Select Committee on Environmental Audit Written Evidence


Memorandum submitted by the Royal Botanic Gardens, Kew

EXECUTIVE SUMMARY

  The Royal Botanic Gardens, Kew submits that:

    The 2010 target adopted by the UK and EU has been useful in focusing attention on this important issue, as have other 2010 targets at global level.

    The UK Government is not on course to meet its 2010 biodiversity target.

    Many species and habitat types in the UK are still declining.

    Some groups, especially fungi, are still so poorly known that they lack a baseline inventory for the UK, without which measures of change are problematic.

    The UK biodiversity indicators are meaningful and useful but not sufficient on their own to give a full picture of progress towards the target.

    Some level of success can be claimed for the policy and institutional frameworks currently in place but there is much scope for improvement, as evidenced by the fact that some species targeted by Biodiversity Action Plans are still experiencing significant decline.

    More work is required to incorporate biodiversity protection into policy-making. In particular, the concept of conserving biological processes needs to be embedded in policy.

    Climate change is already having an impact on UK biodiversity, but its eventual impact cannot yet be predicted with any level of precision.

    Plant-based solutions are an essential element of the drive to combat climate change and the environmental challenges facing us all. RBG Kew and botanic gardens in the UK and UK Overseas Territories have the potential to make a greatly increased impact in countering the environmental challenge by saving threatened plants and habitats, and improving the quality of life for people.

    Plant and fungal conservation activities in the UK and especially in the UK Overseas Territories are severely under-resourced and far from sufficient to enable achievement of the 2010 target to halt loss of domestic biodiversity.

    Unpredictability and lack of continuity of funding present formidable challenges for plant conservation initiatives at a variety of scales, from high throughput seedbanking to implementation of conservation action plans for individual species endemic to UK Overseas Territories.

0  INTRODUCTION

  0.1  The Royal Botanic Gardens, Kew (hereafter RBG Kew) welcomes the Environmental Audit Committee's Inquiry on this important issue. We will address several of the specific questions posed by the Committee from the perspective of plant and fungal diversity in the UK and UK Overseas Territories (UKOTs).

  0.2  Our evidence refers not only to the UK and EU 2010 target of halting domestic biodiversity loss but also to related 2010 targets which apply at national, regional and international level. Documentation relating to these complementary but more detailed targets provides much of the evidence and policy recommendations on which our submission is based. In particular, we would draw the attention of the Committee to: the sixteen 2010 targets of the Global Strategy for Plant Conservation (GSPC; 2002), Plant Diversity Challenge (the UK response to GSPC; PDC; 2004) and Plant Diversity Challenge: 3 Years—16 Targets—1 Challenge (PDC progress report; a progress report on GSPC/PDC in the UK; 2007)[19]. We submit that the UK and EU 2010 target and the other complementary 2010 targets have been useful in focusing attention on conservation of plant and fungal biodiversity in the UK and, to a lesser extent the UKOTs.

  0.3  We consider that significant progress has been made in some areas but that the target of halting loss of domestic biodiversity presents a considerable challenge which is unlikely to be met in its entirety given current trends and resources. In particular we draw the attention of the Committee to the paucity of resources available for plant and fungal conservation in the UK and especially in the UK Overseas Territories, the biodiversity of which is in many ways more significant than that of the UK itself.

POLICY AND PROGRESS

1.  Is the Government on course to meet its 2010 biodiversity target?

  1.1  We submit that the Government is not on course to meet this target. While progress has been made towards meeting some aspects of the 2010 target of halting loss of domestic biodiversity, ample evidence exists that many species and habitat types in the UK are still declining. For example, Change in the British Flora 1987-2004 (2006; Botanical Society of the British Isles) flagged up as particular areas for concern:

    —  the loss of species from infertile habitats, including calcareous grassland (species declining include Gentianella amarella [autumn gentian] and Campanula rotundifolia [harebell])and dwarf shrub heath (eg Pedicularis sylvatica [lousewort] and Platanthera bifolia [lesser butterfly orchid]),

    —  the role of climate change in increasing ruderal/invasive species, potentially at the expense of native species, and

    —  eutrophication of aquatic environments.

  1.2  Change in the British Flora also contains a wealth of information on individual habitats and species, including many examples where, even in habitats which are not declining overall, individual species are declining.

2.  How effective is the biodiversity monitoring and reporting process?

  2.1  The biodiversity monitoring and reporting process is complex and involves a range of different systems and measures. Together, these allow the assessment of many changes in biodiversity for well known groups of organisms (including many flowering plants), but for less well known groups (including many fungi) the situation is not so positive. Further research into the species in such groups present in the UK and their distribution is necessary before we can hope for effective biodiversity monitoring across the board.

  2.2  The biodiversity indicators are only one way in which biodiversity monitoring and reporting take place, and it should be noted that many of the other sources of essential baseline data including New Atlas of the British and Irish Flora (2002) and Change in the British Flora 1987-2004, would not have come to fruition without substantial input from the voluntary/charitable sector.

Are the biodiversity indicators meaningful?

  2.3  The biodiversity indicators provide a useful "broad brushstroke" assessment of where we are with regard to different aspects of biodiversity conservation. Some caveats relating to plants are:

    —  Indicator 2 (Plant Diversity) looks at broad habitat types only and does not appear to take account of declining species within these habitats.

    —  Indicators 3 and 4 (UK BAP Priority Species and Habitats) are useful, but by definition do not take account of all species/habitats.

    —  Indicator 5 (Genetic Diversity) recognises that "genetic diversity is an important component of biodiversity" but only deals with livestock breeds and collections of cultivated plants which themselves conserve only a very narrow genetic base. In the context of the 2010 biodiversity target, we believe that genetic diversity in wild species is more significant and that studies of genetic diversity in declining species are urgently needed to assess the effect on genetic diversity of loss of peripheral populations etc.

Is there adequate data upon which to define targets and to assess progress?

  2.4  As mentioned under 2.1 above, data are available for some groups eg many flowering plants (largely through the voluntary sector), but for some other groups the necessary baseline data are largely lacking. We do not yet have a full inventory of the fungi of the UK—many native species await discovery and documentation, but at current rates of progress, with declining resources for UK mycology, completion of the inventory cannot be anticipated this century. Even for the flowering plants, some habitats have not been monitored in sufficient detail (see comments in Change in the British Flora 1987-2004 pertaining to montane and aquatic habitats, for example).

3.  Are the policy and institutional frameworks effective at protecting biodiversity? Is biodiversity protection addressed effectively at local and regional levels? How successful has the UK Biodiversity Action Plan been? Does Conserving biodiversity—the UK approach address the need to have a joined-up approach to biodiversity protection with the devolved administrations?

  3.1  There are multiple frameworks and there has been some success as a result of these in protection of biodiversity. However, the declines in species and habitats discussed indicate that the frameworks are not fully effective. Likewise, the UK BAP process has seen some successes, but not all species are included and even some that are included are still declining. Given increased levels of devolution, Conserving biodiversity—the UK approach is an appropriate document, but its identification of priority species and habitats (rather than all species and habitats) appears to be a step down from the 2010 biodiversity target. See also our comments about the biodiversity indicators proposed in Conserving biodiversity—the UK approach under 2.2-2.4 above.

4.  How well is biodiversity protection incorporated into the policy-making process? How well will the Ecosystem Approach Action Plan address this issue? Has there been enough progress in ensuring that the value of ecosystem services are reflected in decision-making?

  4.1  There is scope for biodiversity protection to be better incorporated into the policy-making process. Recommendation 3 of the PDC progress report states "Undertake a review of the mechanisms available to conserve important plants and fungi (the protected area network, agri-environment and forestry schemes) and where necessary focus these schemes to ensure they are working to stop plant and fungal diversity loss and to increase ecological resilience in the wider landscape".

  4.2  The importance of understanding and conserving biological process in addition to named taxa has been identified by the Plant Conservation Genetics Working Group of the interagency Plant Conservation Working Group and others. This is particularly relevant in complex groups such as Sorbus, Hieracium and Euphrasia in which hybridisation, changes in ploidy etc. are ongoing processes. Preserving ecosystem function/services in the habitats where these taxa grow will be essential in allowing these natural processes to continue, and we believe that the concept of process needs to be embedded in policy.

KEY THREATS

7.  What impact will climate change have on UK biodiversity? How might the impacts of climate change be reduced? How can potential conflict between climate change mitigation and adaptation measures and biodiversity protection be effectively managed?

  7.1  The impact of climate change on UK biodiversity is not possible to predict with any certainty, but Box 3 in Conserving biodiversity—the UK approach reports on worrying scenarios with climate change posing a significant risk to 5-25% of UK BAP species targets. Despite the lack of certainty, it is clear that climate change is already having an impact, with many ruderal/alien species extending out from their historical strongholds and, conversely, native species with narrow habitat requirements being further marginalised.

  7.2  Recommendation 3 of the PDC progress report states "Support large, landscape-scale conservation initiatives that allow for the conservation of plants and fungi and their habitats in the face of climate change. Focus specifically on those that link up important places for plant and fungal diversity in the UK—thus optimising population size and extent of critical species, conserving genetic diversity, improving habitat condition and restoring resilient and functioning ecosystems". To our knowledge this has yet to be implemented.

  7.3  RBG Kew submits that plant-based solutions are an essential element of the drive to combat climate change and the environmental challenges facing us all. Over ten years, through this Programme, Kew and its global partners will make a greatly increased impact in countering the environmental challenge by saving threatened plants and habitats, and improving the quality of life for people. This represents a major step-change in the scale of activity and delivery of conservation outcomes.

  7.4  RBG Kew plans to work with Defra, and other partners and supporters, both nationally and internationally, to develop and deliver the Breathing Planet Programme which comprises seven key actions:

    1. discovering, collating and accelerating global access to essential information on the variety and distribution of the world's plant and fungal species through fundamental science, enhanced collection programmes, systematics, data capture, GIS science and novel identification tools such as web-based floras and DNA barcoding;

    2. identifying plant and fungal species and regions of the world most at risk of losing their wild diversity, by applying cutting-edge IT and GIS approaches to enable priority setting for conservation programmes targeted at saving the most vulnerable areas first;

    3. helping implement global plant and fungal conservation programmes such as creation of new sustainably managed areas through established and new partnerships in countries richest in diversity and geographical extent of remaining wild vegetation;

  Together these actions will help retain the Earth's major remaining carbon sinks.

    4. extending the Millennium Seed Bank's global partnership programmes to secure in safe storage 25% of the world's plants by 2020, targeting species and regions most at risk from climate change such as alpine endemics, coastal species and those endemic to desertifying lands;

    5. establishing a global network of scientists and practitioners in restoration ecology to use seed banks for the urgent repair and re-establishment of damaged native vegetation;

  These two actions will help recover lost plant productivity and carbon sequestration.

    6. expanding plant and fungal diversity knowledge and Kew's innovative science programmes to the identification and successful growth of locally-appropriate plant species under changing climatic regimes on agricultural, urban and suburban lands;

  This action will help plant-based adaptation to climate change to succeed.

    7. using the high public visitation, web and media opportunities provided by Kew and partner botanic gardens to deliver enjoyable, inspiring experiences that inform people world-wide about plant-based mitigation and adaptation strategies to cope with climate change and other significant environmental challenges facing us all.

RESOURCES

9.  Are there adequate resources for biodiversity protection and enhancement? Has the Government addressed the need to provide additional support for biodiversity protection in the UK Overseas Territories?

  9.1  Plant and fungal conservation activity in the UK is dependent to a large degree on the voluntary/charitable sectors, where resources are limited and restrict the level of activity undertaken. The importance of providing resources to these sectors and of training sufficient people in the necessary skills is flagged up in Recommendations 9 and 10 of the PDC progress report.

  9.2  RBG Kew and partner organisations in the voluntary/charitable sector have invested substantial resources into banking the seed of the UK flora. Kew's Millennium Seed Bank holds c. 96% of the UK's plant species diversity (the highest proportion of the native flora banked of any country in the world), and many rare and threatened species from the UKOTS. However, enhanced government support is now urgently required to enable the seed bank to continue to operate at a scale proportionate to the severity of the threat posed by habitat loss and climate change. Priorities include further banking of UKOTs flora and expanded UK collection programmes to ensure that adequate genetic diversity is conserved in the bank.

  9.3  Activity in the UK Overseas Territories is still at a remarkably low level, given the global significance of the biota in some of the UKOTs. Many taxa are only known from a single UKOT or have populations of global significance in the UKOTs. Already there are documented extinctions of endemic taxa of plants (and other major groups of organisms) in the UKOTs. St Helena, where only fragments of native vegetation survive and many of the endemic species are on the verge of extinction, is an example of the parlous state of biodiversity in the OTs (Fay et al. 2007, Curtis's Bot. Mag. 25: 243-250).

  9.4  RBG Kew is active in plant and fungal conservation work in the UK and the UKOTs, providing scientific expertise to support effective conservation management as well as engaging in training and capacity building activities to enable local staff and other stakeholders to develop sustainable biodiversity action plans. Such work forms part of Kew's statutory obligations and is an institutional priority. However, demand for these services greatly exceeds our ability to deliver, in the context of year-on-year decreases in grant-in-aid from Defra.

  9.5  Our work with partners in the UKOTs has given us a broad understanding of the resource levels and needs of these communities with respect to plant and fungal conservation. RBG Kew recently submitted evidence on this subject to the House of Lords Select Committee on Science and Technology in the course of their Inquiry into Taxonomy and Systematics. The main points of our evidence are outlined below in some detail, as we consider the needs of the UKOTs as among the highest priorities to be addressed by Government if the challenge presented by the 2010 target is to be taken seriously.

9.6  UKOTs plant diversity—context

  9.6.1  UK Overseas Territories support critically important UK biodiversity. The diversity and endemism of plants and fungi found in the UK Overseas Territories is far greater and more biologically important than that of metropolitan UK. The island of St Helena alone has 50 endemic plant species recorded from a native flora of about 60 species of vascular plants. In many cases the endemic species is the sole member of their genus (monospecific), thus representing unique phylogenetic lines.

  9.6.2  In most UKOTs we still have not fully documented the flora and so do not know the full extent of their plant diversity and endemism. A best guess is that across all 16 UKOTs there are at least 180 endemic species of vascular plants—orders of magnitude more than metropolitan UK where most of the endemism is taxonomically below the species level.

  9.6.3  UKOTs also support critical assemblages of plant species at habitat and ecosystem level which provide important ecological services, contributing to human well-being, local economies and climate amelioration including forests, mangroves, coral reefs, sea grass beds.

9.7  UKOTs Capacity needs

  9.7.1  The most critical issue for UKOTs is their lack of in-Territory botanical conservation expertise. Most Territories do not have any locally-based, trained botanical expert who can lead the documentation and conservation of their unique flora. Instead, most Territories are heavily reliant on international partnerships and external funding. In those Territories that do have a degree of locally-based expertise (eg St Helena, Cayman, Turks and Caicos Islands, Bermuda) it usually comprises one person—often a private individual not formally linked to the local agency responsible for biodiversity. Most local people do not see attractive career options in botanical and related environmental professions.

  9.7.2  It is vital that we build on systems to encourage young locals to train for and to see career opportunities in botany, horticulture, and environment. There is a huge need to build local capacity.

9.8  Access to information housed in metropolitan UK

  9.8.1  Most of the information and materials needed by UKOTs to document and conserve their flora are not available locally. They are housed in biodiversity institutes largely in the metropolitan UK eg RBG, Kew, Natural History Museum, London and RBG, Edinburgh. They include herbarium specimens and botanical literature.

  9.8.2  RBG Kew has a programme of repatriating electronic data to the UK Overseas Territories. Herbarium specimens from UKOTs are being located, digitised and made available both on the Web and on DVD to be sent to UKOTs. However, this is largely being done by volunteers and as project budgets allow and so is relatively slow-paced.

9.9  Development of in-Territory Reference Collections

  9.9.1  Virtually none of the UKOTs has active, functioning herbaria. In some cases there are small collections which are inadequately stored in rooms lacking climate control and which are not actively curated eg Montserrat, Cayman. These collections are deteriorating. Falkland Islands has a small herbarium but no curator. As part of a recently completed Darwin Initiative project, a small herbarium was established in the British Virgin Islands and housed in an air-conditioned room in the J.R.O'Neal Botanic Garden, managed by the BVI National Parks Trust, the agency responsible for terrestrial biodiversity management. Sadly, just as this was being implemented the botanic garden manager died suddenly. All developments have stopped until a suitable replacement can be found. The delay in filling this post is due to the lack of local capacity.

  9.9.2  RBG Kew has an active programme of collaborative plant diversity documentation in many of the UKOTs eg Montserrat, TCI, St Helena, Falkland Islands, BVI, and Ascension. In all cases, plant material is collected in duplicate with one set retained at Kew until local facilities are established and the reference collection can be repatriated to each Territory.

  9.9.3  Training is required for those staff that will run the herbarium. Kew offers a Diploma Course in Herbarium Techniques, both at Kew and in regional centres, depending on demand. Several people from UKOTs have attended one of these courses.

9.10  Inadequate access to funding

  9.10.1  Because of their status, Overseas Territories of the UK, are ineligible for many of the funds available for biodiversity conservation. In the UK the only dedicated fund is the small grants Overseas Territories Environment Programme (OTEP). Defra's Darwin Initiative has also provided significant funds to projects based in the UKOTs. However the stop-start nature of endeavours supported by such short-term funding sources is particularly problematic in the UKOTs context, where continuity of effort often depends on a single committed individual. The extinction of at least one endemic plant species (Nesiota elliptica in St Helena) can be ascribed to lack of continuity in conservation efforts in UKOTs.

9.11  The Global Strategy for Plant Conservation

  9.11.1  The UK Overseas Territories were not included in Plant Diversity Challenge, the UK's response to the Global Strategy for Plant Conservation, adopted by the CBD.

  9.11.2  In order for UKOTs to implement the Global Strategy for Plant Conservation and halt loss of their domestic plant diversity, each Territory needs easy access to reference specimens and literature housed in a fully functional herbarium that is adequately staffed and financed, together with facilities and expertise in in situ conservation, seed banking and habitat restoration.

2 June 2008







19   The PDC progress report is available at: http://www.plantlife.org.uk/portal/assets/News%20Sue%20Nottingham/PDC.pdf. The 10 recommendations in that report (q.v.) are all pertinent to the questions posed by the Committee. Back


 
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