Herbicides and Plant Physiology. Andrew H. Cobb

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and long‐distance seed dispersal (Figure 1.2). By recognising these, it is possible to reduce the spread of weed seeds, a vital component of any integrated weed management strategy.

      Source: Adapted from Radosevich, S.R. and Holt, J.S. (1984) Weed Ecology: Implications for Vegetation Management. New York: Wiley; containing information from Hanf (1983).

Weed Common name Seed production per plant
Veronica persica Common field speedwell 50–100
Avena fatua Wild oat 100–450
Galium aparine Cleavers 300–400
Senecio vulgaris Groundsel 1100–1200
Capsella bursa‐pastoris Shepherd’s purse 3500–4000
Cirsium arvense Creeping thistle 4000–5000
Taraxacum officinale Dandelion 5000 (200 per head)
Portulaca oleracea Purslane 10,000
Stellaria media Chickweed 15,000
Papaver rhoeas Poppy 14,000–19,500
Tripleurospermum maritimum spp. inodorum Scentless mayweed 15,000–19,000
Echinochloa crus‐galli Barnyard grass 2000–40,000
Chamaenerion angustifolium Rosebay willowherb 80,000
Eleusine indica Goose grass 50,000–135,000
Digitaria sanguinalis Large crabgrass 2000–150,000
Chenopodium album Fat hen 13,000–500,000
Triticum aestivum Wheat 90–100
Schematic illustration of some methods of weed seed dispersal with their estimated range in metres.

      Source: Liebman, M., Mohler, C.L. and Staver, C.P. (2001) Ecological Management of Agricultural Weeds. Cambridge University Press. Reproduced with permission of Cambridge University Press.

       1.5.7 Dormancy and duration of viability

      The length of time that seeds of individual species of weed remain viable in soil varies considerably. The nature of the research involved in collecting such data means that few comprehensive studies have been carried out, but those that have (see Toole and Brown, 1946, for a 39 year study!) show that although seeds of many species are viable for less than a decade, some species can survive for in excess of 80 years (examples include poppy and fat hen). Evidence from soils collected during archaeological excavations reveals seeds of certain species germinating after burial for 100–600 (and maybe even up to 1700!) years (Ødum, 1965).

      Dormancy in weed seeds allows for germination to be delayed until conditions are favourable. This dormancy may be innate and contributes to the periodicity of germination, as illustrated in Figure 1.1. In addition, dormancy may be induced or enforced in non‐dormant seeds if environmental conditions are unfavourable. This ensures that the weed seed germinates when conditions are most conducive to seedling survival.

Schematic illustration of factors affecting the soil seed population.

      Source: Grundy, A.C. and Jones, N.E. (2002) What is the weed seed bank? In: Naylor, R.E.L. (ed.) Weed Management Handbook, 9th edn. Oxford: Blackwell Publishing/BCPC. Reproduced with permission of John Wiley & Sons.

       1.5.8 Plasticity of weed growth

      The ability of a weed species to make rapid phenotypic adjustment to environmental change (acclimation) may offer a considerable strategic advantage to the weed in an arable context. An example of the consequence of such plasticity is environmental sensing by fat hen (Chenopodium album). This important weed can respond to canopy shade by undergoing rapid stem (internode) elongation, although the plant is invariably shorter if growing in full sun. Similarly,

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