Responses of enzymatic activities within soil aggregates to 9-year nitrogen and water addition in a semi-arid grassland

被引:159
作者
Wang, Ruzhen [1 ,6 ]
Dorodnikov, Maxim [2 ]
Yang, Shan [1 ,3 ]
Zhang, Yongyong [1 ,6 ]
Filley, Timothy R. [4 ]
Turco, Ronald F. [5 ]
Zhang, Yuge [3 ]
Xu, Zhuwen [1 ]
Li, Hui [1 ]
Jiang, Yong [1 ]
机构
[1] Chinese Acad Sci, Inst Appl Ecol, State Key Lab Forest & Soil Ecol, Shenyang 110016, Peoples R China
[2] Univ Gottingen, Soil Sci Temp Ecosyst, Busgen Inst, D-37077 Gottingen, Germany
[3] Shenyang Univ, Coll Environm, Key Lab Reg Environm & Ecoremediat, Shenyang 110044, Peoples R China
[4] Purdue Univ, Dept Earth Atmospher & Planetary Sci, W Lafayette, IN 47907 USA
[5] Purdue Univ, Dept Agron, W Lafayette, IN 47907 USA
[6] Univ Chinese Acad Sci, Beijing 100049, Peoples R China
基金
中国国家自然科学基金;
关键词
Global change; Nitrogen deposition; Precipitation regimes; Extracellular enzymes; Microbial nitrogen limitation; Temperate grassland; MICROBIAL COMMUNITY COMPOSITION; NET PRIMARY PRODUCTIVITY; ORGANIC-MATTER DYNAMICS; CLIMATE-CHANGE; ELEVATED CO2; ECOENZYMATIC STOICHIOMETRY; INCREASED PRECIPITATION; PHOSPHORUS LIMITATION; NUTRIENT ACQUISITION; THEORETICAL-MODEL;
D O I
10.1016/j.soilbio.2014.11.015
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Soil microorganisms secrete enzymes used to metabolize carbon (C), nitrogen (N), and phosphorus (P) from the organic materials typically found in soil. Because of the connection with the active microbial biomass, soil enzyme activities can be used to investigate microbial nutrient cycling including the microbial response to environmental changes, transformation rates and to address the location of the most active biomass. In a 9-year field study on global change scenarios related to increasing N inputs (ambient to 15 g N m(-2) yr(-1)) and precipitation (ambient to 180 mm yr(-1)), we tested the activities of soil beta-glucosidase (BG), N-acetyl-glucosaminidase (NAG) and acid phosphomonoesterase (PME) for three soil aggregate classes: large macroaggregates (>2000 mu m), small macroaggregates (250-2000 mu m) and microaggregates (<250 mu m). Results showed higher BG and PME activities in micro-vs. small macroaggregates whereas the highest NAG activity was found in the large macroaggregates. This distribution of enzyme activity suggests a higher contribution of fast-growing microorganisms in the micro-compared with the macroaggregates size fractions. The responses of BG and PME were different from NAG activity under N addition, as BG and PME decreased as much as 47.1% and 36.3%, respectively, while the NAG increased by as much as 80.8%, which could imply better adaption of fungi than bacteria to lower soil pH conditions developed under increased N. Significant increases in BG and PME activities by as much as 103.4 and 75.4%, respectively, were found under water addition. Lower ratio of BG:NAG and higher NAG:PME underlined enhanced microbial N limitation relative to both C and P, suggesting the repression of microbial activity and the accompanied decline in their ability to compete for N with plants and/or the accelerated proliferation of soil fungi under elevated N inputs. We conclude that changes in microbial activities under increased N input and greater water availability in arid- and semi-arid grassland ecosystems where NPP is co-limited by N and water may result in substantial redistribution of microbial activity in different-sized soil particles. This shift will influence the stability of SOM in the soil aggregates and the nutrient limitation of soil biota. (C) 2014 Elsevier Ltd. All rights reserved.
引用
收藏
页码:159 / 167
页数:9
相关论文
共 70 条
[51]   Chronic N deposition does not apparently alter the biochemical composition of forest floor and soil organic matter [J].
Thomas, Dana C. ;
Zak, Donald R. ;
Filley, Timothy R. .
SOIL BIOLOGY & BIOCHEMISTRY, 2012, 54 :7-13
[52]   Nitrogen additions and microbial biomass: a meta-analysis of ecosystem studies [J].
Treseder, Kathleen K. .
ECOLOGY LETTERS, 2008, 11 (10) :1111-1120
[53]   Direct nitrogen and phosphorus limitation of arbuscular mycorrhizal fungi: a model and field test [J].
Treseder, KK ;
Allen, MF .
NEW PHYTOLOGIST, 2002, 155 (03) :507-515
[54]   AN EXTRACTION METHOD FOR MEASURING SOIL MICROBIAL BIOMASS-C [J].
VANCE, ED ;
BROOKES, PC ;
JENKINSON, DS .
SOIL BIOLOGY & BIOCHEMISTRY, 1987, 19 (06) :703-707
[55]   Spatial distribution of microbial biomass in microaggregates of a silty-loam soil and the relation with the resistance of microorganisms to soil drying [J].
vanGestel, M ;
Merckx, R ;
Vlassak, K .
SOIL BIOLOGY & BIOCHEMISTRY, 1996, 28 (4-5) :503-510
[56]   Terrestrial phosphorus limitation: mechanisms, implications, and nitrogen-phosphorus interactions [J].
Vitousek, Peter M. ;
Porder, Stephen ;
Houlton, Benjamin Z. ;
Chadwick, Oliver A. .
ECOLOGICAL APPLICATIONS, 2010, 20 (01) :5-15
[57]   Linking microbial community composition to function in a tropical soil [J].
Waldrop, MP ;
Balser, TC ;
Firestone, MK .
SOIL BIOLOGY & BIOCHEMISTRY, 2000, 32 (13) :1837-1846
[58]   FATE OF PHOSPHORUS DURING PEDOGENESIS [J].
WALKER, TW ;
SYERS, JK .
GEODERMA, 1976, 15 (01) :1-19
[59]   Changes in soil biological activities under reduced soil pH during Thlaspi caerulescens phytoextraction [J].
Wang, Autumn S. ;
Angle, J. Scott ;
Chaney, Rufus L. ;
Delorme, Thierry A. ;
McIntosh, Marla .
SOIL BIOLOGY & BIOCHEMISTRY, 2006, 38 (06) :1451-1461
[60]   Coupled response of soil carbon and nitrogen pools and enzyme activities to nitrogen and water addition in a semi-arid grassland of Inner Mongolia [J].
Wang, Ruzhen ;
Filley, Timothy R. ;
Xu, Zhuwen ;
Wang, Xue ;
Li, Mai-He ;
Zhang, Yuge ;
Luo, Wentao ;
Jiang, Yong .
PLANT AND SOIL, 2014, 381 (1-2) :323-336