Peters N E, Shanley J B, Aulenbach B T, Webb R M, Campbell D H, Hunt R, Larsen M C, Stallard R F, Troester J, Walker J F
U.S. Geological Survey, 3039 Amwiler Rd., Suite 130 Atlanta, GA 30360-2824, USA.
Sci Total Environ. 2006 Apr 1;358(1-3):221-42. doi: 10.1016/j.scitotenv.2005.04.044. Epub 2005 Jun 22.
Geochemical mass balances were computed for water years 1992-1997 (October 1991 through September 1997) for the five watersheds of the U.S. Geological Survey Water, Energy, and Biogeochemical Budgets (WEBB) Program to determine the primary regional controls on yields of the major dissolved inorganic solutes. The sites, which vary markedly with respect to climate, geology, physiography, and ecology, are: Allequash Creek, Wisconsin (low-relief, humid continental forest); Andrews Creek, Colorado (cold alpine, taiga/tundra, and subalpine boreal forest); Río Icacos, Puerto Rico (lower montane, wet tropical forest); Panola Mountain, Georgia (humid subtropical piedmont forest); and Sleepers River, Vermont (humid northern hardwood forest). Streamwater output fluxes were determined by constructing empirical multivariate concentration models including discharge and seasonal components. Input fluxes were computed from weekly wet-only or bulk precipitation sampling. Despite uncertainties in input fluxes arising from poorly defined elevation gradients, lack of dry-deposition and occult-deposition measurements, and uncertain sea-salt contributions, the following was concluded: (1) for solutes derived primarily from rock weathering (Ca, Mg, Na, K, and H(4)SiO(4)), net fluxes (outputs in streamflow minus inputs in deposition) varied by two orders of magnitude, which is attributed to a large gradient in rock weathering rates controlled by climate and geologic parent material; (2) the net flux of atmospherically derived solutes (NH(4), NO(3), SO(4), and Cl) was similar among sites, with SO(4) being the most variable and NH(4) and NO(3) generally retained (except for NO(3) at Andrews); and (3) relations among monthly solute fluxes and differences among solute concentration model parameters yielded additional insights into comparative biogeochemical processes at the sites.
为确定主要溶解无机溶质产量的主要区域控制因素,对美国地质调查局水、能源和生物地球化学预算(WEBB)项目的五个流域在1992 - 1997水年(1991年10月至1997年9月)进行了地球化学质量平衡计算。这些地点在气候、地质、地貌和生态方面差异显著,分别是:威斯康星州的阿莱夸什溪(低起伏,湿润大陆性森林);科罗拉多州的安德鲁斯溪(寒冷高山、泰加林/苔原和亚高山北方森林);波多黎各的伊卡科斯河(低山地,湿润热带森林);佐治亚州的帕诺拉山(湿润亚热带山麓森林);以及佛蒙特州的斯利珀斯河(湿润北方硬木森林)。通过构建包括流量和季节成分的经验多元浓度模型来确定溪流水输出通量。输入通量根据每周仅湿沉降或总降水量采样计算得出。尽管由于海拔梯度定义不明确、缺乏干沉降和 occult - 沉降测量以及海盐贡献不确定等因素导致输入通量存在不确定性,但得出了以下结论:(1)对于主要源自岩石风化的溶质(钙、镁、钠、钾和H(4)SiO(4)),净通量(径流输出量减去沉积输入量)变化了两个数量级,这归因于受气候和地质母质控制的岩石风化速率的巨大梯度;(2)大气源溶质(铵、硝酸盐、硫酸盐和氯)的净通量在各地点之间相似,其中硫酸盐变化最大,铵和硝酸盐通常被保留(安德鲁斯的硝酸盐除外);(3)月溶质通量之间的关系以及溶质浓度模型参数之间的差异为各地点的比较生物地球化学过程提供了更多见解。