Where were we?
Biodiversity
Across the area we planted 12 species of trees and 7 species of shrub to create a diversity woodland. These species included (image above) Throughout planting I developed my skills in tree identification by the coloration of the buds and bark and the shape of the leaves for example I learnt that Rowan has darker bark and black buds compared to hazel that has lighter bark and medium sized green buds and Field maple having bark that appears to have vein like indentations that run down the length of the stem and light-colored dots on the bark. Trees we did not plant were Dutch elm disease which can be spread by Bark beetles which was accidently imported and has devastated the native Elm in the UK. However, we did plant a species of elm, specifically Wych elm which has resistance to this disease which allows it to be involved in the planting program. Similarly, European ash (Fraxinus excelsior) cannot be planted in the UK because of ‘Ash dieback’ which can be identified by a dark brittle band on the bark which can result in the whole tree collapsing. Compared to reading a book on tree ID, to physically plant the trees has developed my ID skills of native broadleaf and I would more confident now in identifying a species compared to at the start when I started this project.
What were we conserving?
Wildlife corridors are created to link habitats together to allow wildlife to disperse and have connected movement between historic and new sites, otherwise wildlife would be isolated to one area due to habitat fragmentation. Wildlife corridors usually are linear and can vary in size and type to provide connectivity. With ever growing human populations and expansion of urban areas and infrastructure, these wildlife corridors can be many forms such as rivers, woodland, hedgerows and man-made ‘green bridges’ which are more predominant in biodiversity hotspots.Planting on Hardy road next to Westcliff Primary School |
Why is this conservation important?
Forestry research indicates that from 31st
March 2020 there is an estimated 3.21 million hectares which represents 13% of
the total land coverage in the UK, 10% in England, 15% in Wales, 19% in
Scotland. Connectivity fundamentally provides species the ability to freely
immigrate which as a result can assist in supporting a genetically diverse and
genetic flow for meta populations. Freedom to travel though connected wildlife corridors
allow species to avoid predation and movement away from possible catastrophic
events such as wildfires or oil spills into a waterway that could wipe out a
population if they were restricted to one habitat. Alongside this, global pressures of climate change trends, require connectivity for species to immigrate
away from areas which are no longer suitable such as migrating birds which are
migrating further North.
In the UK, Roe deer (Capreolus capreolus) are 1 of 6 deer which travel long distance across the UK
and cover a large extent of occurrence and are commonly seen amongst urban environments.
Linear fragmentation and degraded woodland highlighted an impairment in gene
flow compared to intact connected woodland. In the future genetic
methods may constitute a useful tool to identify the state to prioritize action
plans for maintaining functional wildlife corridors across landscapes. On the
other hand, a mammal which benefits tremendously from intact woodland is the Hazel dormouse (Muscardinus
avellanarius). A rare and vulnerable
species to extinction this species is a priority species on the Biodiversity
Action Plan and under the Wildlife and Countryside act 1981. The Hazel dormouse
has continued to decline in population numbers for over 100 years with 72% of
the population declining 25 years ago.
Planting on site G and H on Hempdykes |
More information
North Lincolnshire Council | Tree planting scheme continues to grow (northlincs.gov.uk)
The Northern Forest: Planting 50 Million Trees | The Woodland Trust
Wildlife
corridors – Woodlands.co.uk
Benefits
of Conserving Wildlife Corridors (biologydiscussion.com)
Burkart, S., Gugerli,
F., Senn, J., Kuehn, R. & Bolliger, J. (2016). Evaluating the functionality
of expert-assessed wildlife corridors with genetic data from roe deer. Basic
and Applied Ecology, 17(1): 52-60.
Dondina, O., Kataoka,
L., Orioli, V. & Bani, L. (2016). How to manage hedgerows as effective
ecological corridors for mammals: A two-species approach. Agriculture,
Ecosystems & Environment, 231: 283-290.
Crooks, K. and Sanjayan, M., 2006. Connectivity conservation:
maintaining connections for nature. Cambridge University Press,
pp.1-20.--- Connectivity
conservation: maintaining connections for nature (Chapter 1) - Connectivity
Conservation (cambridge.org)
Woodland
Statistics - Forest Research
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