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Japanese knotweed Fallopia japonica (9).JPG

Invasive Non-Native Species in NPT

Invasive non-native species (INNS) are regarded as a significant threat to biodiversity. In the UK, all INNS are neophytes, i.e. non-native species that have been introduced into the British flora since 1600AD. Currently, the number of naturalised neophytes in Britain outnumbers the number of native species, but most neophytes have little impact on biodiversity and many may actually add something to it on a local scale. However, there are a group of 14 invasive neophyte species and groups that we believe are of particular concern in NPT.

Of these, Himalayan Balsam (or Indian Balsam), Japanese Knotweed and Rhododendron are notorious, but each species in this list has a significant impact on one or more of our principal habitats (see Table 2). Other potentially invasive species in the county such as Lupin, Chinese Bramble, American Skunk Cabbage and Henry’s Honeysuckle could pose a threat in the future.

 

Several other neophyte species which are abundant and aggressive competitors, particularly in early successional or ruderal environments, include some Stonecrop species, Bilbao Fleabane and Hoary Mustard, but none of these have significant effects on local biodiversity. Similarly, there are a number of garden throw-out species which are widespread and persistent in the county, notably Dotted Loosestrife and Montbretia, which we believe are not having significant effects on biodiversity at present.

 

Interesting problems are posed by some garden plants that have become established and/or naturalised in some habitats where they might cross fertilise and hybridise with native species. Two significant examples are given by Spanish (and Hybrid) Bluebell and the silver-blotched leaf form of Garden Yellow Archangel. The extent to which Spanish/Hybrid Bluebell has hybridised with native Bluebells and the effect that this may have on the genetic purity of local native Bluebell populations is largely unknown. At the moment there is little evidence that there is cause for concern but it seems prudent to eradicate naturalised Spanish/Hybrid Bluebells from areas where they could hybridise with native Bluebells e.g. in ancient woodland and hedgerow. Similarly, it would be wise to control naturalised populations of Garden Yellow Archangel, which is much more vigorous and competitive than our native Yellow Archangel.

With regards to invasive non-native fauna in NPT, we have records for a number of species, including:

  • American Mink

  • Grey Squirrel

  • Red-eared Terrapin

  • Egyptian Goose

Of these, perhaps the most common is the Grey Squirrel, which is ubiquitous across NPT and commonly seen across our parks, gardens and woodlands. The Grey Squirrel is a North American species, which is highly competitive with the native Red Squirrel, as well as transmitting a disease (Parapoxvirus) which has decimated the Red Squirrel populations in Wales. Red Squirrels were once found across the whole of NPT but by 1999 they had disappeared from the county and from much of Wales as a whole. This decline in the Red Squirrel has been attributed to the Grey Squirrel, though habitat loss, road traffic and other predators are also likely to have had an impact. Likewise, a similar correlation can be seen between the decline of the Water Vole and the spread of the American Mink, which has been blamed for the decline of Water Vole in other areas across the UK. We do not have substantial evidence of other non-native fauna causing significant problems in NPT, though this is not to say it is not occurring.

 

Brief descriptions of the INNS of most concern in NPT and a summary of their main impacts is given below. A wider list of INNS problematic across the whole of Wales has been collated and details of this list can be found on the Wales Biodiversity Partnership website.

The Distribution of INNS (of particular concern) in NPT habitats

The table below shows the occurrence of 18 INNS in the NPT’s major terrestrial and freshwater habitat categories. Note that waterweeds are listed as separate species except for Nuttall’s and Canadian Pondweed which are included together. A number of significant issues are clear from this analysis:

 

(i)All the major terrestrial and freshwater ecosystems in NPT have INNS in them.

(ii)Cotoneaster, Himalayan Balsam and Japanese Knotweed are represented in more than half of these habitats while Buddleia and Rhododendron are also widely distributed.

(iii)Urban habitats contain the most INNS and are likely to be the source of INNS in other habitats. For example a number of Cotoneaster species have spread from amenity planting on industrial estates, parks and gardens. Rhododendron has also spread uncontrollably in areas like Margam Park.

(iv)Of the remaining habitats, coastal ecosystems supports the most INNS, e.g. Crymlyn Burrows.

Species
Woodland
Heathland and Moorland
Semi-Natural Grassland
Open Mosaic
Enclosed Farmland
Urban
Freshwater
Wetland
Inland Rock and Cliff
Coastal
Sitka Spruce
x
x
Sea Buckthorn
x
x
Rhododendron
x
x
x
x
x
Parrot's Feathers
x
x
Nuttal's/ Canadian Pondweed
x
x
New Zealand Pigmyweed
x
x
Michaelmas Daisy
x
x
Japanese Rose
x
x
x
Japanese Knotweed
x
x
x
x
x
Holm Oak
x
x
Himalayan Honeysuckle
x
x
x
Himalayan Balsam
x
x
x
x
x
x
Garden Lady's-Mantle
x
x
Curly Waterweed
x
x
Cotoneaster
x
x
x
x
x
x
Canadian Goldenrod
x
x
Buddleia
x
x
x
x
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