Why We Cannot Save Our Wildlife
UK NATURE & ENVIRONMENT — APRIL 2026
Based on Defra official
statistics, published 28 April 2026 | Data: 1,185 species, 1970–2024
There is
a real anger in me about the continued decline of British wildlife. I have
spent 30 years watching all my efforts to save British wildlife come to little,
and understanding why has been my passion throughout my career. I became a
brilliant fundraiser and project manager; I was one of the first advocates of
rewilding and helped make rewilding the dominant philosophy that it is today.
But we
are still losing, the ‘why’ is explored throughout my work and my writings.
Read on. But first, let’s analyse the latest surveys and research.
This
week, the Department for Environment, Food and Rural Affairs published its
annual update to the Indicators of Species Abundance in England, covering data
up to 2024. it is one of the most comprehensive audits of English wildlife ever
assembled. And what it shows is devastating.
Since the
baseline year of 1970, the relative abundance of species across England has
fallen by approximately 40%. Priority species, those already identified as
threatened and in need of targeted conservation action, have fallen by roughly
80%.. And the trend, in 2024, continues downward.
Both indices set to 100 in 1970. All-species index (green): approximately 60 in 2024. Priority species index (red): approximately 20 in 2024. Source: Defra Worksheets 1 and 4, published 28 April 2026.
The mathematics of disappearance
It’s very
complex and a lot is missing, and that complexity is actually hiding things
that make the real picture a lot worse. When Defra’s statisticians assess
species trends over the long term — from the 1970s to the present — they find
that 22% of all monitored species have undergone what is classified as a
“strong decrease”. Another 19% have weakly declined. That means roughly 41% of
English wildlife is heading in the wrong direction, against just 30% that are
broadly stable and 30% showing some degree of recovery.
But the
short-term picture is even more alarming. Looking only at the past decade,
nearly 47% of species are showing strong short-term declines. This is not a
slow burn. The rate of loss appears to be accelerating.
The
priority species data is, if anything, harder to look at. These are the 161
species already known to be in trouble, listed under Section 41 of the Natural
Environment and Rural Communities Act 2006 precisely because they were
identified as requiring focused conservation effort. In 2024, the priority
species index stands at roughly 20 out of 100. The species we most urgently
tried to protect have lost four-fifths of their relative abundance in fifty
years. The long-term trend assessment shows that 48% of priority species have
undergone strong declines, with a further 22% weakly declining. Fewer than 12%
are broadly stable.
The species we most urgently
tried to protect have lost four-fifths of their relative abundance in fifty
years.
A tour through the wreckage
There are
more worrying signs when you look at individual taxonomic groups. As any
experienced ecologist will tell you, it is those most important to supporting
our ecosystem that are doing badly, and that means the decline will only
worsen.
MOTHS
Moths
constitute the largest single group in the indicator, with 444 species tracked
through the Rothamsted Insect Survey’s network of light traps and through
specialist priority moth monitoring. They are also among the most severely affected.
Over the long term, more than half of all monitored moth species are declining:
27% strongly, 25% weakly. Over the short term, the picture is even worse, with
44% in strong short-term decline.
This
matters for reasons that go beyond the moths themselves. Moths are nocturnal
pollinators of enormous ecological importance, visiting flowers that day-flying
insects miss entirely. Research has estimated that moths transfer pollen
between a wider variety of plant species than bees and butterflies combined.
They are also a primary food source for bats, for swifts, for nightjars, for
hedgehogs. When moth populations collapse, the reverberations travel up the
food chain and across the food web in ways that are difficult to predict but
impossible to stop.
Eight
moth species that were previously included in the indicator have had to be
dropped this year because their populations have fallen so far that there is
insufficient data to model a reliable trend. Among them: the emperor moth, the
grey mountain carpet, the heath rustic. We are not watching these species
struggle. We are watching the monitoring infrastructure for tracking their
struggle begin to fail.
BUMBLEBEES
Of the 11
bumblebee species in the indicator, nearly half have shown strong long-term
declines. The BeeWalks scheme, which began in 2010, has documented a troubling
picture: 45% of species strongly declining over that period, 63% showing strong
short-term falls. Bumblebees are of course among our most important
pollinators, responsible for a significant proportion of the pollination of
both wild plants and agricultural crops. Their loss is not merely a
conservation problem. It is an agricultural and economic one.
The
ecological context matters here. Bumblebees are losing habitat at both ends:
the wildflower-rich grasslands they need for foraging have been reduced to
fragments by decades of agricultural intensification, while the warm
south-facing banks they require for nesting have been degraded or built over.
Climate change is shifting the distributions of both the bees and the plants
they depend upon, often at different rates and in different directions. The
result is a slow uncoupling of relationships that took millions of years to
establish.
FRESHWATER INVERTEBRATES
The 235
freshwater macroinvertebrate taxa tell us a different story: a long period of
improvement in river water quality following the clean-up of industrial
pollution has produced genuine recovery in some species. But the proportion
showing strong short-term declines still stands at 44%.
What the
indicator cannot fully capture is the nature of the threats bearing down on
freshwater ecosystems right now. Sewage spills from water companies, agricultural
run-off, microplastics, pharmaceutical compounds in treated wastewater, the
cumulative warming of river temperatures: these are stressors piling on top of
one another faster than any monitoring scheme can track.
FISH
The fish
data, drawn from the Environment Agency’s National Fish Population Database,
covers 37 freshwater and estuarine species and is notable for its instability.
What the data shows is high polarisation: 32% of fish species in strong
long-term decline, but 35% showing strong increases. This is not reassurance.
It reflects the fact that some species have benefited from habitat improvements
while others have continued to collapse, and that the aggregate masks a great
deal of turbulence beneath it.
Known Knows, Knows Unknown &
Unknown Unknowns
The most
important statement in the technical annex accompanying this data is that the
UK is estimated to be home to around 55,000 native species of fauna, flora and
fungi. This indicator tracks only 1,185.
The 2.2%
are, on the whole, the species we happen to be able to monitor: the birds that
visit fixed transects, the butterflies that fly in daylight along paths where
volunteers walk, the moths attracted to the light traps. They skew
overwhelmingly towards vertebrates and towards charismatic, well-studied
invertebrate groups. They almost entirely exclude fungi, which constitute 32%
of the UK’s species. They exclude most beetles, most flies, most wasps and
ants, most spiders. They exclude mosses and liverworts. They exclude the vast
majority of invertebrates entirely.
This is not a criticism of the researchers. They are doing extraordinary work with limited resources, drawing on citizen science surveys run by charitable organisations, statutory monitoring by the Environment Agency, and volunteer networks that have taken decades to build. The Breeding Bird Survey alone relies on the annual effort of thousands of amateur naturalists who walk fixed transects at dawn each spring. Without them, we would know almost nothing.
The 40%
decline in species abundance that this indicator documents is a decline in the
abundance of the 2.2% of species we can track. The remaining 97.8% are
experiencing we know not what. Given what we know about the trajectory of
habitat loss, agricultural intensification, pollution and climate change, there
is no ecological reason to believe they are doing better than the species we
can see, and some concern they are doing worse.
What the data cannot tell
us: The
indicator covers birds, butterflies, moths, bats, a handful of mammals, some
freshwater species and a limited number of plants. It tells us nothing directly
about beetles (4,000 UK species), flies (7,000 species), spiders (670 species),
fungi (15,000 species), or the vast majority of wild plants. The 40% decline
figure represents the most visible fraction of a much larger and largely
unmeasured collapse.
Priority species and the illusion
of targeted conservation
The
priority species index deserves particular attention, because it is the one
most directly connected to fifty years of explicit conservation policy. Since
the Wildlife and Countryside Act 1981, through the UK Biodiversity Action Plan
in the 1990s, the Natural Environment and Rural Communities Act in 2006 and now
the Environment Act 2021, successive governments have identified threatened
species, listed them, written action plans for them and allocated resources to
their recovery. The priority species tracked in this indicator are the
beneficiaries of more targeted conservation efforts than any other wildlife in
England.
They have
declined by 80%.
In a
sense, this is the most important number in the entire dataset. It tells us
that the existing framework for conservation, identify threatened species,
targets resources, monitors, and reports, has not worked. Not in aggregate. Not
for the species it was most specifically designed to help.
There are, of course, individual success stories. The peregrine falcon has returned to English cities. The red kite now circles above many motorway verges. Bittern numbers have risen from a handful of booming males to several hundred. These are real and significant achievements, and the people who made them happen deserve genuine credit. But they are the exception in a dataset where the rule is ongoing, accelerating decline. Cherishing the recoveries while ignoring the broader trend is like praising a few successful repairs while the building continues to burn.
Why has
targeted conservation failed at scale? The honest answer is that targeted
conservation has largely operated at the wrong level. It has focused on
individual species when the problem is systemic. It has tried to protect
fragments of habitat while the processes destroying habitat have continued
unimpeded. It has worked within the existing economic and agricultural
framework rather than challenging the framework itself.
Protecting a small population of
stone curlews on a managed reserve does not address the fact that the intensive
arable landscape surrounding it is essentially dead to almost all other
wildlife.
The structural drivers, but not
the root cause
The
technical annex to this data release is very plain about what it measures and
about what it cannot. It is deafeningly quiet about why things are happening,
because government statistics are framed not to challenge the people who
control the Government and the powerful interests they protect.
But this
is no surprise to me. They have been documented in hundreds of peer-reviewed
studies and summarised in successive State of Nature reports. They are:
agricultural intensification, the use of pesticides and herbicides on a
landscape scale, the loss of hedgerows and field margins, urban sprawl, light
pollution, river pollution, the fragmentation and degradation of semi-natural
habitats, and the compounding effects of climate change on species already
stressed by all of the above.
Almost
all of these drivers are the direct result of policy choices. The UK’s post-war
agricultural policy, shaped by European subsidies and domestic price support
mechanisms, systematically incentivised farmers to remove hedgerows, drain
wetlands, plough grasslands and maximise yields from every available hectare.
The results were spectacular for food production and catastrophic for wildlife.
Over roughly three decades between 1950 and 1980, England lost around half its
ancient woodland, most of its lowland heath and wet grassland, and the vast
majority of its wildflower meadows.
The
post-Brexit agricultural settlement was supposed to change this. The
Environmental Land Management schemes, replacing the area-based subsidies of
the Common Agricultural Policy, were designed to pay farmers for environmental
outcomes rather than production. The theory was sound. The economics and
practice have been a disaster - the simple truth is we cannot afford to pay
landowners not to destroy wildlife. The fundamental question is, we should not
pay landowners to rent a little wildlife from them, but tax those landowners
who destroy nature, natural processes and ecosystem services.
We can
liken this problem to a tree; a tree represents a systemic problem like
poverty, injustice, inefficient land use or degradation of our environment.
Hacking at branches is futile, as it can stimulate growth, whereas striking at
the root eliminates the source.
The root
cause of all environmental problems are becuase people make money from
destroying nature - that is the root and the problem we need to face.
“There are a thousand hacking at
the branches of evil to one who is striking at the root, and it may be that he
who bestows the largest amount of time and money on the needy is doing the most
by his mode of life to produce that misery which he strives in vain to relieve.”
― Henry
David Thoreau, Walden
What ‘halting the decline by
2030’ actually requires
The
Environment Act 2021 committed the UK government to halting the decline in
species abundance by 2030 and increasing it by at least 10% by 2042. The target
is legally binding. The data published this week tells us that in 2024, with
six years remaining, the trend continues downward.
Halting a
decline of this magnitude and trajectory in six years would require action at a
scale that is without precedent in the history of English nature conservation.
It would require not tinkering at the margins of agricultural policy but
fundamentally changing the economics of farming and land ownership in England.
It would require not protecting a few more Sites of Special Scientific Interest
but restoring ecological function across a significant proportion of the
English countryside. It would require addressing water quality, light
pollution, pesticide use and urban expansion simultaneously, with the kind of
joined-up policy ambition that no recent government has shown the slightest
inclination to attempt.
It would
also require honesty about the fact that conservation, as currently practised,
is operating far too far downstream of the problems it is trying to solve.
Counting species in reserves while the surrounding landscape continues to
degrade is not a conservation strategy. It is an attempt to maintain a living
museum while human activity engulfs and destroys it.
How to make damaging nature
unprofitable
None of
this means conservation effort has been wasted, or that individual species
cannot recover. Some clearly can. Beaver reintroductions, which John McAlistair
and I pioneered back in 2001, have transformed stretches of riparian habitat at
a pace that has impressed ecologists, with knock-on effects on water quality,
flood attenuation and invertebrate diversity that would have taken decades of
active management to replicate. Rewilding projects on degraded agricultural
land have shown that, given time and reduced grazing pressure, substantial
biological richness can return without continuous intervention.
But these
examples work because they change the conditions on the ground, not just the
species list. That is the logic that needs to operate at a national scale, and
it is a logic that voluntary conservation spending and poorly designed
biodiversity credits cannot deliver on their own.
The
argument made here is that two fiscal tools could do what targeted conservation
has not: a Land Value Tax, which shifts the cost of holding land onto its site
value rather than its productive use, removing the incentive to farm
intensively purely to maintain an appreciating asset; and direct externality
pricing on the pollution that agriculture and industry impose on soil, rivers
and the species that depend on them. Together, these would harness price
signals to drive land use decisions in a direction that conservation payments
are currently trying to purchase, expensively and incompletely, against the
grain of the existing incentive structure.
This is
not land seizure or central planning. It is a correction to a market that
currently prices land as a risk-free appreciating asset while treating the
ecological damage it causes as someone else’s problem, only alleviated by taxpayer
subsidy. Getting those prices right is the only promising route to reversing
wildlife decline, rather than adding further layers of subsidy and bureaucracy
to a system whose underlying incentives remain unchanged.
Conservationists
need to grasp this idea and fast, and release all other ideas that are
economically unfeasible and counterproductive - read my other blogs to
understand why.
* * *
The 2024 data published by Defra
this week shows the all-species index standing at approximately 60 (index value,
baseline 100 in 1970) and the priority species index at approximately 20. The
next update, including 2025 data, is expected in spring 2027. The underlying
code used to generate the models is published openly on GitHub by the
Biological Records Centre.
DATA SOURCES
All figures derived from Defra, Indicators of
Species Abundance in England, 1970 to 2024, published 28 April 2026 (Official
Statistics). Technical methodology described in the accompanying Technical
Annex, also published 28 April 2026. Species trend data: Bat Conservation
Trust, British Trust for Ornithology, Butterfly Conservation, Environment
Agency, Joint Nature Conservation Committee, People’s Trust for Endangered
Species, Plantlife, Queen Mary University of London, Rare Breeding Birds
Programme Secretariat, Rothamsted Research, Royal Society for the Protection of
Birds, UK Centre for Ecology & Hydrology, and partner organisations. All
data published under the Open Government Licence v3.0.
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