ArticleEnvironmental science and pollution research international2021
Remediation potential of spent mushroom substrate on Cd pollution in a paddy soil.
Article in Environmental science and pollution research international, 2021. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 5 papers.
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Who cites it
5 citing papers in PubMed, 13 citations in OpenAlex.
- Effects of Combined Application of Mushroom Residue and Chemical Fertilizer on Greenhouse Soil Quality and Microbial Community Structure and Function.Microorganisms · 2026Article
- Enzymatic and non-enzymatic removal of organic micropollutants with spent mushroom substrate of Agaricus bisporus.Applied microbiology and biotechnology · 2024Article
- Responses of Crop Yield, Soil Fertility, and Heavy Metals to Spent Mushroom Residues Application.Plants (Basel, Switzerland) · 2024Article
- Spent substrate from mushroom cultivation: exploitation potential toward various applications and value-added products.Bioengineered · 2023Review
- Biotechnological Applications of Mushrooms under the Water-Energy-Food Nexus: Crucial Aspects and Prospects from Farm to Pharmacy.Foods (Basel, Switzerland) · 2023Review
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Authors and funding
6 authors at 1 institution in 1 country.
Funding
Abstract
To investigate the remediation potential of spent mushroom substrate (SMS) on Cd pollution in a paddy soil, a rice pot experiment was conducted to study the effects of SMS addition on the availability of Cd in soil and the uptake of Cd in rice tissues. Five percent of SMS from Pleurotus eryngii (SMS-A, treatment: A), SMS from Agaricus bisporus (SMS-B, treatment: B), or SMS-A plus SMS-B (1:1, treatment: A+B) were added into a Cd-contaminated paddy soil before planting, respectively. The treatment of no SMS amendment was set up as the control (CK). At the four main growth stages of rice, the soils and plant samples were collected to detect the soil properties, Cd concentration in soils and rice tissues, and Cd fractions in soils. Results indicated that the application of SMS-A, SMS-B, and A+B significantly increased soil pH by 14.0-22.9, 23.9-32.9, and 22.7-30%, organic matter (OM) contents by 12.9-31.5, 22.1-34.5, and 26.1-36.9% comparing with CK. While cation exchange capacities (CECs) were increased by 3.6-8.5, 4.9-13.1, and 0.4-10.0% in A, B, and A+B treatments, respectively, except those at the maturation stage in A and B treatments. However, the CaCl
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Registered trials
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