Ahmad Riaz, James Trevor K, Rahman Anis, Holland Patrick T
AgResearch, Ruakura Research Centre, Hamilton, New Zealand.
J Environ Sci Health B. 2003 Nov;38(6):683-95. doi: 10.1081/PFC-120025553.
Soil dissipation of the herbicide clopyralid (3,6-dichloropicolinic acid) was measured in laboratory incubations and in field plots under different management regimes. In laboratory studies, soil was spiked with commercial grade liquid formulation of clopyralid (Versatill, 300 g a.i. L(-1) soluble concentrate) @ 0.8 microg a.i. g(-1) dry soil and the soil water content was maintained at 60% of water holding capacity of the soil. Treatments included incubation at 10 degrees C, 20 degrees C, 30 degrees C, day/night cycles (25/15 degrees C) and sterilized soil (20 degrees C). Furthermore, a field study was conducted at the Waikato Research Orchard near Hamilton, New Zealand starting in November 2000 to measure dissipation rates of clopyralid under differing agricultural situations. The management regimes were: permanent pasture, permanent pasture shielded from direct sunlight, bare ground, and bare ground shielded from direct sunlight. Clopyralid was sprayed in dilute solution @ 600 g a.i. ha(-1) on to field plots. Herbicide residue concentrations in soil samples taken at regular intervals after application were determined by gas chromatograph with electron capture detector. The laboratory experiments showed that dissipation rate of clopyralid was markedly faster in non-sterilized soil (20 degrees C), with a half-life (t1/2) of 7.3 d, than in sterilized soil (20 degrees C) with t1/2 of 57.8 d, demonstrating the importance of micro-organisms in the breakdown process. Higher temperatures led to more rapid dissipation of clopyralid (t1/2, 4.1 d at 30 degrees C vs 46.2 d at 10 degrees C). Dissipation was also faster in the day/night (25/15 degrees C) treatment (t1/2, 5.4 d), which could be partly due to activation of soil microbes by temperature fluctuations. In the field experiment, decomposition of clopyralid was much slower in the shaded plots under pasture (t1/2, 71.5 d) and bare ground (t1/2, 23.9 d) than in the unshaded pasture (t1/2, 5.0 d) and bare ground plots (t1/2, 12.9 d). These studies suggest that environmental factors such as temperature, soil water content, shading, and different management practices would have considerable influence on rate of clopyralid dissipation.
在实验室培养条件下以及不同管理模式的田间地块中,对除草剂氯吡嘧磺隆(3,6 - 二氯吡啶甲酸)的土壤消解情况进行了测定。在实验室研究中,向土壤中添加商业级氯吡嘧磺隆液体制剂(Versatill,300 g a.i. L⁻¹ 可溶性浓缩物),添加量为 0.8 μg a.i. g⁻¹ 干土,并将土壤含水量维持在土壤持水量的 60%。处理方式包括在 10℃、20℃、30℃下培养,昼夜循环(25/15℃)以及无菌土壤(20℃)。此外,2000 年 11 月起在新西兰汉密尔顿附近的怀卡托研究果园开展了一项田间研究,以测定不同农业情况下氯吡嘧磺隆的消解速率。管理模式包括:永久牧场、避免阳光直射的永久牧场、裸地以及避免阳光直射的裸地。将氯吡嘧磺隆以 600 g a.i. ha⁻¹ 的稀释溶液喷洒到田间地块。施用后定期采集土壤样本,通过带有电子捕获检测器的气相色谱仪测定其中的除草剂残留浓度。实验室实验表明,氯吡嘧磺隆在非无菌土壤(20℃)中的消解速率明显更快,半衰期(t1/2)为 7.3 天,而在无菌土壤(20℃)中的半衰期为 57.8 天,这表明微生物在降解过程中具有重要作用。较高温度导致氯吡嘧磺隆消解更快(30℃下 t1/2 为 4.1 天,10℃下为 46.2 天)。在昼夜循环(25/15℃)处理中消解也更快(t1/2 为 5.4 天),这可能部分归因于温度波动对土壤微生物的激活作用。在田间实验中,牧场和裸地遮荫地块中氯吡嘧磺隆的分解比未遮荫的牧场(t1/2 为 5.0 天)和裸地地块(t1/2 为 12.9 天)慢得多(牧场遮荫地块 t1/2 为 71.5 天,裸地遮荫地块 t1/2 为 23.9 天)。这些研究表明,温度、土壤含水量、遮荫以及不同管理措施等环境因素会对氯吡嘧磺隆的消解速率产生相当大的影响。