Control of lead solubility in soil contaminated with lead shot: effect of soil moisture and temperature

Soil Research ◽  
2009 ◽  
Vol 47 (3) ◽  
pp. 296 ◽  
Author(s):  
R. G. McLaren ◽  
C. P. Rooney ◽  
L. M. Condron

An incubation experiment was carried out to assess the rate of oxidation of lead (Pb) shot and subsequent transfer of Pb to the soil under different soil moisture and temperature regimes. Lead was readily released from Pb shot into the soil environment due to rapid corrosion of the Pb shot; however, the rate of Pb shot dissolution was slower at 70% than at 100% field moisture capacity. The corrosion and development of crust material on Pb shot, and corresponding increases in soil solution Pb and Pb associated with the soil solid phase, were also slower at 10°C than 25 or 30°C. Soil moisture and temperature also influenced the speciation of soil solution Pb as modelled using WHAM 6, mainly through the effects of moisture and temperature on soil pH, total soluble Pb, and dissolved organic C. The rate of approach to equilibrium of the Pb shot–soil–soil solution system will be much slower where soil moisture and temperature limit Pb shot corrosion. Calculated free ion Pb2+ concentrations suggest that after 6 months, almost all samples contaminated with Pb shot exceeded soil critical limits for Pb toxicity.

2020 ◽  
Vol 10 ◽  
Author(s):  
Cristina Eimil-Fraga ◽  
Roque Rodríguez-Soalleiro ◽  
María José Fernández-Sanjurjo ◽  
Esperanza Álvarez-Rodríguez

The influence of plantation age on the chemical properties of acidic soils was studied in 16 plots in adult <em>Pinus pinaster</em> stands established in Galicia (NW Spain). The Al fractions in the soil solid phase and the total Al in soil solution were determined in the upper soil layer (0-20 cm) and the lower soil layer (20-40 cm) in each plot. The pH, total C and N, exchangeable Ca, Mg, Na, K, and Al and Al saturation (% Al) were determined in the solid fraction. Aluminium was extracted from the solid phase with the following solutions: ammonium oxalate (Al<sub>o</sub>), sodium pyrophosphate (Al<sub>p</sub>), copper chloride (Al<sub>cu</sub>) and ammonium chloride (Al<sub>NH4</sub>). The total Al in the liquid phase was also determined. All soil chemical parameters, except total N, C/N ratio and % Al, were significantly influenced by soil depth. The mean pH was lower in the upper than in the lower layer (4.57 vs. 4.97), but the opposite was observed for the organic C (77.2 vs. 50.4 g kg<sup>-1</sup>), the effective cation exchange capacity (eCEC) (9.43 vs. 6.25 cmol<sub>(+)</sub> kg<sup>-1</sup>), P (8.95 vs. 4.65 mg kg<sup>-1</sup>) and the exchangeable cations. Organic matter, total N and eCEC were significantly and positively correlated with plantation age (r = 0.69 in the upper layer and r = 0.82 in the lower layer, p &lt; 0.01; r = 0.62, p &lt; 0.05 in the upper layer and r = 0.78, p &lt; 0.01 in the lower layer; r = 0.77, p &lt; 0.01 in the upper layer and r = 0.85, p &lt; 0.0001 in the lower layer, respectively), and pH<sub>KCl</sub> was negatively correlated with plantation age (r = -0.55 in the upper soil layer and r = -0.61 in the lower soil layer, p &lt; 0.05). The concentrations of the different Al forms in all soils decreased in the order Al<sub>p </sub>&gt; Al<sub>o </sub>&gt; Al<sub>cu </sub>&gt; Al<sub>NH4</sub>. Highly stable organo-aluminium complexes (Al<sub>p-cu</sub>) predominated over moderate and low stability complexes (Al<sub>cu</sub>) in all soil plots. The highly stable organo-Al complexes were significantly more abundant in the lower layer, whereas the opposite was observed for the exchangeable Al and the total Al in soil solution. The concentrations of all Al forms (except Al<sub>p-cu</sub>) were significantly and positively correlated with plantation age (Al<sub>o</sub> r = 0.50, p &lt; 0.05 for the upper layer and r = 0.67, p &lt; 0.01 for the lower layer; Al<sub>p</sub> r = 0.64, p &lt; 0.01 for the lower layer; Al<sub>cu </sub>r = 0.84 for the upper layer and r = 0.83 for the lower layer, p &lt; 0.0001; Al<sub>cu-NH4</sub> r = 0.65 for the upper layer and r = 0.78 for the lower layer, p &lt; 0.01; Al<sub>NH4</sub> r = 0.76, p &lt; 0.01 for the upper layer and r = 0.84, p &lt; 0.0001 for the lower layer; total Al in soil solution r = 0.61 for the upper layer and r = 0.60 for the lower layer, p &lt; 0.05). Stepwise linear regression analysis showed that plantation age, pH and total C explained between 67% and 93% of the variance in the Al forms. In all regression models, plantation age was a significant predictor variable for the different Al fractions, except total soluble Al, which is an important variable to consider in the study of chemical properties in forest soils.


2002 ◽  
Vol 37 (C1) ◽  
pp. C1-259-C1-264 ◽  
Author(s):  
G. Sokolik ◽  
S. Ovsiannikova ◽  
I. Kimlenko

Soil Research ◽  
1994 ◽  
Vol 32 (2) ◽  
pp. 269 ◽  
Author(s):  
NW Menzies ◽  
LC Bell ◽  
DG Edwards

Soil solid phase and soil solution characteristics were evaluated on surface and subsoil horizons of 60 acid, highly weathered soils in the unamended state, and on a subset of 39 surface horizons following the addition of CaSO4.2H2O. The activity of Al3+ Was found to be strongly correlated with the soil solution pH, with Al3+ activity increasing as pH decreased. For surface soils in the unamended state, and for the majority of subsoils, the Al3+ activity calculated was comparable to the theoretical activity supported by the dissolution of gibbsite (Al2O3.3H2O). The Al3+ activity in CaSO4.2H2O-amended samples tended to fall below that maintained by gibbsite dissolution and was more closely correlated with the Al3+ activity supported by the dissolution of jurbanite (AlSO4 (OH).5H2O).


2002 ◽  
Vol 31 (1) ◽  
pp. 162 ◽  
Author(s):  
S. H. Badawy ◽  
M. I. D. Helal ◽  
A. M. Chaudri ◽  
K. Lawlor ◽  
S. P. McGrath

2002 ◽  
Vol 31 (1) ◽  
pp. 162-167 ◽  
Author(s):  
S. H. Badawy ◽  
M. I. D. Helal ◽  
A. M. Chaudri ◽  
K. Lawlor ◽  
S. P. McGrath

Coatings ◽  
2021 ◽  
Vol 11 (6) ◽  
pp. 625
Author(s):  
Lijuan Chen ◽  
Bo Wei ◽  
Xianghong Xu

The influence of sulfate-reducing bacteria (SRB) on the corrosion behaviors of X80 pipeline steel was investigated in a soil environment by electrochemical techniques and surface analysis. It was found that SRB grew well in the acidic soil environment and further attached to the coupon surface, resulting in microbiologically influenced corrosion (MIC) of the steel. The corrosion process of X80 steel was significantly affected by the SRB biofilm on the steel surface. Steel corrosion was inhibited by the highly bioactive SRB biofilm at the early stage of the experiment, while SRB can accelerate the corrosion of steel at the later stage of the experiment. The steel surface suffered severe pitting corrosion in the SRB-containing soil solution.


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