Threshold application rates of wood ash to an acidic forest soil

被引:74
作者
Kahl, JS
Fernandez, IJ
Rustad, LE
Peckenham, J
机构
[1] UNIV MAINE,DEPT APPL ECOL & ENVIRONM SCI,ORONO,ME 04469
[2] SHEVENELL GALLEN & ASSOCIATES,BANGOR,ME 04401
关键词
D O I
10.2134/jeq1996.00472425002500020003x
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Changes in soil and soil solution chemistry were studied for 2 yr after application of wood ash to an acidic forest Spodosol. Application rates to four 50 m(2) plots were: 0 (control), 6, 13, and 20 Mg CaCO3 equivalents per hectare (Mg ha(-1)). In soil solution, the 13 and 20 Mg ha(-1) treatments caused large but generally transient increases in base cations, pH, and anions. At 20 Mg ha(-1), solution concentrations of H, acid neutralizing capacity (ANC), K, and SO4 remained elevated for 20 mo. There was minimal response in soil solutions at 6 Mg ha(-1), suggesting that this rate may represent a threshold below which there is only minor response in soil solution chemistry. Loss of soil N into soil solution (as NO3) at the two higher application rates may have decreased available-N in the already N-limited soil. In the O horizon, all treatments resulted in increased pH and higher exchangeable Ca, K, Mg, CEC, and percent base saturation; Mn and Al decreased, In the B horizon, exchangeable Ca, K, Mg, and percent base saturation were higher than In the control. Responses in soil chemistry were not generally proportional to the ash application rate. Furthermore, the responses in soil chemistry al different application rates were generally not distinguishable from each other after 25 mo. The treatment rate of 6 Mg ha(-1) ash was sufficient to favorably alter soil exchange chemistry, without seriously affecting solution chemistry. Above 6 Mg ha(-1), soil exchange sites were unable to buffer ash amendments, resulting in substantial changes in solution chemistry.
引用
收藏
页码:220 / 227
页数:8
相关论文
共 32 条
[21]   EFFECTS OF FERTILIZATION ON THE FLUXES OF CHEMICAL-ELEMENTS THROUGH DIFFERENT FOREST ECOSYSTEMS [J].
MATZNER, E ;
KHANNA, PK ;
MEIWES, KJ ;
ULRICH, B .
PLANT AND SOIL, 1983, 74 (03) :343-358
[22]  
NAYLOR LM, 1989, TAPPI JUN, P199
[23]  
NAYLOR LM, 1986, TAPPI J OCT, P199
[24]   EFFECT OF WOOD ASH APPLICATION ON SOIL-PH AND SOIL TEST NUTRIENT LEVELS [J].
OHNO, T ;
ERICH, MS .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 1990, 32 (3-4) :223-239
[25]   A METHOD FOR JUDGING ALL CONTRASTS IN THE ANALYSIS OF VARIANCE [J].
SCHEFFE, H .
BIOMETRIKA, 1953, 40 (1-2) :87-104
[26]   TIMING, MAGNITUDE, AND IMPACT OF ACIDIC DEPOSITION ON SENSITIVE FOREST SITES [J].
SHORTLE, WC ;
BONDIETTI, EA .
WATER AIR AND SOIL POLLUTION, 1992, 61 (3-4) :253-267
[27]   ALUMINUM-INDUCED CALCIUM DEFICIENCY SYNDROME IN DECLINING RED SPRUCE [J].
SHORTLE, WC ;
SMITH, KT .
SCIENCE, 1988, 240 (4855) :1017-1018
[28]   WOOD-ASH COMPOSITION AND SOIL-PH FOLLOWING INTENSE BURNING [J].
ULERY, AL ;
GRAHAM, RC ;
AMRHEIN, C .
SOIL SCIENCE, 1993, 156 (05) :358-364
[29]   THE SHORT-TERM EFFECTS OF WOOD-ASH AMENDMENT ON FOREST SOILS [J].
UNGER, YL ;
FERNANDEZ, IJ .
WATER AIR AND SOIL POLLUTION, 1990, 49 (3-4) :299-314
[30]   MICROBIAL ACTIVITIES IN A HISTOSOL - EFFECTS OF WOOD ASH AND NPK FERTILIZERS [J].
WEBER, A ;
KARSISTO, M ;
LEPPANEN, R ;
SUNDMAN, V ;
SKUJINS, J .
SOIL BIOLOGY & BIOCHEMISTRY, 1985, 17 (03) :291-296