The frequency of creeping perennials has also increased with minimal cultivation, for example field bindweed (C. arvensis) and Canada thistle (C. arvense). Chancellor and Froud‐Williams (1986) also point to the occurrence of unusual species in undisturbed arable land, particularly wind‐dispersed seeds of the genera Epilobium, Artemisia, Conyza and Lactuca, and suggest that these may be the problem weeds of the future. Current increases in minimum and zero cultivation methods for establishment of cereal and oilseed crops, for environmental and financial reasons, will undoubtedly be mirrored by further changes in the weed spectrum of arable land.
Table 1.12 Main broadleaf weeds and grass weeds present in 2359 winter cereal fields.
Source: Whitehead, R. and Wright, H.C. (1989) The incidence of weeds in winter cereals in Great Britain. Brighton Crop Protection Conference, Weeds 1, 107–112.
Broadleaf weeds | Fields infested (%) | Grass weeds | Fields infested (%) |
---|---|---|---|
Stellaria media | 94 | Poa annua | 79 |
Veronica persica | 72 | Avena spp. | 42 |
Matricaria spp. | 67 | Alopecurus myosuroides | 38 |
Galium aparine | 58 | Elytrigia repens | 21 |
Lamium purpureum | 47 | Lolium spp. | 14 |
Viola arvensis | 45 | Anisantha sterilis | 13 |
Sinapis arvensis | 36 | Poa trivialis | 7 |
Veronica hederifolia | 30 | Volunteer cereals | 7 |
Capsella bursa‐pastoris | 23 | ||
Volunteer oilseed rape | 23 | ||
Papaver rhoeas | 18 | ||
Fumaria officinalis | 17 | ||
Chenopodium album | 13 | ||
Aphanes arvensis | 12 | ||
Geranium spp. | 11 |
Herbicide choice and use has also had a profound effect on the weed flora in cereals (Martin, 1987). The use of 2,4‐D and MCPA since the late 1940s has caused a decline in many susceptible weeds, such as charlock (S. arvensis) and poppy (Papaver rhoeas), although more tolerant species, including chickweed (S. media), knotgrass (P. aviculare) and the speedwells (Veronica spp.), have prospered. The introduction of herbicide mixtures in the 1960s with, for example, mecoprop and ioxynil, gave a much wider spectrum of weed control. Other herbicides have since been developed for an autumn‐applied, residual action, including, for example, chlorsulfuron and chlorotoluron for improved control of grasses, and new molecules for the control of specific weeds, for example fluroxypyr for cleavers (G. aparine). However, the same principles will always apply, namely that the selection pressure caused by sustained herbicide use will allow less‐susceptible weed species to become dominant, and their continued use may encourage the selection of herbicide‐resistant individuals within a species, as has now occurred to many herbicides (see Chapter 13).
Climate change is predicted to have significant effects on both the geographical distribution of weeds and the severity of weed infestations. Evolutionary rate (for instance, in the development of herbicide resistance) has been demonstrated to vary dependent upon both temperature and moisture availability. This is probably a result of a combination of factors including generation time, population size and relative fitness of herbicide‐resistant individuals. All of these factors may be affected by increased average global temperatures and subsequent differences in regional weather patterns (Anon., 2000). In addition, milder winters