Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Key Laboratory of Environment Remediation and Ecological Health, Ministry of Education, Zhejiang University, Hangzhou, Zhejiang, 311300, China.
Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Key Laboratory of Environment Remediation and Ecological Health, Ministry of Education, Zhejiang University, Hangzhou, Zhejiang, 311300, China.
Environ Pollut. 2021 Apr 15;275:116542. doi: 10.1016/j.envpol.2021.116542. Epub 2021 Feb 6.
Cadmium (Cd) is the most concerning soil pollutant, and a threat to human health, especially in China. The in-situ immobilization of Cadmium by amendments is one of the most widely adopted methods to remedy soil contamination. The study was designed to evaluate the effect of organo-chemical amendments on soil Cd bioavailability and nitrogen cycling microbes under continuous planting of rice (Oryza sativa) and pak choi (Brassica chinensis L.). The experiment was carried out using four amendments, Lime, Zeolite, Superphosphate, and Biochar, at two different ratios; M1: at the ratio of 47:47:5:1, and M2 at the ratio of 71:23:5:1, respectively. Moreover, both M1 and M2 were enriched at four levels (T1: 0.5%; T2: 1%; T3: 2%; T4: 4%). Results showed that compared with CK (Cd enriched soils), the yield of rice under treatments of M1T1 and M2T1 increased by 8.93% and 8.36%, respectively. While the biomass (fresh weight) of pak choi under M1 and M2 amendments increased by 2.52-2.98 times and 0.76-2.89 times respectively, under enrichment treatments T1, T2, and T3. The total Cd concentrations in rice grains treated with M1T3 and M2T3 decreased by 89.25% and 93.16%, respectively, compared with CK. On the other hand, the total Cd concentrations in pak choi under M1T3 and M2T2 decreased by 92.86% and 90.23%, respectively. The results showed that soil pH was the main factor affecting Cd bioavailability in rice and pak choi. The Variance partitioning analysis (VPA) of rice and pak choi showed that soil pH was the most significant contributing factor. In the rice season, the contribution of soil pH (P) on Cd bioavailability was 10.14% (P = 0.102), and in the pak choi season, the contribution of soil pH was 8.38% (P = 0.133). Furthermore, the abundance of ammonia oxidation and denitrifying microorganisms had significantly correlation with soil pH and exchange Cd. In rice season, when the enrichment level of amendments increased from 0.5% (T1) to 2% (T3), the gene abundance of AOA, AOB, nirK, nirS and nosZ (І) tended to decrease. While in pak choi season, when the enrichment level increased at the level of 0.5% (T1), 1% (T2), and 2% (T3), the gene abundance of AOB, nirS, and nosZ (І) increased. Additionally, the gene abundance of AOA and nirK showed a reduction in the pak choi season contrasting to rice. And the mixed amendment M2 performed better at reducing Cd uptake than M1, which may have correlation with the ratio of lime and zeolite in them. Finally, we conclude that between these two amendments, when applied at a moderate level M2 type performed better than M1 in reducing Cd uptake, and also showed positive effects on both gene abundance and increase soil pH.
镉(Cd)是最受关注的土壤污染物,对人类健康构成威胁,尤其是在中国。通过添加改良剂原位固定镉是修复土壤污染最广泛采用的方法之一。本研究旨在评估有机化学改良剂在连续种植水稻(Oryza sativa)和白菜(Brassica chinensis L.)条件下对土壤镉生物有效性和氮循环微生物的影响。该实验使用四种改良剂,石灰、沸石、过磷酸钙和生物炭,以两种不同的比例;M1:比例为 47:47:5:1,M2 为 71:23:5:1,分别进行。此外,M1 和 M2 都以四个水平(T1:0.5%;T2:1%;T3:2%;T4:4%)进行富集。结果表明,与 CK(富含 Cd 的土壤)相比,M1T1 和 M2T1 处理下水稻的产量分别提高了 8.93%和 8.36%。而 M1 和 M2 改良剂处理下,白菜的生物量(鲜重)分别增加了 2.52-2.98 倍和 0.76-2.89 倍。与 CK 相比,用 M1T3 和 M2T3 处理的水稻糙米中总 Cd 浓度分别降低了 89.25%和 93.16%。另一方面,M1T3 和 M2T2 处理下白菜中总 Cd 浓度分别降低了 92.86%和 90.23%。结果表明,土壤 pH 是影响水稻和白菜中 Cd 生物有效性的主要因素。对水稻和白菜的方差分解分析(VPA)表明,土壤 pH 是最显著的贡献因素。在水稻季,土壤 pH(P)对 Cd 生物有效性的贡献为 10.14%(P=0.102),在白菜季,土壤 pH 的贡献为 8.38%(P=0.133)。此外,氨氧化和反硝化微生物的丰度与土壤 pH 和交换 Cd 显著相关。在水稻季,当改良剂的富集水平从 0.5%(T1)增加到 2%(T3)时,AOA、AOB、nirK、nirS 和 nosZ(І)的基因丰度趋于降低。而在白菜季,当富集水平在 0.5%(T1)、1%(T2)和 2%(T3)时,AOB、nirS 和 nosZ(І)的基因丰度增加。此外,与水稻相比,AOA 和 nirK 的基因丰度在白菜季减少。而混合改良剂 M2 比 M1 更能降低 Cd 的吸收,这可能与它们中石灰和沸石的比例有关。最后,我们得出结论,在这两种改良剂中,M2 型在适度水平下比 M1 型更能降低 Cd 的吸收,同时对基因丰度的增加和土壤 pH 的提高也有积极的影响。