有机生产系统中抑制多年生匍匐杂草的多样化作物排序

Greta Gramig , Zachary A. Pull , Patrick M. Carr
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引用次数: 0

摘要

在大平原北部,有机生产往往受到多年生匍匐杂草的限制。生产者通常依靠紫花苜蓿来控制这些杂草,但这并不总是切实可行的。因此,我们研究了加拿大蓟、田缚草和多年生耧斗菜对三种多样化作物序列的抑制作用:(i) ALF:三年种植紫花苜蓿,第四年种植硬红春小麦(HRSW);(ii) LENCL:第一年种植小扁豆,第二年在硬红春小麦上间种黄甜菜,第三年种植黄甜菜绿肥,第四年种植硬红春小麦;(iii) CCPLY:第一年种植九种冷季型覆盖作物(CC),第二年种植硬红春小麦,第三年种植九种冷暖季型覆盖作物,第四年种植硬红春小麦。从 2019 年到 2021 年,在杂草萌发高峰期,ALF 的加拿大蓟密度下降,但 LENCL 和 CCPLY 的密度保持不变。在杂草无性生长高峰期,ALF的加拿大蓟密度在2020年最大(每平方米-2有7个芽),然后在2021年和2022年下降(每平方米-2分别有1个和0.6个芽)。在LENCL,加拿大蓟的密度在2019年至2020年期间没有变化(分别为每平方米15株和14株),但在2021年下降到每平方米0.3株,然后在2022年再次反弹到每平方米5株。在CCPLY内,加拿大蓟的密度没有随着时间的推移而变化(平均值=9株/平方米-2)。杂草无性生长高峰期的加拿大蓟生物量也遵循类似的模式。同样,与 LENCL 或 CCPLY 相比,ALF 能更有效地抑制多年生耧斗菜和田野蓼。因此,紫花苜蓿仍然是管理多年生匍匐杂草的良好选择。不过,在 LENCL 和 CCPLY 中,这些杂草种类都没有大幅增加,而且不同种植序列的最终年 HRSW 产量也没有差异。因此,这两个耕作序列可在管理多年生匍匐杂草的同时提供作物多样化选择。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Diversified crop sequencing for suppression of creeping perennial weeds in organic production systems

In the Northern Great Plains, organic production is often limited by creeping perennial weeds. Producers have typically relied on alfalfa to control these weeds but this is not always practical. Therefore, we investigated Canada thistle, field bindweed, and perennial sowthistle suppression from three diversified crop sequences: (i) ALF, three years of alfalfa followed by a fourth year of hard red spring wheat (HRSW); (ii) LENCL, lentil the first year, HRSW interseeded with yellow sweetclover the second year, yellow sweetclover green manure the third year, and HRSW the fourth year; and (iii) CCPLY, nine species cool-season cover crop (CC) polyculture the first year, HRSW the second year, nine-species cool and warm season CC the third year, and HRSW the fourth year. From 2019 to 2021, at peak weed emergence, Canada thistle density declined in ALF, but remained unchanged in LENCL and CCPLY. During peak weed vegetative growth, Canada thistle density in ALF was greatest during 2020 (7 shoots per m−2), then declined during 2021 and 2022 (1 and 0.6 shoots m−2, respectively). Within LENCL, Canada thistle density did not change from 2019 to 2020 (15 and 14 shoots m−2, respectively), but then declined to 0.3 shoots m-2 in 2021 before rebounding again to 5 shoots m−2 in 2022. Within CCPLY, Canada thistle density did not change over time (mean ​= ​9 shoots m−2). Canada thistle biomass at peak weed vegetative growth followed similar patterns. Likewise, ALF was shown to suppress perennial sowthistle and field bindweed more effectively than LENCL or CCPLY. Hence, alfalfa remains a good choice for creeping perennial weed management. However, none of these weed species increased substantially in LENCL and CCPLY, and the final year HRSW yield did not differ among cropping sequences. Therefore, these two sequences may provide crop diversification options along with creeping perennial weed management.

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