Nutrient mineralisation and microbial functional diversity in a restored bog approach natural conditions 10 years post restoration

被引:55
作者
Andersen, Roxane [1 ,3 ,4 ]
Wells, Corey [2 ]
Macrae, Merrin [2 ]
Price, Jonathan [2 ]
机构
[1] Macaulay Land Use Res Inst, James Hutton Inst, Aberdeen AB15 8QH, Scotland
[2] Univ Waterloo, Dept Geog & Environm Management, Waterloo, ON N2L 3G1, Canada
[3] Univ Laval, PERG, Quebec City, PQ G1V 0A6, Canada
[4] Univ Highlands & Isl, Environm Res Inst, Thurso KW147JD, Caithness, Scotland
基金
加拿大自然科学与工程研究理事会;
关键词
Ombtrophic peatlands; Peatland restoration; Belowground processes; Microbial functional diversity; Nutrient dynamics; Cutover peatlands; Mineralization; Carbon utilization profiles; PHOSPHORUS MINERALIZATION; NITROGEN MINERALIZATION; COMMUNITY STRUCTURE; ORGANIC-CARBON; PEATLAND; WATER; SOIL; PLANT; DECOMPOSITION; QUEBEC;
D O I
10.1016/j.soilbio.2013.04.004
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Peatland restoration has been implemented on sites exploited for horticultural peat for over a decade in Eastern Canada. However, little is known about nutrient dynamics and microbial processes in this region. Belowground nitrogen (N) and phosphorus (P) transformations and carbon utilisation by microorganisms were examined in a harvested peatland 10 years after restoration measures were implemented to assess whether restoration is returning the peatland to a state that falls within the natural range of variation found in a neighbouring bog. N mineralisation rates were almost 10-fold higher in the surface (0-10 cm) compared to the subsurface (10-20 cm) layers for all sites and were highly variable within sites. P pools were small (<0.02 mu g g(-1) dry peat) and mineralisation rates of P were low in all sections. In the surface layer, the net mineralisation and ammonification rates appeared to be highest in unrestored sites but lowest in restored sites. In contrast, the capacity of microorganisms in using different carbon (C) sources, also described as microbial functional diversity, was highest at restored sites but lowest at unrestored sites. The preferable C sources varied between sites and were significantly correlated with aboveground vegetation composition. Our study suggests that microbial activity and nutrient transformations differ between natural and unrestored harvested peatlands. Our results indicate that the presence of vegetation regrowth in the unrestored area of a peatland alters belowground processes by stimulating microbial activity and increasing the uptake of nutrients, leading to smaller pools of inorganic N available in the peat. When restoration has been carried out, microbial activity is even higher than in natural conditions, possibly leading to high immobilization of N, and net mineralisation rates are very low. This research indicates that while belowground processes have shifted from unrestored conditions following restoration, they do not appear to be fully re-established to a degree similar to natural conditions 10 years post-restoration. (C) 2013 Elsevier Ltd. All rights reserved.
引用
收藏
页码:37 / 47
页数:11
相关论文
共 73 条
[51]  
Rowell D.L, 1995, Soil science: Methods and applications
[52]   The implications of exoenzyme activity on microbial carbon and nitrogen limitation in soil: a theoretical model [J].
Schimel, JP ;
Weintraub, MN .
SOIL BIOLOGY & BIOCHEMISTRY, 2003, 35 (04) :549-563
[53]  
Sen R., 2012, P 14 INT PEAT C STOC
[54]   Hydrological changes following restoration of the Bois-des-Bel Peatland, Quebec, 1999-2002 [J].
Shantz, M. A. ;
Price, J. S. .
JOURNAL OF HYDROLOGY, 2006, 331 (3-4) :543-553
[55]  
Sonesson M., 1980, ECOLOGY SUBARCTIC MI, V30, P209
[56]   Peat bog restoration: Effect of phosphorus on plant re-establishment [J].
Sottocornola, Matteo ;
Boudreau, Stephanie ;
Rochefort, Line .
ECOLOGICAL ENGINEERING, 2007, 31 (01) :29-40
[57]   MECHANISMS FOR SOIL-MOISTURE EFFECTS ON ACTIVITY OF NITRIFYING BACTERIA [J].
STARK, JM ;
FIRESTONE, MK .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1995, 61 (01) :218-221
[58]   Dissolved organic carbon production and runoff quality following peatland extraction and restoration [J].
Strack, M. ;
Toth, K. ;
Bourbonniere, R. ;
Waddington, J. M. .
ECOLOGICAL ENGINEERING, 2011, 37 (12) :1998-2008
[59]   Litter type affects the activity of aerobic decomposers in a boreal peatland more than site nutrient and water table regimes [J].
Strakova, P. ;
Niemi, R. M. ;
Freeman, C. ;
Peltoniemi, K. ;
Toberman, H. ;
Heiskanen, I. ;
Fritze, H. ;
Laiho, R. .
BIOGEOSCIENCES, 2011, 8 (09) :2741-2755
[60]   Disentangling direct and indirect effects of water table drawdown on above- and belowground plant litter decomposition: consequences for accumulation of organic matter in boreal peatlands [J].
Strakova, Petra ;
Penttila, Timo ;
Laine, Jukka ;
Laiho, Raija .
GLOBAL CHANGE BIOLOGY, 2012, 18 (01) :322-335