SlideShare a Scribd company logo
ABSTRACT
It is widely accepted that afforestation adversely affects soil chemical properties. A
significant decrease in pH, base cation status and acid neutralising capacity
(ANC), coupled with increasing acidity have been observed to occur in acid
coniferous forest soils both in the Northern and Southern Hemispheres.
International and local studies in Southern Africa have observed declining
productivity over successive rotations in pine plantations. Increasing acidity loads
in the Northern Hemisphere and their adverse effects on forest health have
generated a search for chemical indices that would assist in pursuing thresholds
beyond which forest vitality is damaged. A common and widely used chemical
index is the Ca/Al ratio. The most common parameter adopted is the Ca/Al molar
ratio in soil solutions. Recent studies in Southern Africa (Swaziland, Kwazulu-
Natal) and in the Sabie area (Eastern Escarpment) have indicated that some
forest compartments (Pinus sp.) may experience Ca/Al molar ratios dropping
below unity. The value of unity is widely used and proposed as a threshold beyond
which tree vitality may be adversely affected.
This study was conducted to determine the state of surface (0-20cm) soils
underlying pine plantations of different ages in the Sabie area on the Eastern
Escarpment of Southern Africa. The pine plantations were selected in areas
overlying a uniform bedrock (shale), high altitude, high rainfall, north facing aspect
and confined to 3 pine species (P. elliottii, P. patula and P. taeda). A composite
sample was taken from each of 22 forest compartments varying in age (between
22 and 67 years) and rotation (first, second and third). In addition, the results of
previous investigations of forest soils in the Eastern Escarpment region were
considered in order to expand the array of forest compartment ages and the size
of the overall data set used for statistical analysis, so that comparisons could be
made.
Prior to analysis the soils were air dried and sieved (2mm). Characterising the soil
1
and investigation of the acidity status was conducted by analysis of pH (in water
and KCl), organic carbon, acid neutralising capacity and exchangeable acidity and
basic cations. All the pine forest surface soils are highly acidic. The acidification of
natural soils under grassland is enhanced by afforestation and increases with
increasing period of afforestation, predominantly within the first two decades. The
pH levels (3.7-4.1 in KCl) dropped markedly in surface soils in the first two
decades following afforestation. KCl-extractable acidity was observed to decline in
a similar way for the first two decades. There is some indication of further
acidification with plantation age beyond two decades, although the effect is not
significant.
Base saturation levels do not exceed 25%, and exhibit a general drop in respect to
afforestation of grassland soils. The depletion of basic cations (BC) from the
exchange sites is evident as shown by a decline in the BC/acidity ratio, to values
below unity, predominantly in the first decade following afforestation.
High levels of organic carbon were detected in the surface soils of the pine
plantations studied (3.7-10%). The presence of organic matter is important in the
context of Al complexation, which was confirmed by a significant correlation
(r2
=0.59) between CuCl2-extractable Al and organic carbon.
Soil solution composition was estimated based on the analysis of saturated paste
extracts. The analysis included determination of pH (in the paste and in the
extract), electrical conductivity (EC), dissolved organic carbon (DOC), monomeric
Al, monomeric silica and major cations and anions. In addition, geochemical
modelling (MINTEQA2) was used to calculate ion activities and saturation indices.
Similarly to the solid phase, the soil solution was highly acidic with pH (saturated
paste) levels ranging from 4.36 to 4.91. An important observation, and of utmost
importance for future studies, was that of declining ionic strength of the soil
solution with increasing plantation age (r2
=0.59).
Additional interesting observations were made of unexpectedly high levels of
fluoride in solution (1.9-12 mg/l), which altered the detection of Al3+
and Al(OH)X
3-X
2
concentrations in solution, and the calculation of alumino-silicate mineral solubility
equilibria. The colorimetric method used for the detection of monomeric Al in
solution probably excludes, to a large extent, F-complexed Al thus, posing great
difficulty in the calculation of F-free monomeric Al activity in solution.
Consequently, a more realistic approach was considered. In the process of
calculating monomeric Al activities in solution (using MINTEQA2), the fluoride
concentrations were thus, excluded. The inclusion of F in geochemical speciation
calculations has indicated that the majority of Al species in solution are complexed
to F and in addition, produced inconsistencies with respect to saturation indices of
gibbsite, kaolinite and jurbanite. Evaluating the dissolution of Al in the absence of
F offers the possibility that the dissolution of Al is controlled by Al-OM complexes
(under pH 4.7) and by gibbsite (above pH 4.7).
The Ca/Al molar concentration ratio in solution was observed to drop in the soils
following afforestation, and to reach, in some cases, levels below unity thus
suggesting, that at some future time, forest health may be adversely affected.
Ca/Al activity ratios calculated in the presence of F, were more than five orders of
magnitude higher than activity ratio calculated in the absence of F.
High concentrations of NH4
+
were detected in solution (4.8-36.5 mg/l) while other
soluble forms of nitrogen were detected in significantly lower concentrations (NO2
-
4 mg/l; NO3
-
- mostly undetected). The Abundance of NH4
+
-N coupled with smaller
concentrations of NO2 may be the cause of the method used for the preparation of
the saturated soil pastes and consequently interruption of biochemical processes
such as nitrification taking place in the soil environment. Alternetively, the reason
may be the loss of nitrogen from the F and H horizons (forest floor) to the upper
mineral horizon in the form of NH4
+
-N, whereas the loss of nitrogen from the A
horizon is mainly in the form of NO3-N.
High levels of dissolved organic carbon (DOC) were detected (53-193mg/l) and
conform to the abundance of organic matter. A considerable anion deficit with
respect to the charge balance of major ions in solution was assumed to be
accounted for by negatively charged dissolved organic matter.
3
Comparing the Ca/Al ratio of the soil solution to the basic cations/acidity ratio of
the exchange sites reveals similar trends (r2
=0.37 and r2
=0.39, respectively) with
plantation age. As with acidity and pH, the Ca/Al ratio drops markedly in the first
two decades following afforestation. Thus, strengthening the argument that the
most prominent chemical changes in surface soils of these pine plantations occur
within the first 20 to 30 years after the grasslands soils have been planted to trees.
4

More Related Content

PDF
Status of heavy metals in agricultural soils and the need for adapted soil th...
DOC
CHAPTER3.DOC
PDF
Hydrochemical Characteristics and Shallow Groundwater Quality in Kirkuk Urban...
PDF
11.phosphorus speciation in drinking water treatment residuals
PPT
42. soil acidity and ph by allah dad khan
PDF
Acid Mine Drainage In Pennsylvania Streams
PDF
Justin Beslity -Thesis
PDF
Lime requirement of acid soil, liming materials, reclamation and management o...
Status of heavy metals in agricultural soils and the need for adapted soil th...
CHAPTER3.DOC
Hydrochemical Characteristics and Shallow Groundwater Quality in Kirkuk Urban...
11.phosphorus speciation in drinking water treatment residuals
42. soil acidity and ph by allah dad khan
Acid Mine Drainage In Pennsylvania Streams
Justin Beslity -Thesis
Lime requirement of acid soil, liming materials, reclamation and management o...

What's hot (19)

PPTX
Chemistry and physics of submerged soil
PDF
Carbon utilization efficiency
PPTX
The Roles of Mangrove for Metal(Loid)S Retention and Implication for Designin...
PDF
Chemistry of Submerged Soils
PDF
K cl in_fertigation
PDF
Submerged soil chemistry and management
PPTX
waterlogged soils
DOC
CHAPTER4.DOC
PPTX
LIME REQUIREMENT AND LIMING MATERIALS FOR ACIDIC SOIL
PDF
Subsurface 1D Transport of Dioxin Beneath An Uncontrolled Dump Site - A Case ...
PPTX
Soil organic carbon analysis techniques
PPT
Soil Potassium
PPTX
pH and its effects on nutrient availablity
PPSX
Phosphate fixation
PPTX
Acidic,Salic, And Alkali Soils
PPTX
Naresh gohil
PDF
Hydrogeochemistry and Microbiology of Wadi Al Bih Limestone Aquifer in Northe...
PPTX
Chemistry of submerged soils re
PPT
Problem soils and soil acidity, P K MANI
Chemistry and physics of submerged soil
Carbon utilization efficiency
The Roles of Mangrove for Metal(Loid)S Retention and Implication for Designin...
Chemistry of Submerged Soils
K cl in_fertigation
Submerged soil chemistry and management
waterlogged soils
CHAPTER4.DOC
LIME REQUIREMENT AND LIMING MATERIALS FOR ACIDIC SOIL
Subsurface 1D Transport of Dioxin Beneath An Uncontrolled Dump Site - A Case ...
Soil organic carbon analysis techniques
Soil Potassium
pH and its effects on nutrient availablity
Phosphate fixation
Acidic,Salic, And Alkali Soils
Naresh gohil
Hydrogeochemistry and Microbiology of Wadi Al Bih Limestone Aquifer in Northe...
Chemistry of submerged soils re
Problem soils and soil acidity, P K MANI
Ad

Viewers also liked (10)

PPT
Comm 309
PPTX
Cubo y cilindro
PPTX
PDF
How To Maintain Soft And Glowing Skin During The Winter Months
DOCX
PPF Family Office
DOC
Bhupesh_Resume
PPT
Introducing me older kids
PDF
Kids united
PDF
Удмуртия-текст
PPT
Social context of language learning
Comm 309
Cubo y cilindro
How To Maintain Soft And Glowing Skin During The Winter Months
PPF Family Office
Bhupesh_Resume
Introducing me older kids
Kids united
Удмуртия-текст
Social context of language learning
Ad

Similar to ABSTRACT.RTF (20)

DOC
CHAPTER5.DOC
DOC
CHAPTER1.DOC
RTF
RTF
REFERENC.RTF
RTF
INTRODUC.RTF
RTF
PDF
Soil quality parameters in ferralsols teixeira 2002
PDF
Assessment of fe(ii), fe(iii) and al(iii) in a mineralogical profile of gabon...
RTF
PDF
Acid soil indicators in forest soils.pdf
PDF
Variability in the Physico-chemical Properties of Soils of Similar Lithology ...
PDF
Variability in the Physico-chemical Properties of Soils of Similar Lithology ...
PPT
Chemical & Microbial analysis of farm & forest soil
PDF
E03401029034
PDF
Fertility Levels of Soils under Selected Tree Vegetations for Efficient Agro-...
PDF
A comparative study of the physical and chemical properties of soils under di...
PDF
Eko 2014-0006
PDF
Justin Beslity -Thesis
PDF
D0411315
PDF
Restoring Degraded Land after Oil, Gas and Mining Operation
CHAPTER5.DOC
CHAPTER1.DOC
REFERENC.RTF
INTRODUC.RTF
Soil quality parameters in ferralsols teixeira 2002
Assessment of fe(ii), fe(iii) and al(iii) in a mineralogical profile of gabon...
Acid soil indicators in forest soils.pdf
Variability in the Physico-chemical Properties of Soils of Similar Lithology ...
Variability in the Physico-chemical Properties of Soils of Similar Lithology ...
Chemical & Microbial analysis of farm & forest soil
E03401029034
Fertility Levels of Soils under Selected Tree Vegetations for Efficient Agro-...
A comparative study of the physical and chemical properties of soils under di...
Eko 2014-0006
Justin Beslity -Thesis
D0411315
Restoring Degraded Land after Oil, Gas and Mining Operation

More from David Sugarman (14)

PPSX
HLS cctv safe city / Transportation report david sugarman
DOCX
Cv david sugarman
RTF
TABLE3-1.RTF
DOC
CHAPTER2
RTF
TITLE.RTF
RTF
ACKNOWLE.RTF
PPS
Ace.Final Presentation.Team7
PDF
About us and about you
PPT
mdlog.PPT
PPT
אורקל חדש
PPS
CellNets MTN
PPS
CellNets Vodacom
PPT
presentation to an operator
HLS cctv safe city / Transportation report david sugarman
Cv david sugarman
TABLE3-1.RTF
CHAPTER2
TITLE.RTF
ACKNOWLE.RTF
Ace.Final Presentation.Team7
About us and about you
mdlog.PPT
אורקל חדש
CellNets MTN
CellNets Vodacom
presentation to an operator

ABSTRACT.RTF

  • 1. ABSTRACT It is widely accepted that afforestation adversely affects soil chemical properties. A significant decrease in pH, base cation status and acid neutralising capacity (ANC), coupled with increasing acidity have been observed to occur in acid coniferous forest soils both in the Northern and Southern Hemispheres. International and local studies in Southern Africa have observed declining productivity over successive rotations in pine plantations. Increasing acidity loads in the Northern Hemisphere and their adverse effects on forest health have generated a search for chemical indices that would assist in pursuing thresholds beyond which forest vitality is damaged. A common and widely used chemical index is the Ca/Al ratio. The most common parameter adopted is the Ca/Al molar ratio in soil solutions. Recent studies in Southern Africa (Swaziland, Kwazulu- Natal) and in the Sabie area (Eastern Escarpment) have indicated that some forest compartments (Pinus sp.) may experience Ca/Al molar ratios dropping below unity. The value of unity is widely used and proposed as a threshold beyond which tree vitality may be adversely affected. This study was conducted to determine the state of surface (0-20cm) soils underlying pine plantations of different ages in the Sabie area on the Eastern Escarpment of Southern Africa. The pine plantations were selected in areas overlying a uniform bedrock (shale), high altitude, high rainfall, north facing aspect and confined to 3 pine species (P. elliottii, P. patula and P. taeda). A composite sample was taken from each of 22 forest compartments varying in age (between 22 and 67 years) and rotation (first, second and third). In addition, the results of previous investigations of forest soils in the Eastern Escarpment region were considered in order to expand the array of forest compartment ages and the size of the overall data set used for statistical analysis, so that comparisons could be made. Prior to analysis the soils were air dried and sieved (2mm). Characterising the soil 1
  • 2. and investigation of the acidity status was conducted by analysis of pH (in water and KCl), organic carbon, acid neutralising capacity and exchangeable acidity and basic cations. All the pine forest surface soils are highly acidic. The acidification of natural soils under grassland is enhanced by afforestation and increases with increasing period of afforestation, predominantly within the first two decades. The pH levels (3.7-4.1 in KCl) dropped markedly in surface soils in the first two decades following afforestation. KCl-extractable acidity was observed to decline in a similar way for the first two decades. There is some indication of further acidification with plantation age beyond two decades, although the effect is not significant. Base saturation levels do not exceed 25%, and exhibit a general drop in respect to afforestation of grassland soils. The depletion of basic cations (BC) from the exchange sites is evident as shown by a decline in the BC/acidity ratio, to values below unity, predominantly in the first decade following afforestation. High levels of organic carbon were detected in the surface soils of the pine plantations studied (3.7-10%). The presence of organic matter is important in the context of Al complexation, which was confirmed by a significant correlation (r2 =0.59) between CuCl2-extractable Al and organic carbon. Soil solution composition was estimated based on the analysis of saturated paste extracts. The analysis included determination of pH (in the paste and in the extract), electrical conductivity (EC), dissolved organic carbon (DOC), monomeric Al, monomeric silica and major cations and anions. In addition, geochemical modelling (MINTEQA2) was used to calculate ion activities and saturation indices. Similarly to the solid phase, the soil solution was highly acidic with pH (saturated paste) levels ranging from 4.36 to 4.91. An important observation, and of utmost importance for future studies, was that of declining ionic strength of the soil solution with increasing plantation age (r2 =0.59). Additional interesting observations were made of unexpectedly high levels of fluoride in solution (1.9-12 mg/l), which altered the detection of Al3+ and Al(OH)X 3-X 2
  • 3. concentrations in solution, and the calculation of alumino-silicate mineral solubility equilibria. The colorimetric method used for the detection of monomeric Al in solution probably excludes, to a large extent, F-complexed Al thus, posing great difficulty in the calculation of F-free monomeric Al activity in solution. Consequently, a more realistic approach was considered. In the process of calculating monomeric Al activities in solution (using MINTEQA2), the fluoride concentrations were thus, excluded. The inclusion of F in geochemical speciation calculations has indicated that the majority of Al species in solution are complexed to F and in addition, produced inconsistencies with respect to saturation indices of gibbsite, kaolinite and jurbanite. Evaluating the dissolution of Al in the absence of F offers the possibility that the dissolution of Al is controlled by Al-OM complexes (under pH 4.7) and by gibbsite (above pH 4.7). The Ca/Al molar concentration ratio in solution was observed to drop in the soils following afforestation, and to reach, in some cases, levels below unity thus suggesting, that at some future time, forest health may be adversely affected. Ca/Al activity ratios calculated in the presence of F, were more than five orders of magnitude higher than activity ratio calculated in the absence of F. High concentrations of NH4 + were detected in solution (4.8-36.5 mg/l) while other soluble forms of nitrogen were detected in significantly lower concentrations (NO2 - 4 mg/l; NO3 - - mostly undetected). The Abundance of NH4 + -N coupled with smaller concentrations of NO2 may be the cause of the method used for the preparation of the saturated soil pastes and consequently interruption of biochemical processes such as nitrification taking place in the soil environment. Alternetively, the reason may be the loss of nitrogen from the F and H horizons (forest floor) to the upper mineral horizon in the form of NH4 + -N, whereas the loss of nitrogen from the A horizon is mainly in the form of NO3-N. High levels of dissolved organic carbon (DOC) were detected (53-193mg/l) and conform to the abundance of organic matter. A considerable anion deficit with respect to the charge balance of major ions in solution was assumed to be accounted for by negatively charged dissolved organic matter. 3
  • 4. Comparing the Ca/Al ratio of the soil solution to the basic cations/acidity ratio of the exchange sites reveals similar trends (r2 =0.37 and r2 =0.39, respectively) with plantation age. As with acidity and pH, the Ca/Al ratio drops markedly in the first two decades following afforestation. Thus, strengthening the argument that the most prominent chemical changes in surface soils of these pine plantations occur within the first 20 to 30 years after the grasslands soils have been planted to trees. 4