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Physical damage to earthworms (Eisenia fetida, upper panel, and Lumbricus terrestris, lower panel) observed in some individuals in the high biochar application rate treatments

Physical damage to earthworms (Eisenia fetida, upper panel, and Lumbricus terrestris, lower panel) observed in some individuals in the high biochar application rate treatments

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Biochar is the degradation-resistant product generated by the pyrolysis of organic materials and is produced for the intended use of land application in order to promote carbon sequestration and soil improvement. However, despite the many potential benefits biochar application offers, it is important to quantify any ecological impacts that may resu...

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... This may lessen the BCH's effectiveness as a modifier and make the problem of weeds or pathogens having a high level of tolerance to particular pesticides or herbicides worse (Liu et al., 2018a). Additionally, in (Elliston & Oliver, 2020). Human respiratory health risks may arise from BCH nanoparticles generated during the production and transportation processes. ...
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Human activities in various fields of agriculture and industry cause an increasing amount of wastes. Proper and practical use of these wastes will reduce the pressure on the environment. Biochar (BCH) is a carbon substance generated by heating plant residue and trash in a condition with little or no oxygen. BCH’s unique qualities make it an appropriate soil amendment. BCH affects various physical properties, chemical properties, and soil biology and improves soil fertility. BCH increases the yield of plants by providing the needed elements. BCH is an increasing study field in agriculture and ecosystems, and as an energy source that is ecologically friendly and improves soil quality and health. It’s been extensively researched for its agriculture and ecological advantages, but there is little research on its structures and applications. This study attempts to present a summary of BCH’s effects on soil fertility.
... Penelitian dari Eliston & Oliver (2020), menunjukkan bahwa selain pengaruh makanan, tingginya produksi kotoran juga disebabkan oleh keanekaragaman dan perbedaan spesies cacing tanah. Produksi kotoran cacing tanah pada suatu kawasan dikaitkan dengan kondisi faktor fisika-kimia tanah, pola penggunaan lahan, kebiasaan makan, dan ketersediaan sumber makanan. ...
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... Earthworms play a vital function by enhancing plant growth through improvements in soil fertility (Elliston and Oliver 2020). Due to their ecological importance, earthworms are frequently employed as ecological indicators to evaluate the potential effects of chemicals on soil organisms (Yao et al. 2020). ...
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... Some studies have indicated, however, that excessive application of biochar to soil can have a detrimental effect on earthworms, potentially causing toxicity. Elliston and Oliver performed an earthworm avoidance experiment on Eisenia fetida using both natural soil and artificial soil [10], following a duration of more than two weeks. Eisenia fetida individuals were exposed to soil containing a 20% biochar amendment; as a result, alterations were observed in the structures of certain organisms, indicating a harmful impact of elevated biochar application rates on the test subjects. ...
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... Wine tree cuttings biochar and low tar hardwood lump charcoal increased the accumulation of PAHs in earthworms (Malev et al. 2016), leading to an increase of MDA enzymes produced by the oxidative stress response (Godlewska et al. 2021). This further corroborated the internal or external abrasion of earthworms by wheat straw biochar particles, elevated soil pH, as well as increased PAHs concentrations in both the treated soils and earthworms residing in them (Elliston and Oliver 2020). Besides the biomass feed properties, preparation protocol, pyrolysis temperature, and time also play important roles in determining the obtained biochar properties (Ippolito et al. 2020). ...
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... Species-Dependent Variations: Different earthworm species have distinct gut microbiomes and digestive processes, which can influence the elemental composition of the castings. For example, Lumbricus terrestris and Eisenia fetida, two commonly studied species, exhibit differences in nutrient cycling capabilities [67]. Dietary Influence: The elemental composition of castings is directly influenced by the earthworm's diet. ...
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... However, when the BC content in soil and aquatic environment is too high, it will threaten terrestrial and aquatic biological populations. It was reported that the high application rate of wheat straw and rice husk BC in the soil would lead to the physical injury and death of some earthworms (Elliston and Oliver 2020). In addition, Shi et al. (2021) studied the effects of BC on earthworms and showed that BC could cause weight loss in earthworms and damage the stability of the lysosomal membrane in earthworm cells. ...
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Black carbon (BC) is a carbonaceous residue produced via incomplete combustion of fossil fuels or biomass, including soot and biochar. BC is ubiquitous in the natural environment, negatively impacting human health and climate. Based on in-depth research, its positive role in removing pollutants has attracted extensive attention. First, this paper briefly summarizes the number and growth trend of BC publications from 1999 to 2022. Second, the source, migration and transformation, and detection methods of BC and its potential risks to the environment and health were introduced. Moreover, the mechanisms of BC influence on the fate and environmental effects of coexisting pollutants are summarized. This review provides a reference for understanding the sources, risks, and dynamic changes of BC and its impact on the behavior and environmental effects of coexisting pollutants. Considering the future application of BC in the environment and its important role in the carbon cycle, the following aspects require further study: (1) unifying the definition standard of BC; (2) developing more accurate and reliable methods for separating and quantifying BC than existing methods; (3) exploring methods to analyze the structural characteristics of BC, which is conducive to thoroughly studying the fate and impact on other pollutants; (4) assessing the ecological effects and mechanisms of BC of different properties (such as particle size, color, and hydrophobicity), especially long-term risk assessments, which are beneficial to the dose control and type selection of BC for environmental remediation; and (5) investigating physical and chemical properties of BC from different sources and production methods as well as the effects of environmental factors on the behavior and toxicity of coexisting pollutants, which will help regulate and improve the removal efficiency of BC for pollutants.
... Results are expressed on a v/v of fresh material basis. Two toxicity tests (Elliston and Oliver, 2019) were therefore conducted for the 0-10 mm BSRW fraction blended with either garden soil or peat. In the first test (toxicity test 1), soil (blended with 10% v/v horticultural sand) was used. ...
... The experiments were carried out in a room with controlled temperature (20-22°C). The worms were fed 2 g of cooked oats each week (Elliston and Oliver, 2019); the mortality of the earthworms was monitored for a period of 3 weeks. ...
... Although it is necessary to verify the ecotoxicological repercussion of biochar on earthworms, few studies exist in the literature (Godlewska et al. 2017;Brtnicky et al. 2021;Xiang et al. 2021). Interestingly, some authors revealed that biochar causes weight loss, a decrease in cast production, DNA damage, oxidative stress, and reproduction disruption in earthworms (Marks et al. 2016;Koltowski et al. 2017;Anyanwu et al. 2018;Zhang et al. 2019;Elliston and Oliver 2020;Kamau et al. 2020;Shi et al. 2021). However, no negative impacts were revealed in the work of Ferreira et al. (2021), who reported that passage through earthworm guts promotes biochar functionalization and that this did not negatively affect Pontoscolex corethrurus even at the highest dose (10% w/w). ...
... However, no negative impacts were revealed in the work of Ferreira et al. (2021), who reported that passage through earthworm guts promotes biochar functionalization and that this did not negatively affect Pontoscolex corethrurus even at the highest dose (10% w/w). Consequently, the effect of biochar appears dependent on its type (Zhang et al. 2017;Pokharel et al. 2020) and doses (Elliston and Oliver 2020;Han et al. 2021). More investigations are necessary to better understand the interaction between earthworms and biochar. ...
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Due to anthropogenic activities, various pollutants can be found in agricultural soil, such as cadmium (Cd) and 2,4-dichlorophenoxyacetic acid (2,4-D). They are highly toxic and can have a negative impact on soil fertility. For remediation strategies, biochar has acquired considerable attention due to its benefits for agriculture. However, we should recognize the ecological risk posed by biochar use. In addition, little is known about its non-desirable effects on soil organisms such as earthworms, especially in the case of soil remediation. In this study, earthworms (Eisenia andrei) were exposed to soil contaminated with Cd (0.7 mg/kg), (2,4-D) (7 mg/kg), and a mixture of the two in the presence and absence of biochar (2%). A 7- and 14-day incubation experiment was carried out for this purpose. Cd and 2,4-D uptakes in earthworms’ tissues, oxidative stress, cytotoxic response, DNA damage, histopathological changes, and gene expression level were assessed. Results suggested that biochar increased the bioavailability of Cd and 2,4-D and the frequency of micronuclei (MNi) and decreased the lysosomal membrane stability (LMS) in earthworms. Also, histopathological examination detected numerous alterations in animals exposed to the contaminants without any amelioration when biochar was added. The biochemical response of earthworms in terms of oxidative stress demonstrates that in the presence of biochar, animals tend to alleviate the toxicity of Cd and 2,4-D. This was also supported by transcriptomic analyses where expression gene levels related to oxidative stress were upregulated in earthworms exposed to Cd and 2,4-D + biochar. The present investigation brought new insights concerning the use of biochar in agriculture.
... These results highlight that the use of biochar for soil restoration may reduce the chance of PTEs entering the terrestrial food web through earthworms, if they are predated by higher animals (i.e. mammals, birds, reptiles and amphibians) (Elliston and Oliver, 2020). Only Sb-BAF increased for earthworms grown in the amended soils (i.e. ...
Article
This study aimed to evaluate the influence of Eisenia fetida (Savigny), added to an acidic soil contaminated with potentially toxic elements (PTEs; As, Sb, Cd, Pb, Zn) and amended with a softwood-derived biochar (2 and 5% w/w), on the mobility of PTEs and soil health (i.e. nutrient availability, enzyme activity and soil basal respiration). The PTEs bioaccumulation by E. fetida and the acute ecotoxicity effects of the amended soils were also evaluated. The interaction between earthworms and biochar led to a significant increase in soil pH, organic matter, dissolved organic carbon content, cation exchange capacity, and exchangeable Ca compared to the untreated soil. Moreover, the water-soluble and readily exchangeable PTE fraction decreased (with the exception of Sb) between 1.2- and 3.0-fold in the presence of biochar and earthworms. Earthworms, biochar, and their combination, led to a reduction of phosphomonoesterase activity which in soils amended with biochar and earthworms decreased between 2.2- and 2.5-fold with respect to the untreated soil. On the other hand, biochar and earthworms also enhanced soil basal respiration and protease activity. Although the survival rate and the weight loss of E. fetida did not change significantly with the addition of 2% biochar, adding the highest biochar percentage (5%) resulted in a survival rate that was ~2-fold lower and a weight loss that was 2.5-fold higher than the other treatments. The PTE bioaccumulation factors for E. fetida, which were less than 1 for all elements (except Cd), followed the order Cd > As>Zn > Cu > Pb > Sb and were further decreased by biochar addition. Overall, these results highlight that E. fetida and biochar, especially at 2% rate, could be used for the restoration of soil functionality in PTE-polluted environments, reducing at the same time the environmental risks posed by PTEs, at least in the short time.