“…Cress, lettuce and tomato seeds are used in most of the past studies due to their higher growth response and sensitivity to phytotoxic substances. Both promotion and inhibition of seed germination after mixing with biochar was observed by other studies (Margenot et al 2018;Mumme et al 2018;Rathnayake et al 2021). In our study, lettuce, germination rate was 6% higher in BC75P25 and BC25P75…”
Highlights Sawmill byproduct was used to produce biochar Addition of biochar increased the pH, EC and nutrient content in the medium The inclusion of biochar in 25% to 50% volume ratio improved plant growth parameters compared to peat-only media Higher biochar proportions in the medium diminish the physico-chemical properties and plant growth parameters
“…Cress, lettuce and tomato seeds are used in most of the past studies due to their higher growth response and sensitivity to phytotoxic substances. Both promotion and inhibition of seed germination after mixing with biochar was observed by other studies (Margenot et al 2018;Mumme et al 2018;Rathnayake et al 2021). In our study, lettuce, germination rate was 6% higher in BC75P25 and BC25P75…”
Highlights Sawmill byproduct was used to produce biochar Addition of biochar increased the pH, EC and nutrient content in the medium The inclusion of biochar in 25% to 50% volume ratio improved plant growth parameters compared to peat-only media Higher biochar proportions in the medium diminish the physico-chemical properties and plant growth parameters
“… Yuan et al (2020a) and Wang et al (2020a) upcycled waste PET plastic bottles into engineered biochar for post-combustion CO 2 capture, successfully mitigating two critical environmental issues of plastic pollution and climate change, simultaneously, and this approach was further identified as a closed carbon loop from the life-cycle perspective, which is beneficial to achieve carbon neutrality by 2050 and sustainable plastic management. Rathnayake et al (2021) studied the properties and environmental applications of biochar produced by co-pyrolyzing biomass and plastic. In their study, spent growing medium and used plastic growing bags were co-pyrolyzed at 550 °C while the plastic content in the feedstock mixture was varied among 0, 0.25, 2.5, 5 and 10%.…”
Section: Biochar Production From Plastic Wastesmentioning
“…The co-pyrolysis of biomass and different types of plastics has been frequently studied; it should be noted that most studies on this topic focused on the interactions on thermal behavior and kinetics analysis [ 10 , 11 , 12 ]. Furthermore, some studies have demonstrated that co-pyrolysis could generate a positive synergistic interaction between improving the yield and the properties of production when compared to conventional pyrolysis technology [ 13 , 14 , 15 ]. Due to the use of different species and mix ratios of feedstock and pyrolysis conditions, a variety of conclusions on the characteristics of pyrolytic production have been acquired.…”
Section: Introductionmentioning
confidence: 99%
“…Due to the use of different species and mix ratios of feedstock and pyrolysis conditions, a variety of conclusions on the characteristics of pyrolytic production have been acquired. For example, Rathnayake et al (2021) [ 14 ] found that the presence of plastic in feedstock mostly had negative effects on the C and H content of biochars derived from the spent strawberry growing medium and a mostly positive effect on those of the bean crop residue-derived biochars [ 14 ]. During pyrolysis, cellulose, hemicellulose, and lignin behave differently, and also some extent of interaction may occur, which increases the complexity of the overall process.…”
It is inevitable that reclaimed cotton stalks will contain a certain amount of plastic film due to the wide application of plastic mulching during the process of cotton cultivation, and this makes it inappropriate to return it to the field or for it to be processed into silage. In this study, biochars were prepared by the co-pyrolysis of cotton stalk with low-density polyethylene (LDPE) in the proportions of 1:0, 3:1, 2:1, and 1:1 (w/w) at 400 °C, 450 °C, and 500 °C and maintaining them for 1 h. The effects of the co-pyrolysis of cotton stalk with LDPE on the properties of biochars (e.g., pH, yield, elemental analysis, specific surface area, etc.) and the Pb(II) removal capacity were analyzed. Co-pyrolysis cotton stalks with LDPE could delay the decomposition of LDPE but could promote the decomposition of cotton stalk. At 400 °C and 450 °C, the addition of LDPE decreased the H/C ratio, while no significant difference was found between the pristine biochar and the blended biochar pyrolyzed at 500 °C. An FTIR analysis indicated that the surface functional groups of biochar were not affected by the addition of LDPE, except for CH3 and CH2. The results of the SEM showed that LDPE could cover the surface of biochar when pyrolyzed at 400 °C, while many macropores were found in the blended biochar that was pyrolyzed at 450 °C and 500 °C, thus increasing its surface area. The blended biochar that was pyrolyzed at 500 °C was more effective in the removal of Pb(II) than the cotton-stalk-derived biochar, which was dominated by monolayer adsorption with a maximum adsorption capacity of approximately 200 mg·g−1. These results suggested that the co-pyrolysis of cotton stalks and LDPE may be used to produce biochar, which is a cost-effective adsorbent for heavy metal removal from aqueous solutions.
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