Compost has been used to stabilise lead (Pb) in soil. However, compost contains a high level of dissolved organic matter (DOM) which may make Pb bioavailable in plant and thereby limiting its effectiveness and application. Addition of biochar to compost can reduce this effect. Rice husk (RH) and Cashew nut shell (CNS) biochars and compost-modified biochars were used in comparison to compost for stabilizing Pb in lead smelting slag (LSS)-contaminated soil (Pb = 18,300 mg/kg) in Nigeria. Efficiency of Pb stabilisation in control and amended soils was assessed using CaCl2 batch leaching experiment and plant performance. In pot experiments, maize plant was grown on the contaminated soil and on soil treated with minimum and optimum doses of the amendments singly and in combination for 6 weeks. Agronomical and chemical parameters of the plants were measured. CaCl 2-extractable Pb in the untreated soil was reduced from 60 mg/kg to 0.55 mg/kg in RHB amended soils and non-detectable in other amended soils. RH-biochar/compost increased plant height, number of leaf and leaf area more than the others. Similarly, at minimum rate, it reduced root and shoot Pb by 91% and 86.0% respectively. Compost-modified rice husk biocharstabilised Pb in lead smelting slag contaminated soil reduced Pb plant uptake and improved plant growth. Lead stabilisation through the use of rice husk biochar with compost may be a green method for remediation of lead smelting slag-contaminated soil.
A high concentration of lead in soil that is contaminated by lead slag is dangerous to man and the ecosystem. The level of Pb above background concentrations in soil affects soil fertility, plant and animal health. High levels of Pb in soil can alter biomass of soil microbes and their activities in nutrient recycling. They can also cause plant physiological disturbances such as oxidative stress and reduction in plant yield [
There are reports of soil contamination with Pb in many parts of the world that are known with mining and lead-acid battery recycling activities [
Studies have shown that remediation of Pb-impacted soil using compost stabilizes heavy metals, restores soil fertility and promots plant health on the remediated soils [
Previous research on heavy metals stabilisation in soil by organic wastes was mainly with the use of compost [
The soil sample for this study was randomly collected from an abandoned lead smelting slag contaminated site in Ibadan, Nigeria. The site lies between longitude 7˚24'N and latitude 4˚00'E at an elevation of 174 m above sea level. The large expanse of agricultural land in this area has been made unproductive due to the impact of the LSS illegally dumped on the land several years ago. Soils were sampled at different points at 15 cm depth and mixed to form composite sample which was transported to the laboratory.
The biochars were produced from rice husk and cashew nut shell. These agricultural residues were chosen due to their abundance in Nigeria and in other places in the world. Their use as biochar sources will minimise the problem of managing their waste. Compost was prepared from wild sunflower (Tithoniadiversifolia) and poultry liter in ratio 3:1 of sunflower to poultry manure for 12 weeks [
The soil samples were air-dried at room temperature for two weeks, mechanically ground and sieved to <2 mm. The <2 mm fraction soil samples were analysed for physicochemical parameters. Organic carbon was determined using potassium dichromate method [
0.01 M CaCl2 batch leaching experiment was conducted to optimize Pb stabilisation potentials of biochars,
Parameters | Contaminated soil | Biochars | Compost | |
---|---|---|---|---|
Rice husk | Cashew nut shell | |||
pH | 5.70 | 7.40 | 6.30 | 8.70 |
TOC | 1.80 | - | - | - |
Sand (%) | 43 | - | - | - |
Silt (%) | 59 | - | - | - |
Clay (%) | 9 | - | - | - |
N (mg/kg) | 600 | 13,200 | 23,000 | 9600 |
Ca (mg/kg) | 213 | 9780 | 5340 | 29,000 |
Mg (mg/kg) | 86 | 3530 | 135 | 4540 |
P (mg/kg) | 71.5 | 197 | 107 | 2090 |
K (cmol/kg) | 0.46 | 12.4 | 2.80 | 21.9 |
CEC (cmol/kg) | 4.62 | 110 | 36.9 | 210 |
Pb (mg/kg) | 18,300 | 0.90 | 1.20 | 1.50 |
-Not available, TOC―Total organic carbon content, CEC―Cation exchange capacity.
compost and compost-modified biochars in terms of the amount added to the contaminated soil. 0.0 g (contaminated soil without amendment), 0.05 g, 0.1 g, 0.2 g, 0.4 g of each biochar and compost was added singly and in combination with compost to 1.00 g of contaminated soil in 50 mL polycarbonate centrifuge tube. 5 mL of 0.01 M CaCl2 solution was added and the solution was shaken for 2 hrs at 160 rpm using an orbital shaker, after which the solution was filtered using Whatman filter paper No. 2. The filtrates were analysed for Pb concentration using atomic absorption spectrophotometer (Buck scientific model 210A). The percent stabilisation efficiencies of the amendments were calculated.
Pot experiment was set up in a greenhouse to study the effect of biochars and compost both singly and in combination (equal proportion by weight using the minimum dose) on soil Pb stabilisation, maize plant growth and Pb accumulation. For comparison, the most effective dose (0.4 g) and the minimum dose (0.05 g) of the amendments from the batch leaching test were selected for the pot experiment. The amount of biochars and compost required were calculated with regards to the amount of soil used for planting (500 g) based on the results of the optimisation. This was equivalent to 25 g (50 g for combination) and 200 g of amendment per 500 g of soil to represent 0.05 and 0.4 g amendment/g soil rates respectively. Altogether there were 9 treatments and each treatment was performed in duplicate, giving a total of 18 bags. No extra macronutrient treatment from external source was applied to the soils.
The amendments were thoroughly mixed with the soils and transferred into 30 cm diameter polyethylene bags. Each bag was placed in a plastic bowl to prevent loss of leachate from the system and water was applied to each bag until soil reached 70% water holding capacity after which they were allowed to equilibrate for one week. During the period of one week the bags were watered every two days (approximately 100 - 200 mL). After one week, the soil was sown with two maize seeds but the survival of the seedlings to the end of the experiments was dependent on the type and rates of the amendments. Watering of the plants was done at two days intervals. The leachate collected in each saucer was also returned to the experimental soil when necessary to prevent loss of the metal. At six weeks of planting, agronomical parameters such as plant height, number of leaves and leaf area were taken. After 6 weeks, plants were harvested. The roots of the maize plants were washed with distilled water to remove soil, the plant were separated into shoot and root and oven-dried for 3 days at 80˚C. The dry biomass was determined. After biomass determination, the oven-dried plant parts were ground. Depending on the root dry weight of the plant ≤ 1.00 g of each was ashed in a muffle furnace for 6 hours at a temperature between 450˚C - 500˚C for Pb determination [
The physico-chemical properties of the soil, biochars and compost are
The pH of CNSB is slightly acidic (6.30) compared to the pH of rice RHB and compost which are alkaline. The acidic pH of CNSB can be attributed to its anacardic acids content [
The control and the amended soils at the different doses were subjected to 0.01 M CaCl2 solution extraction to determine extractable Pb. The extractable Pb was highly dependent on the dose and the amendment type. The results are summarized in
As can be observed, increase in amendments doses from 0.05 to 0.4 g/g soil decreased the extractable Pb concentrations from 60 mg/kg in the control soil to non-detectable levels in the Compost, CNSB, Compost- modified biochars and to 0.55 mg/kg in the RHB treated soils.
To evaluate the efficiency of the treatments on the stabilisation of Pb in the soil and bioavailability in plant, maize plants were grown for six weeks on the untreated and treated soils. It must be noted that although maize plant would not generally be considered as appropriate plant to evaluate treatment efficiency, it was used because it is a known lead accumulator [
Maize growth was enhanced by the amendments except with higher rate of CNSB. There are variations in the mean plant height, number of leaves and leaf area ranging from 40 ± 11 to 90 ± 1 cm, 2 ± 1 to 8 ± 1 and 70 ± 8 to 280 ± 11 cm2 respectively among the plants grown on the soils. From the results, evidence of stunted growth perhaps due to Pb toxicity and the acidic nature of the soil were observed with plants grown on the control soil and the soil treated with higher rates of CNSB.
Plants grown on the soil that was amended with higher rate of CNSB showed mean height of 40 cm compare with 50 cm in the control, 2 leaves compared with 3 leaves in the control and an area of 70 cm2 compared with 86 cm2 in the control. The condition did not improve with addition of compost at this rate.CNS biocharis acidic as shown in
The response of maize plant in terms of root and shoot dry biomass is presented in
amendment type and rate, compost alone promoted the highest root and shoot biomass. For all other treatments, with the exception of CNSB at the rate of 200 g/500g the root and shoot biomass yields were higher than those of the control plant.
Cashew nut shell biochar at the highest rate (200 g/500g) produced the least root (0.1) and shoot (0.25) biomass values. However, addition of compost to the CNSB even at a lower rate (50 (1:1) g/500g) improved the performance of the biochar with 0.65 root and 1.45 shoot biomass values. The observed less performance of the CNSB may be associated with its acidic nature, the condition which is not favourable for plant growth. Unlike CNSB, the pH values of both compost (8.70) and RHB (7.40) are alkaline. The observed desirable performance of compost-modified CNSB may also be connected to this alkaline nature of compost which increased the pH of CNSB and therefore favours plant growth. This suggests that pH of the biochar is an important factor to consider when developing biochar remediation of heavy metals contaminated soils.
The concentrations of Pb measured in soil, maize plant root and shoot after harvesting are shown in
Treatments | Post-Harvest Soil | Root | Shoot |
---|---|---|---|
Control | 15,340 | 2260 | 530 |
C1 | 8650 | 950 | 390 |
C2 | 8250 | 650 | 210 |
RHB1 | 12,200 | 410 | 120 |
RHB2 | 9100 | 400 | 100 |
RHB1/C1 | 9800 | 200 | 74 |
CNSB1 | 12,750 | 500 | 140 |
CNSB2 | 9950 | 450 | 190 |
CNSB1/C1 | 10,600 | 260 | 100 |
CNSB = Cashew nut shell biochar; RH B = Rice husk biochar; C = Compost.
Total soil Pb content was reduced from 15,340 mg/kg in the control soil after harvesting to concentrations which ranged from 8250 (C2) to 12,750 mg/kg (CNSB1) in the treated soils.
Similarly, total root Pb content was reduced from 2260 mg/kg to concentrations which ranged from 200 (RHB1/C1) to 950 mg/kg (C1). Furthermore, total shoot Pb content was reduced from 530 mg/kg to concentrations which ranged from 74 (RHB1/C1) to 390 mg/kg (C1). The results demonstrate that compost performed best in terms of stabilisation of Pb in soil while the compost-modified biochars particularly mixture of rice husk biochar and compost at lower rate performed better at reducing Pb available in maize plant. This was followed by the two biochars when used singly. The soil Pb levels in soil amended with higher rates (200 g/500g) of compost and amendments were the least. This perhaps was due to dilution effect which high rate of amendment could produce on the contaminant in soil [
The observed decrease in the concentration of Pb in the soil, plant root and shoot may be associated with some inherent factors of the different amendments which changed the chemistry of the soil. The factors among others include the pH, organic matter and the chemical components of the amendments.
Sabilisation of Pb in soil can be achieved through adsorption, complexation and precipitation which are influenced by the pH, dissolved organic carbon (humic substances) and mineral components of the amendments and soil respectively. At lower pH of the soil, there is an increase in the H+ ion concentrations and it is expected that H+ ion will compete with adsorption of Pb on the surface of the amended soil, thus decreasing stabilisation of Pb in the soil. At high pH, OH-ion increases which favours soil stabilisation of Pb. The acidic to near neutral pH (6.30) of CNSB coupled with acidity (pH = 5.70) of the soil implies competition of H+ with Pb on the surface of the CNSB amended soil, hence less Pb stabilisation. On the other hand, addition of compost and RHB to the soil was expected to increase the pH of the soil due to their alkaline pH, implying an increase in the negative sites of the soil which favoured Pb stabilisation.
Compost and biochars contain dissolved organic matter (humic and fulvic acids) which also possibly enhanced stabilisation of Pb in soil. High ability of Pb to form more stable coordination complexes with humicacids has been documented [
Inorganic chemical composition of the amendments perhaps also played a important role in the stabilisation of Pb in the soil and uptake by plant. As presented in
The results of uptake of Pb in maize plant grown both on the control and amended soils are shown in
The physico-chemical parameters of compost, rice husk biochar and to an extent cashew nut shell biochar present them as non-toxic, potential soil fertilisers and heavy metal immobilising agents. There are substantial observable reductions in extractable Pb concentrations in Pb smelting slag contaminated soil, maize plant root and shoot following the application of compost, rice husk and cashew nut shell biochars and compost-modified biochars. The combined effects of nutrient holding capacities of compost and RHB on making the contaminated soil fertile yield healthier plants. The extent of stabilisation might have been controlled by pH, organic matter and the chemical components of the amendments. Application of compost was the best in lowering Pb in soil while compost-modified RH-biochar was the best in lowering uptake by maize plant. Cashew nut shell performed less both in stabilsation of Pb in soil and plant uptake especially when applied singly. The observed less performance of the CNSB may be associated with its acidic nature, the condition which is unfavourable to plant growth. This suggests that the pH of biochar is an important factor to consider when developing biochar remediation of heavy metals contaminated soils. Combination of compost with biochar could be a very effective way of decontaminating and re-vegetating lead smelting slag-contaminated soil. There is a need for further studies on optimisation of the use of compost modified-biochar in the contaminated soil, its effects on other minor quantities of heavy metals that may be contained in the soil, its mechanism of heavy metals stabilization in soil and field applications.
Mary B.Ogundiran,Olamide O.Lawal,Sifau A.Adejumo, (2015) Stabilisation of Pb in Pb Smelting Slag-Contaminated Soil by Compost-Modified Biochars and Their Effects on Maize Plant Growth. Journal of Environmental Protection,06,771-780. doi: 10.4236/jep.2015.68070