Effects of salicylic acid-grafted bamboo hemicellulose on gray mold control in blueberry fruit: The phenylpropanoid pathway and peel microbial community composition

Du, Rongyu; Deng, Jia; Huang, Eric; Chen, Lin; Tang, Junrong; Liu, Yun; Shi, Zhengjun; Wang, Fang

doi:10.1016/j.ijbiomac.2023.126303

Cited by 5 publications

(2 citation statements)

References 53 publications

Supporting

Mentioning

Contrasting

Order By: Relevance

“…45 The last-stage weight loss from 506.32 to 900 K is ascribed to the carbonization of the residual components of the adsorbents. 46 The final weight losses of AP, AP-G1.0-AMP, and AP-2.0-AMP are 70.1, 67.6, and 66.2%.…”

Section: ■ Results and Discussionmentioning

confidence: 96%

“…The pyrolysis of cellulose, hemicelluloses, and part of the PAMAM dendrimers causes the second-stage weight loss of the biosorbents from 373.15 to 506.32 K, accounting for 3.56 and 3.42% of the weight loss . The last-stage weight loss from 506.32 to 900 K is ascribed to the carbonization of the residual components of the adsorbents . The final weight losses of AP, AP-G1.0-AMP, and AP-2.0-AMP are 70.1, 67.6, and 66.2%.…”

Section: Resultsmentioning

confidence: 99%

See 1 more Smart Citation

Synthesis of Aminomethylpyridine-Decorated Polyamidoamine Dendrimer/Apple Residue for the Efficient Capture of Cd(II)

Cong,

Wu,

Wang

et al. 2024

Langmuir

View full text Add to dashboard Cite

Water contamination irritated by Cd(II) brings about severe damage to the ecosystem and to human health. The decontamination of Cd(II) by the adsorption method is a promising technology. Here, we construct aminomethylpyridinefunctionalized polyamidoamine (PAMAM) dendrimer/apple residue biosorbents (AP-G1.0-AMP and AP-G2.0-AMP) for adsorbing Cd(II) from aqueous solution. The adsorption behaviors of the biosorbents for Cd(II) were comprehensively evaluated. The maximum adsorption capacities of AP-G1.0-AMP and AP-G2.0-AMP for Cd(II) are 1.40 and 1.44 mmol•g −1 at pH 6. The adsorption process for Cd(II) is swift and can reach equilibrium after 120 min. The film diffusion process dominates the adsorption kinetics, and a pseudo-second-order model is appropriate to depict this process. The uptake of Cd(II) can be promoted by increasing concentration and temperature. The adsorption isotherm follows the Langmuir model with a chemisorption mechanism. The biosorbents also display satisfied adsorption for Cd(II) in real aqueous media. The adsorption mechanism indicates that C−N, N�C, C−O, CONH, N−H, and O−H groups participate in the adsorption for Cd(II). The biosorbents display a good regeneration property and can be reused with practical value. The as-prepared biosorbents show great potential for removing Cd(II) from water solutions with remarkable significance.

show abstract

Section: ■ Results and Discussionmentioning

confidence: 96%

Section: Resultsmentioning

confidence: 99%