Boesch D F, Brinsfield R B, Magnien R E
University of Maryland Center for Environmental Science, P.O. Box 775, Cambridge, MD 21613, USA.
J Environ Qual. 2001 Mar-Apr;30(2):303-20. doi: 10.2134/jeq2001.302303x.
Chesapeake Bay has been the subject of intensive research on cultural eutrophication and extensive efforts to reduce nutrient inputs. In 1987 a commitment was made to reduce controllable sources of nitrogen (N) and phosphorous (P) by 40% by the year 2000, although the causes and effects of eutrophication were incompletely known. Subsequent research, modeling, and monitoring have shown that: (i) the estuarine ecosystem had been substantially altered by increased loadings of N and P of approximately 7- and 18-fold, respectively; (ii) hypoxia substantially increased since the 1950s; (iii) eutrophication was the major cause of reductions in submerged vegetation; and (iv) reducing nutrient sources by 40% would improve water quality, but less than originally thought. Strong public support and political commitment have allowed the Chesapeake Bay Program to reduce nutrient inputs, particularly from point sources, by 58% for P and 28% for N. However, reductions of nonpoint sources of P and N were projected by models to reach only 19% and 15%, respectively, of controllable loadings. The lack of reductions in nutrient concentrations in some streams and tidal waters and field research suggest that soil conservation-based management strategies are less effective than assumed. In 1997, isolated outbreaks of the toxic dinoflagellate Pfiesteria piscicida brought attention to the land application of poultry manure as a contributing factor to elevated soil P and ground water N concentrations. In addition to developing more effective agricultural practices, emerging issues include linking eutrophication and living resources, reducing atmospheric sources of N, enhancing nutrient sinks, controlling sprawling suburban development, and predicting and preventing harmful algal blooms.
切萨皮克湾一直是文化富营养化深入研究的对象,并且为减少营养物质输入付出了巨大努力。1987年,人们承诺到2000年将氮(N)和磷(P)的可控来源减少40%,尽管当时富营养化的成因和影响还不完全清楚。随后的研究、建模和监测表明:(i)河口生态系统已因氮和磷负荷分别增加约7倍和18倍而发生了显著改变;(ii)自20世纪50年代以来,缺氧情况大幅增加;(iii)富营养化是沉水植被减少的主要原因;(iv)将营养物质来源减少40%将改善水质,但改善程度低于最初预期。公众的大力支持和政治承诺使切萨皮克湾项目能够将营养物质输入,特别是点源输入,减少了58%的磷和28%的氮。然而,模型预测非点源磷和氮的减少量分别仅达到可控负荷的19%和15%。一些溪流和潮汐水域营养物质浓度缺乏下降以及实地研究表明,基于土壤保护的管理策略效果不如预期。1997年,有毒甲藻费氏藻的零星爆发使人们关注到家禽粪便的土地施用是土壤磷含量升高和地下水氮浓度升高的一个促成因素。除了制定更有效的农业实践外,新出现的问题还包括将富营养化与生物资源联系起来、减少氮的大气来源、增强营养物质汇、控制郊区无序扩张以及预测和预防有害藻华。