ICAR Indian Institute of Soil Science, Nabibagh, Bhopal 462038, India.
ICAR Indian Agricultural Research Institute, New Delhi 110012, India.
Ecotoxicol Environ Saf. 2018 Aug 15;157:409-416. doi: 10.1016/j.ecoenv.2018.03.092. Epub 2018 Apr 11.
Climate change may increase the pest infestation leading to intensive use of insecticides. However, the effect of insecticide and climate factors on soil methane (CH) consumption is less understood. A laboratory experiment was carried out to evaluate the effect of temperature (15 °C, 35 °C, and 45 °C), moisture holding capacity (MHC) (60%, 100%), biochar (0%, 1%) and chlorpyrifos (0 ppm, 10 ppm) on CH consumption and microbial abundance in a tropical Vertisol of central India. Methane consumption rate k (ng CH consumed g soil d) varied from 0.065 ± 0.005 to 0.608 ± 0.018. Lowest k was in 15 °C-60% moisture holding capacity (MHC)-no biochar and with 10 ppm chlorpyrifos. Highest k was in 35 °C-100% MHC-1% biochar and without (0 ppm) chlorpyrifos. Cumulative CO production (ng CO produced g soil d) varied from 446 ± 15 to 1989 ± 116. Both CH consumption and CO production peaked in the treatment of 35 °C-100% MHC-1% biochar. Chlorpyrifos inhibited CH consumption irrespective of treatments. Abundance of 16S rRNA of eubacteria (× 10 g soil) varied from 2.33 ± 0.58 to 85.67 ± 7.00. Abundance of 16S rRNA genes representing Actinomycetes (× 10 g soil) varied from 7.67 ± 1.53 and pmoA gene (Methanotrophs) (× 10 g soil) varied from 1.23 ± 0.59 to 34.33 ± 6.51. Chlorpyrifos inhibited abundance of heterotrophic bacteria and methanotrophs but stimulated actinomycetes. Biochar stimulated the CH consumption, CO production and microbial abundance. Study highlighted that use of chlorpyrifos under climate change factors may inhibit CH consumption but the use of biochar may alleviate the negative effect of the chlorpyrifos.
气候变化可能会导致害虫滋生加剧,从而导致杀虫剂的大量使用。然而,杀虫剂和气候因素对土壤甲烷(CH)消耗的影响还不太清楚。本实验室实验评估了温度(15°C、35°C 和 45°C)、持水能力(MHC)(60%、100%)、生物炭(0%、1%)和毒死蜱(0 ppm、10 ppm)对印度中部热带变性土中 CH 消耗和微生物丰度的影响。CH 消耗率 k(ng CH 消耗 g 土壤 d)在 0.065±0.005 到 0.608±0.018 之间变化。在 15°C-60%MHC-无生物炭和 10 ppm 毒死蜱的处理中,k 值最低。在 35°C-100%MHC-1%生物炭和无(0 ppm)毒死蜱的处理中,k 值最高。累积 CO 产量(ng CO 产生 g 土壤 d)在 446±15 到 1989±116 之间变化。在 35°C-100%MHC-1%生物炭的处理中,CH 消耗和 CO 产生均达到峰值。无论处理如何,毒死蜱均抑制 CH 消耗。细菌 16S rRNA 的丰度(×10 g 土壤)在 2.33±0.58 到 85.67±7.00 之间变化。放线菌 16S rRNA 基因丰度(×10 g 土壤)在 7.67±1.53 和 pmoA 基因(甲烷营养菌)(×10 g 土壤)在 1.23±0.59 到 34.33±6.51 之间变化。毒死蜱抑制了异养细菌和甲烷营养菌的丰度,但刺激了放线菌。生物炭刺激了 CH 消耗、CO 生成和微生物丰度。研究结果表明,在气候变化因素下使用毒死蜱可能会抑制 CH 消耗,但使用生物炭可能会减轻毒死蜱的负面影响。