Invertebrate survey at Gunpowder Park, the former Royal Ordnance Site in the Lee Valley At the same time occasional scarification and furrowing of areas within the substrate-poor grasslands to expose bare ground and produce a varied topography will produce valuable microhabitats and also help prevent the loss of sparsely vegetated areas through succession. The proportion of new grasslands that need to be subject to this form of management is unlikely to be large - an average of 5% disturbed per year is probably more than enough to maintain the invertebrate populations requiring this kind of habitat. This is pretty much unknown territory, but it is probably best to aim for a proportion of disturbance in as many grasslands as feasible, so that invertebrate populations can benefit from habitat at a landscape rather than isolated level. The areas disturbed to expose bare ground can be small, and could either produced as a patchwork within the grasslands or in strips or corridors, whichever would better suit landscape issues and public perception. Additional sowing of plants such as Fodder Vetch Vicia villosa, Lucerne Medicago sativa, Carrot Daucus carota and Parsnip Pastinaca sativa into the developing grasslands is recommended. These plants are extremely valuable forage resources to different invertebrate species, and might encourage colonization of the grasslands with important species recorded at the nearby Rammey Marsh. Scarification of areas prior to sowing would be likely to improve the success of this strategy. Where there are slopes, especially south facing, it is recommended that small areas are periodically scraped to expose bare ground. The creation of short sections of vertical bank would also be extremely beneficial for ground nesting aculeate Hymenoptera. Osier Marsh The major management problem in the Osier Marsh area will be to prevent the loss of the seasonally exposed PFA pond edges and marsh vegetation to colonization by osier and birch, especially in dry summers. Pulling of invading willow and osier is recommended to slow succession, but in the longer term further mechanical work to open up areas lost to developing woodland would be highly advantageous. If osier and birch scrub and woodland could be removed and large enough areas of PFA substrate exposed, then valuable open habitats would develop on the friable PFA. An existing raised area immediately to the south at the eastern end of the western PFA pond has a somewhat heathy nature, and a more extensive area of similar habitat would be valuable. Raised PFA in the form of mounds and banks would provide important nesting substrate for ground nesting species. Currently this type of habitat is restricted to a rather few upturned root plates in the open, where for example in 2003 the mining bee Andrena clarkella was seen nesting on the southern side of the western PFA pond. Excavated areas in exposed PFA would develop vegetation communities associated with damper habitats, and there would be every possibility that glades of marsh orchids previously found on PFA in the Lee Valley (Shaw 1994) might colonize or reappear. The development of more extensive marshy vegetation, especially with plants such as Angelica, Purple Loosestrife, mint, figwort etc. would provide additional extremely valuable invertebrate habitat. Comfrey is an invasive plant, which can out-compete and replace existing diverse vegetation. Although bumblebees use its flowers and the agromyzid fly Agromyza ferruginosa, a local species that mines Symphytum, was recorded during this survey new to Essex, the plant has deep-branched tap roots and large shading leaves and will spread rapidly and smother other vegetation, becoming 1 10 Essex Naturalist (New Series) 21 (2004)