01, respectively); mean maximum change in SRP during storms increased with disturbance (r = 0.7, p = 0.04); and mean maximum change in NO3- during storms was marginally correlated with disturbance (r = 0.58, p = 0.06). Soil characteristics were significant predictors of baseflow DOC, SRP, and Ca2+, but were not correlated with suspended sediment fractions, any nitrogen species, or pH. Despite the largely intact riparian zones of these headwater streams, upland soil and vegetation disturbances had clear effects on stream chemistry during baseflow and stormflow conditions.
由于集水区特征决定了河流中的沉积物和养分输入,高地干扰会影响河流水化学。本宁堡军事基地(位于佐治亚州哥伦布市附近)的集水区因军事训练强度的空间变异性而经历了一系列高地干扰强度。我们利用这一干扰梯度来研究高地土壤和植被干扰对河流水化学的影响。在基流期间,平均总悬浮沉积物(TSS)浓度和平均无机悬浮沉积物(ISS)浓度随集水区干扰强度的增加而增加(TSS:R2 = 0.7,p = 0.005,范围 = 4.0 - 10.1 mg L(-1);ISS:R2 = 0.71,p = 0.004,范围 = 2.04 - 7.3 mg L(-1));溶解有机碳(DOC)浓度(R2 = 0.79,p = 0.001,范围 = 1.5 - 4.1 mg L(-1))和可溶性活性磷(SRP)浓度(R2 = 0.75,p = 0.008,范围 = 1.9 - 6.2 μg L(-1))随干扰强度的增加而降低;氨(NH4+)、硝酸盐(NO3-)和溶解无机氮(DIN)浓度与干扰强度无关。风暴期间TSS和ISS的增加与干扰呈正相关(R2分别为0.78和0.78,p分别为0.01和0.01);风暴期间SRP的平均最大变化量随干扰增加(r = 0.7,p = 0.04);风暴期间NO3-的平均最大变化量与干扰有微弱相关性(r = 0.58,p = 0.06)。土壤特征是基流DOC、SRP和Ca2+的重要预测因子,但与悬浮沉积物组分、任何氮形态或pH均无相关性。尽管这些源头溪流的河岸带基本保持完好,但高地土壤和植被干扰在基流和暴雨径流条件下对河流水化学仍有明显影响。