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Distribution and Fate of Anthropogenic Nitrogen in the Calamagrostis angustifolia Wetland Ecosystem of Sanjiang Plain, Northeast China
Author(s) -
Sun ZhiGao,
Liu JingShuang
Publication year - 2008
Publication title -
journal of integrative plant biology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 2.734
H-Index - 83
eISSN - 1744-7909
pISSN - 1672-9072
DOI - 10.1111/j.1744-7909.2007.00627.x
Subject(s) - microcosm , sanjiang plain , nitrogen , environmental science , wetland , fertilizer , nutrient , ecosystem , agronomy , environmental chemistry , chemistry , ecology , biology , marsh , organic chemistry
Wetlands are important for the protection of water quality of rivers and lakes, especially those adjacent to agricultural landscapes, by intercepting and removing nutrients in runoff. In this study, the 15 N tracer technique was applied to study the distribution and fate of anthropogenic nitrogen ( 15 N‐fertilizer) in Calamagrostis angustifolia Kom wetland plant‐soil microcosms to identify the main ecological effects of it. 15 NH 4 15 NO 3 solution (14.93 mg N/L, 20.28 at.% 15 N) was added to each microcosm of the first group, which was approximate to the current nitrogen concentration (CNC) of farm drainage, and 29.86 mg N/L 15 NH 4 15 NO 3 solution was added to another group, which was approximate to the double nitrogen concentration (DNC) of farm drainage, while no nitrogen (NN) was added to the third group. The results suggest that the input of anthropogenic nitrogen has positive effects on the biomass and total nitrogen content of plant, and the positive effects will be elevated as the increase of its input amount. The increase of 15 N‐fertilizer can also elevate its amounts and proportions in plant nitrogen. Soil nitrogen is still the main source of plant nitrogen, but its proportion will be reduced as the increase of 15 N‐fertilizer. The study of the fate of 15 N‐fertilizer indicates that, in CNC treatment, only a small proportion is water‐dissolved (0.13 ± 0.20%), a considerable proportion is soil‐immobilized (17.02 ± 8.62%), or plant‐assimilated (23.70 ± 0.92%), and most is lost by gaseous forms (59.15 ± 8.35%). While in DNC treatment, about 0.09 ± 0.15% is water‐dissolved, 15.33 ± 7.46% is soil‐immobilized, 23.55 ± 2.86% is plant‐assimilated, and 61.01 ± 5.59% is lost by gaseous forms. The double input of anthropogenic nitrogen can not elevate the proportions of plant‐assimilation, soil‐immobilization and water‐dissolution, but it can enhance the gaseous losses.