Relationships between net nitrogen mineralization, properties of the forest floor and mineral soil, and wood production in Pinus radiata plantations

2001 ◽  
Vol 31 (5) ◽  
pp. 889-898 ◽  
Author(s):  
J Clive Carlyle ◽  
EK Sadanandan Nambiar
Keyword(s):  
Organic Matter ◽  
Soil Properties ◽  
Pinus Radiata ◽  
N Mineralization ◽  
Forest Floor ◽  
Mineral Soil ◽  
Soil N ◽  
Wood Production ◽  
Total N

We examined the relationship between net nitrogen (N) mineralization (subsequently termed N mineralization) in the forest floor and mineral soil (0–0.15 m) of 20 Pinus radiata D. Don plantations ranging in age from 23 to 59 years, how mineralization was influenced by soil properties, and its relationship to wood production. Forest floor properties had a narrower relative range than the same set of mineral soil properties. Total N in the litter layer was 5.0–9.5 g·kg–1 compared with 0.23–2.53 g·kg–1 in mineral soil. Laboratory rates of net N mineralization ranged between 1.1 and 9.7 mg·kg–1·day–1 in forest floor and between 0.02 and 0.53 mg·kg–1·day–1 in mineral soil. The range in litter lignin (35.3–48.0%) was especially narrow, despite the large range in stand productivity. Nitrogen mineralized in the forest floor was not correlated with any of the measured forest floor or mineral soil properties. Nitrogen mineralized per unit mineral soil N (ksn) was negatively correlated with the mineral soil N to organic phosphorus ratio (N/Po) (r2 = 0.82). In mineral soil a relationship combining N/Po and total N concentration explained 90% of the variation in N mineralized. Nitrogen mineralized in the forest floor was correlated with that mineralized in the mineral soil when expressed per unit C or N (r2 = 0.54 or 0.57, respectively). Thus, the quality of organic matter in the forest floor partly reflected the quality of organic matter in the mineral soil with respect to N mineralization. Mineralization in mineral soil dominated the net N available to the stand. For sandy soils, wood production (m3·ha–1·year–1) was correlated with N mineralized in the forest floor + mineral soil (r2 = 0.71). In P. radiata stands growing in southern Australia, rates of wood production per unit N mineralized and per unit rainfall appear to be substantially higher than those of a wide range of natural and planted stands in North America.

scholarly journals Aspen and white spruce productivity is reduced by organic matter removal and soil compaction

2012 ◽  
Vol 88 (03) ◽  
pp. 306-316 ◽  
Author(s):  
Richard Kabzems
Keyword(s):  
Organic Matter ◽  
Soil Properties ◽  
Bulk Density ◽  
Soil Compaction ◽  
Forest Floor ◽  
Mineral Soil ◽  
White Spruce ◽  
Soil Bulk Density ◽  
Post Treatment ◽  
Organic Matter Removal

Declines in forest productivity have been linked to losses of organic matter and soil porosity. To assess how removal of organic matter and soil compaction affect short-term ecosystem dynamics, pre-treatment and year 1, 5 and 10 post-treatment soil properties and post-treatment plant community responses were examined in a boreal trembling aspen (Populus tremuloidesMichx.)-dominated ecosystem in northeastern British Columbia. The experiment used a completely randomized design with three levels of organic matter removal (tree stems only; stems and slash; stems, slash and forest floor) and three levels of soil compaction (none, intermediate [2-cm impression], heavy [5-cm impression]). Removal of the forest floor initially stimulated aspen regeneration and significantly reduced height growth of aspen (198 cm compared to 472–480 cm) as well as white spruce (Picea glauca [Moench] Voss) height (82 cm compared to 154–156 cm). The compaction treatments had no effect on aspen regeneration density. At Year 10, heights of both aspen and white spruce were negatively correlated with upper mineral soil bulk density and were lowest on forest floor + whole tree removal treatments. Recovery of soil properties was occurring in the 0 cm to 2 cm layer of mineral soil. Bulk density values for the 0 cm to 10 cm depth remained above 86% of the maximum bulk density for the site, a soil condition where reduced tree growth can be expected.

Nitrogen mineralization characteristics of forest floor organic matter on slash-burned sites in coastal British Columbia

1991 ◽  
Vol 21 (2) ◽  
pp. 235-241
Author(s):  
J. W. Fyles ◽  
I. H. Fyles ◽  
M. C. Feller
Keyword(s):  
Organic Matter ◽  
Nitrogen Mineralization ◽  
N Mineralization ◽  
Forest Floor ◽  
Soil Survey ◽  
Total N ◽  
Potentially Mineralizable N ◽  
N Fertility ◽  
Low K ◽  
Floor Material

Nitrogen mineralization characteristics of the dominant types of organic matter in the forest floor of slash-burned sites were measured using a 26-week aerobic incubation. Six classes of forest floor material were distinguished on the basis of morphology and N mineralization characteristics. Fermentation layer materials, matted together with fungal hyphae, had a high content of total and potentially mineralizable N (N0) (7804 and 2816 μg/g, respectively) and mineralized the most N during incubation (1605 μg/g). Decayed wood had the lowest level of total N (1816 μg/g) and N0 (195 μg/g) and mineralized the least N (266 μg/g) despite a high inherent mineralization rate (k) (0.16). Humified materials (Hd and Hr) occupied a midrange, with the exception of those from thin residual horizons, which had high N0 values (2246–6009 μg/g) and low k-values (0.005–0.012). The significant differences in N mineralization among organic materials that are morphologically or ecologically distinct in the field suggest that it may be possible to assess site N fertility using intensive forest floor and soil survey data and information on the N characteristics of dominant horizon types.

Initial quantitative characterization of soil nutrient regimes. I. Soil properties

1987 ◽  
Vol 17 (12) ◽  
pp. 1557-1564 ◽  
Author(s):  
R. D. Kabzems ◽  
K. Klinka
Keyword(s):  
Soil Properties ◽  
Forest Floor ◽  
Mineral Soil ◽  
Soil Nutrient ◽  
N Fertilization ◽  
Total N ◽  
Quantitative Classification ◽  
Topographic Features ◽  
Exchangeable Ca ◽  
Study Sites

Previous attempts to characterize soil nutrient regimes of forest ecosystems have been qualitative evaluations utilizing vegetation and (or) topographic features, morphological soil properties, and mineralogy of soil parent materials. The objective of this study was to describe and provide initial data for quantitative classification of soil nutrient regimes in some Douglas-fir ecosystems on southern Vancouver Island. A multivariate classification using forest floor plus mineral soil mineralizable N and exchangeable Mg quantities was proposed for the four nutrient regimes (poor, medium, rich, and very rich) recognized in this study. Significant differences in mineralizable and total N existed between the four identified soil nutrient regimes. The previous N fertilization of two study sites did not seem to change soil N status sufficiently to alter the classification. The differences in nutrient availability were more distinct when forest floor and mineral soil properties, expressed on an areal basis, were summed. There were no significant differences in exchangeable Ca and Mg for the poor and medium soil nutrient regimes. The humus form of the forest floor was an important characteristic for identifying soil nutrient regimes in the field; however, the nutrient quantities of the forest floor reflected differences in bulk density and depth and did not effectively distinguish between regimes.

Nitrogen dynamics in conifer-dominated forests with and without hardwoods

1987 ◽  
Vol 17 (11) ◽  
pp. 1434-1441 ◽  
Author(s):  
D. A. Perry ◽  
C. Choquette ◽  
P. Schroeder
Keyword(s):  
N Mineralization ◽  
Forest Floor ◽  
C:N Ratio ◽  
Mineral Soil ◽  
Soil N ◽  
Mixed Stands ◽  
Soil P ◽  
Soil N Mineralization ◽  
Leaf Litterfall ◽  
Uniform Area

Nitrogen and carbon in the surface 12 cm of mineral soil, N in leaf litterfall, anaerobic N mineralization rates in the soil and forest floor, and root and N accretion to sand traps placed in surface soil layers were compared in forests with hardwoods either completely or partially removed during a conifer thinning 3 years before. An adjacent unthinned conifer–hardwood stand was also included. Conifer stocking did not differ between thinned stands with and without hardwoods. Stands without hardwoods averaged 520 kg/ha more N in mineral soil (p < 0.001), 20% more N mineralized from soil during 7-day incubations (p < 0.001), and lower soil C:N ratio (p = 0.02) than stands with hardwoods. These variables did not differ between thinned and unthinned mixed stands. Soil N did not correlate with the number of hardwoods removed. Weight of forest floor and rate of N mineralization from the forest floor did not differ between mixed and pure stands. However, stands with hardwoods returned about 10 kg•ha−1•year−1 more N in leaf litter (due to higher N concentration in conifer litter as well as the presence of high-N hardwood litter); stands without hardwoods accreted about 10 kg•ha−1•year−1 more N in sand traps. Soil N mineralization in mixed stands correlated positively with N mineralization in the forest floor but not with N accretion to sand traps, while the opposite was true in pure conifer stands. Although pretreatment variability among stands cannot be ruled out, the replicated treatments within a relatively uniform area make it appear likely that differences were related to the presence or absence of hardwoods. This was not a simple additive effect, however, but a community-level phenomenon, that is, conifers cycled N differently when mixed with hardwoods than when in pure stands.

Acid Deposition and Nutrient Leaching from Deciduous Vegetation and Podzolic Soils at the Turkey Lakes Watershed

1988 ◽  
Vol 45 (S1) ◽  
pp. s96-s100 ◽  
Author(s):  
N. W. Foster ◽  
J. A. Nicolson
Keyword(s):  
Acid Deposition ◽  
Forest Floor ◽  
Mineral Soil ◽  
Soil N ◽  
Ion Concentrations ◽  
Podzolic Soils ◽  
Native Soil ◽  
Turkey Lakes Watershed ◽  
A Minor

Mean annual ion concentrations and ion fluxes in precipitation induced by contact with a maple–birch forest and soil were determined for 1981–85 at the Turkey Lakes Watershed (47°03′N, 84°15′W). Neutralization of atmospherically deposited H+ was effected by the canopy and mineral soil. Sulphate was an important counter-ion for K+ leached from the vegetation. Acid deposition had a minor impact on the quality of stemflow and forest floor percolate, which were enriched in K+ and Ca2+ mobilized in association with organic anions. Calcium and Mg2+ were leached from the mineral soil in association with SO42− and NO3−. Sulphate was derived largely from acid deposition, and NO3− from both precipitation and nitrification of native soil N.

scholarly journals Factors influencing the soil-plant nitrogen cycle of hill pastures under conventional and organic management

2003 ◽  
pp. 195-198
Author(s):  
R.L. Parfitt ◽  
G.W.Yeates D.J. Ross ◽  
A.D. Mackay ◽  
P.J. Budding
Keyword(s):  
Organic Matter ◽  
Soil Organic Matter ◽  
N Mineralization ◽  
Dominant Factor ◽  
Net N Mineralization ◽  
Soil N ◽  
Organic Management ◽  
N Supply ◽  
Wide Range

Nitrogen (N) is the major nutrient that limits pasture growth in New Zealand. Here we test the hypothesis that N supply to herbage from soil microbial mineralization is a function of both the quantity and quality of the soil organic matter, and that this underlying process is similar under conventional and organic management. Preliminary results for October- November 2002 from nine sites with a wide range of soil N status at AgResearch, Ballantrae show that microbial-mineralized N supply from the soil to herbage was the dominant factor controlling the differences in herbage growth. Herbage N was also highly correlated with the soil N supply, as estimated from a 56-day laboratory incubation of soil (0-7.5 cm, and 7.5-20 cm depths). For these soils, spring herbage production could be estimated from the negative relationship with the C:N ratio of the topsoils. This suggests the over-riding factor in the N supply at the nine sites was the quality of soil organic matter in the topsoils. Quality is enhanced through the growth of legumes that in turn depend on the P status of the soil. The soil parent material at some sites (1996 organic farmlets) is calcareous mudstone, which has a high P status, and may explain some differences in site fertility not explained by past P applications. The relationship between the quantity and quality of organic matter and microbial N mineralization in the four farmlets that had organic management appeared to be on the same trend-lines as those in the conventional farmlets, indicating that the underlying net N mineralization process was similar under conventional and organic management. Other factors statistically related to herbage yield and soil net N mineralization were some groups of nematodes and microbial P, but not microbial biomass C or N. Keywords: N mineralisation, non-chemical farms, organic farms, soil fertility

The use of laboratory measurements to predict nitrogen mineralization and nitrification in Pinus radiata plantations after harvesting

1998 ◽  
Vol 28 (8) ◽  
pp. 1213-1221 ◽  
Author(s):  
J Clive Carlyle ◽  
EK Sadanandan Nambiar ◽  
Mark W Bligh
Keyword(s):  
Nitrogen Mineralization ◽  
Pinus Radiata ◽  
N Mineralization ◽  
Forest Floor ◽  
Mineral Soil ◽  
Net N Mineralization ◽  
Laboratory Measurements ◽  
Aerobic Incubation ◽  
Highly Correlated ◽  
Sequential Coring

We tested whether laboratory estimates of net N mineralization and nitrification (subsequently termed N mineralization and nitrification) could be used to predict these processes in the field after harvesting nine Pinus radiata D. Don. plantations. Laboratory rates of N mineralization and nitrification were measured by aerobic incubation (20°C) of intact cores. Annual rates of these processes in the field were measured using a sequential coring procedure. Rates of N mineralization in the laboratory were 1.1-6.6 and 0.019-0.525mg·kg-1·day-1 for forest floor and mineral soil, respectively (nitrification accounted for 6-71 and 8-93% of N mineralization). Annual N mineralization by forest floor in the field was 5.2-23.9kg·ha-1·year-1and was not correlated with N mineralized in the laboratory. Annual N mineralization in mineral soil in the field was 16-74kg·ha-1·year-1and was highly correlated (r2 = 0.97) with N mineralized in the laboratory. Annual nitrification in forest floor in the field ranged from 3 to 45% of annual N mineralization, and in mineral soil from 4 to 27%, both were correlated with relative nitrification measured in the laboratory.

Predicting soil N mineralization: Relevance of organic matter fractions and soil properties

2011 ◽  
Vol 43 (8) ◽  
pp. 1714-1722 ◽  
Author(s):  
Gerard H. Ros ◽  
Marjoleine C. Hanegraaf ◽  
Ellis Hoffland ◽  
Willem H. van Riemsdijk
Keyword(s):  
Organic Matter ◽  
Soil Properties ◽  
N Mineralization ◽  
Soil N ◽  
Soil N Mineralization ◽  
Organic Matter Fractions
Sign in / Sign up

Export Citation Format

Share Document