Bernhard Wehr

Dr. Bernhard Wehr

orcid

Research Focus & Metrics

Academic Career Length

23Years (2004-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 June 2004 in Plant Physiology and Biochemistry
Verified
Journal Article
Closed access
BWBernhard Wehr
Bernhard Wehr
NMNeal WIlliam Menzies
Neal WIlliam Menzies
FBF.Pax C. Blamey
F.Pax C. Blamey

1 December 2021 in Journal of Food Composition and Analysis
Verified
Journal Article
Closed access
Binh NguyenBinh Nguyen
Binh Nguyen
HHH.T. Hong
H.T. Hong
TOT.J. O’hAre
T.J. O’hAre
BWBernhard Wehr
Bernhard Wehr
NMN.W. Menzies
N.W. Menzies
SHStephen Mark Harper
Stephen Mark Harper

3 March 2023 in SOIL
Verified
Journal Article
Open access
PDF file
SNSara Niaz
Sara Niaz
BWBernhard Wehr
Bernhard Wehr
RDRam C. Dalal
Ram C. Dalal
PKPeter Martin Kopittke
Peter Martin Kopittke
NMNeal W. Menzies
Neal W. Menzies
In the natural environment, soils undergo wetting and drying (WD) cycles due to precipitation and evapotranspiration. The WD cycles have a profound impact on soil physical, chemical, and biological properties and drive the development of structure in soils. Degraded soils are often lacking structure, and the effect of organic amendments and WD cycles on structure formation of these soils is poorly understood. The aim of this study was to evaluate the role of biotic and abiotic factors on aggregate formation and stabilization of sodic soils after the addition of gypsum and organic amendments (feedlot manure, chicken manure, lucerne pallets, and anionic poly acrylamide). Amended soils were incubated at 25 ∘C over four WD cycles, with assessment of soil microbial respiration, electrical conductivity, pH, sodium adsorption ratio (SAR), aggregate stability in water (ASWAT), aggregate size distribution, and mean weight diameter. Our results demonstrate that WD cycles can improve aggregate stability after the addition of amendments in sodic Vertisols, but this process depends on the type of organic amendment. Lucerne pellets resulted in highest soil microbial respiration, proportions of large macroaggregates (>2000 µm), and mean weight diameter. In contrast, dispersion was significantly reduced when soils were treated with chicken manure, whilst anionic polyacrylamide only had a transient effect on aggregate stability. When these organic amendments were applied together with gypsum, the stability of aggregates was further enhanced, and dispersion became negligible after the second WD cycle. The formation and stability of small macroaggregates (2000–250 µm) was less dependent on the type of organic amendments and more dependent on WD cycles as the proportion of small macroaggregates also increased in control soils after four WD cycles, highlighting the role of WD cycles as one of the key factors that improves aggregation and stability of sodic Vertisols.

9 April 2010 in Journal of Agricultural and Food Chemistry
Verified
Journal Article
Closed access
BWBernhard Wehr
Bernhard Wehr
FBF. P. C. Blamey
F. P. C. Blamey
JHJ. V. Hanna
J. V. Hanna
PKPeter Martin Kopittke
Peter Martin Kopittke
GKG. L. Kerven
G. L. Kerven
NMNeal WIlliam Menzies
Neal WIlliam Menzies

26 March 2010 in Journal of Agricultural and Food Chemistry
Verified
Journal Article
Closed access
BWBernhard Wehr
Bernhard Wehr
FBF. Pax C. Blamey
F. Pax C. Blamey
NMNeal WIlliam Menzies
Neal WIlliam Menzies

31 January 2017 in Journal of Forest Research
Verified
Journal Article
Closed access
BWBernhard Wehr
Bernhard Wehr
TSTim E. Smith
Tim E. Smith
NMNeal WIlliam Menzies
Neal WIlliam Menzies
The establishment and early growth of a clonal teak plantation on a leached and acidic alluvial soil on North Queensland, Australia was studied over 18 months. The soil was treated with three lime treatments (0, 1 and 2 Mg ha−1) and three CaCl2 treatments (0, 50 and 100 kg ha−1). After 18 months, the average tree height ranged from 105 to 227 cm and survival ranged from 39% to 97%. Tree height and survival was not causally affected by the lime or CaCl2 treatments. Detailed investigation of soil properties in each plot revealed teak growth and survival was positively affected by total soil carbon concentration, water-holding capacity (WHC) and Al saturation, and negatively affected by exchangeable Mg and DTPA-extractable Mn. Results indicate that teak is relatively tolerant of low pH (pH 4.4) and moderately high exchangeable Al concentrations (1 cmol(c) kg−1) in soil. We conclude that organic matter (carbon) plays a critical role at our site by improving the soil physical characteristics such as soil porosity, aggregate stability and WHC. Also, sites with high total carbon had high Al saturation of the soil and high teak growth, suggesting that soil C acts by immobilising Al and Al impairs soil C degradation. Growth may be impaired by Mn toxicity and by Mg affects on soil structure. From a teak plantation management perspective, it is desirable to select soils with high organic matter, whereas pH and Ca status have little effect on early growth.