This report reads your land through continuous GIS data and satellite monitoring going back to 2018, currently. A large number of satellite sensor platforms (see methodology) feed through an ecoregion- and regime-aware scoring engine to produce what we call the Land Health Score.

The four ecosystem processes drive the verdict. The water cycle (how rain lands and stays); energy flow (how plants capture and store sunlight); the mineral cycle (how nutrients turn over); and community dynamics (how the plant assembly works as a functional system). Together they shape the property’s ability to absorb shocks, recover from disturbance, and build productive capital over time.

We score relative to a reference state that fits your land’s ecoregion, climate brittleness and management regime. A grassland in a non-brittle Atlantic climate is scored against grassland norms for that setting; a forest stand is scored against closed-canopy reference; agroforestry is scored against agroforestry references. The verdict you read is calibrated to your land.

The report leads with the Verdict and the Strategic Brief; read these first. Then drill into the chapters that matter to your question. Treat the numbers as indicative, not advisory: a strong direction-of-travel signal, suitable for planning, baseline-setting and disclosure, but not a substitute for ground inspection where a material decision rides on the answer.

Indicative Use Only

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What you’re seeing is substantive and comprehensive, but it is not yet complete.

This report is indicative, not advisory. It cannot constitute formal ecological, agricultural, financial, or land management advice and should not be treated as such.

The Land Health Score for Wilder Wood Farm in 2025 is Level 5.6.

Over the past 8 years the trajectory has been steady.

Level 5 sits in the transitional zone between a degenerating ecosystem and a high-functioning one.

This Strategic Brief consolidates the assessment, diagnostic, and actionable insights for Wilder Wood Farm into a single operational overview. The land sits at Land Health Score (EDX) of 5.6 across 175.2 hectares and 44 fields, with a steady (mid) trajectory across 8 years. The limiting ecosystem process is Community Dynamics at 56%; the carbon balance is +6.1 tCO₂e/ha/yr. The brief is short and operational, designed to be readable in a single sitting before a decision meeting; the master Land Health Report is comprehensive, designed for the diagnostic and audit work that precedes major commitments.

The structure of the brief follows the order of decisions: verdict (where the land stands), key findings (what is driving the verdict), priorities (what to do first), and pointers (where the underlying evidence lives). All cross-references in this brief point to chapters of the master Land Health Report so any single line in the brief is one click away from its supporting evidence.

Brittleness 3.5/10 (Non-brittle) and the normal weather class for the most recent year (2025) frame how the priorities should be sequenced. Brittle environments compress the window in which interventions can take effect; stress years narrow that window further. Where the trajectory is positive, the brief's priorities focus on maintenance and amplification; where the trajectory is steady or negative, the priorities focus on diagnosis and first-move corrections. The four ecosystem-process scores read water cycle (WCI 83%), energy flow (EFI 63%), mineral cycle (MCI 66%), and community dynamics (CDI 54%); the lowest-scoring process is usually the one to address first.

This overview summarises the key characteristics of the site. For full diagnostic detail, methodology, and confidence assessment, see the Baseline Land Health Assessment.

In the pages that follow you will find key findings relevant at a strategy level. There are also section references to the larger separate Baseline Land Health Report so the reader who wishes to know more detail can find it.

Assessment

Wilder Wood Farm sits at Land Health Score 5 (mid) at 58.8 percent on the site-wide grassland ensemble, placing it in the upper half of the Transitional band and within touching distance of the Recovering threshold above. The four wooded and agroforestry parcels tracked separately average considerably higher at Land Health Score 7 (mid), 69.1 percent, with three of the four sitting in the healthy range. The property is a 175-hectare mixed estate in the Atlantic Central ecoregion of Devon, spanning 38 permanent and rotational grassland parcels, two agroforestry alley-cropping fields (Hundred Acre Wood and Six Pine Trees), two wood-pasture parkland parcels (Owl's Holt and Wol's Wood), and three floodplain meadows along the river. The operating context is forgiving Atlantic country: brittleness sits at 3.4 (non-brittle, where rest reliably produces recovery), rainfall is dependable, and biological decay runs year-round. The 2025 growing season classified as Normal, with 348 mm of growing-season rain, three stress weeks and four optimal weeks, drier than the exceptional 2024 (486 mm, zero stress weeks) but well within the normal envelope. The eight-year trajectory shows the property climbing from Land Health Score 5 (low) in 2018 to Score 6 (mid) at its 2023 peak, then softening back to Score 5 (mid) in 2025 as two drier growing seasons tested the system. The 2025 reading is a fair test result, not a management reversal. Full site character sits in section 4 Context, and the trajectory read in section 2.1 Executive Summary.

Diagnostic

The limiting ecosystem process across the property is community dynamics: the diversity and functional richness of the plant community. Across 43 diagnosed parcels, 36 return community dynamics as the weakest of the four ecosystem processes, averaging 56 percent site-wide and running ten to fifteen points below the other three on almost every field. Water cycling is the strongest process at 83 percent site-wide with only a nine-point spread across the grassland parcels, mineral cycling holds at 66 percent, and energy capture at 63 percent is respectable. The pattern is classic productive-but-brittle: the underlying water and nutrient cycles have been restored, but sward composition has yet to catch up. Full process synthesis sits in section 3 Diagnostic Synthesis. The pattern shows up most acutely on four grassland parcels (Three Blind Mice Meadow, Goldilocks Field, Old MacDonald's Farmyard, The Cat and the Fiddle) that sit at Land Health Score 3 to 4 with all four processes weakening together. It shows up in a milder form across the mid-band. The four forest-track parcels diverge sharply: Hundred Acre Wood and Six Pine Trees perform at Score 7, Wol's Wood is recovering at Score 6 after a 2021 to 2022 canopy disturbance, and Owl's Holt sits at Score 3 with energy flow at 20 percent following a run of biomass losses. Carbon is a strong positive across the estate, drawing roughly six tonnes of CO2-equivalent per hectare per year with gross photosynthesis around 1,200 gC/m²/yr against ecosystem respiration of 896. Green process detail is in section 6, water cycle detail in section 5, carbon and forest-track diagnostics in section 7.

Actionable Insights

Diversity gap on the weakest grassland: Three Blind Mice Meadow, Goldilocks Field and Old MacDonald's Farmyard sit at Land Health Score 3 with community diversity in the 30 to 35 percent range and all four processes weakening together; this is the largest single lever on the property and moves the aggregate toward the Recovering band (section 3.10, section 9).

Rest before seed, on-farm before purchased: extend recovery periods on the weaker parcels by 20 to 50 percent, defer one or two paddocks for full seed set, then transfer hay with ripe seed heads from Peter Rabbit's Patch, Poohsticks Bridge and Mary's Garden onto the weaker fields; purchased seed is the last resort after two to three seasons (section 3.9, section 6, section 9).

Owl's Holt recovery window: wood-pasture parcel at Land Health Score 3 with energy flow at 20 percent, canopy cover at 66.7 percent and down 2.2 percentage points year-on-year, following four disturbance signals including a September 2025 severity event; requires a clean three-year recovery window with no further biomass extraction (section 3.10b, section 6, section 8).

The Cat and the Fiddle compaction check: wet valley field (Topographic Wetness Index 19.3) reading Water Cycle Index of only 65 percent alongside Mineral Cycle Index at 38 percent, the divergence between wet landscape position and modest water score points to surface compaction; walk after rain, check pugging around gateways and troughs, rest through wet months before any diversity work (section 3.9, section 8).

Ridge fields need shelter before intensification: Old Brown's Field, The Spider's Web Meadow, Baa-Baa Pasture and Old Mother Hubbard's Field sit on exposed ridge positions holding Land Health Score 6; hedgerow reinforcement or shelterbelt planting unlocks the next tier of enterprise options before any stocking increase (section 6, section 9).

Alley-cropping trajectory is the property's flagship: Hundred Acre Wood and Six Pine Trees hold Land Health Score 7 with recurring tree-row work signals across 2018, 2020, 2022 and 2025 reading as normal management rhythm; stretching row-work intervals or staggering the rotation so three-quarters of rows sit in full canopy at any time would lift energy flow into the mid-70s (section 7, section 9).

Wol's Wood recovery monitoring: biomass loss events in 2021 and 2022 pulled the parcel to Land Health Score 3 in 2024; strong bounce back to Score 6 in 2025 with canopy cover at 84.6 percent, understorey diversity is now the process to watch as light conditions stabilise (section 3.10b, section 8).

Aspect-differentiated rotation calendar: south-facing and east-facing parcels (Old Brown's Field, The Three Bears' Cottage, Mr Toad's Hall) warm two to three weeks ahead of the north-facing meadows (Peter Rabbit's Patch, Squirrel Nutkin's Field), and hold moisture two to three weeks longer in dry spells; running two rotation speeds rather than one uniform interval better matches the recovery envelope of each aspect (section 10, section 9).

Risk is the other side of the diagnostic coin. Where Section 3 of the Baseline Land Health Report identifies what is limiting ecosystem function and what to do about it, this section identifies what could go wrong, and where the exposure is greatest. The assessment covers ecological, financial, and compliance risk, drawing on the same data used throughout this report.

Ecological Risk

Ecological risk measures the vulnerability of each field to ecosystem process failure. Fields that are already stressed, declining in trajectory, or exposed to erosion represent the greatest operational risk to the land-based business.

Financial Risk

Natural capital is the productive foundation of any land-based business. This section translates ecological metrics into financial risk language, asset trajectory, revenue volatility, and the risk of stranded land.

Compliance & Certification Risk

Regulatory and certification frameworks increasingly require evidence of ecosystem condition and trajectory. This section assesses readiness against common standards.

All status indicators are satellite-derived and indicative. They are not formal compliance assessments. Where a standard requires independent verification, audit, or client-specific disclosures, this report provides the underlying evidence base but not the certification itself.

Risk Matrix

Each field plotted by likelihood of ecosystem stress (low EHI + declining trend) against impact (field area × vulnerability). Fields in the upper-right quadrant represent the greatest risk to the property.

Drought exposure on shallow-soil ridges is the headline risk

The biggest thing that could go wrong on this property is a genuine summer drought landing on the ridge-top pastures at the same time as a stocking peak. Devon has been forgiving so far. The last eight growing seasons have all sat inside the normal band for a non-brittle site (rainfall between 314 and 486 mm across the growing season, with 2024 being unusually generous). But the pattern to notice is that stress weeks and optimal weeks are both climbing over time, which is the signature of a climate that is becoming more variable rather than drier on average. A property that has never really been tested by drought does not yet know where its weak points are. The ridge-top fields are where a dry summer would show first. Old Brown's Field sits on a ridge (95 percent ridge, south-facing, Land Health Score 6 mid), The Spider's Web Meadow (76 percent ridge, east-facing) and Old Mother Hubbard (63 percent ridge) are the next most exposed. These fields already read a little drier in the water cycling data than the valley-floor fields, with Water Cycle Index in the mid-80s rather than the low-90s. That is still healthy, but the gap tells you which fields will lose ground first in a dry July. The management response is not complicated: rotate livestock off the ridges in a dry spell and onto the valley fields (Peter Rabbit's Patch, Poohsticks Bridge, Rabbit's Bottom Field) which will hold moisture two to three weeks longer.

The Cat and the Fiddle, Old MacDonald's Farmyard, Goldilocks and Three Blind Mice need attention this year

Four grassland parcels are running well below the site average and represent the concentrated risk on the property. The Cat and the Fiddle is at Land Health Score 4 (low) with mineral cycling reading 38 percent, which is genuinely weak. Old MacDonald's Farmyard, Goldilocks Field and Three Blind Mice Meadow are all at Score 3 with all four ecosystem processes in the 30 to 45 percent range. Nothing else on the property is anywhere near this band. These four fields are a combined risk to the site headline and, more practically, they are the fields most likely to fail in a stressed year because they have the least ecological buffer. The pattern across these four is uniform-low weakness rather than one dominant process failure, which points at systemic causes: possibly compaction, possibly a legacy of heavy set-stocking, possibly a soil chemistry issue. Worth walking these four with a spade this spring. If the top 15 cm shows a compaction pan, a single aeration pass followed by extended rest and mob grazing will reset the trajectory faster than any other intervention.

Owl's Holt is the forest-track risk to watch

On the forest parcels the picture is broadly good, but Owl's Holt is the exception and needs naming clearly. The parcel reads at Land Health Score 3 (mid) with energy flow at 20 percent, which is a collapsed reading against the wooded-pasture reference. The trajectory tells the story: this parcel ran at Score 5 to 6 from 2018 to 2021, dropped to Score 4 in 2022 and 2023, hit Score 2 in 2024, and is now recovering at Score 3. The disturbance record shows four separate biomass signals between 2018 and 2025, including a partial harvest signal in 2022 and a spectral break in September 2025. Canopy cover currently reads 66.7 percent, down 2.2 percentage points year-on-year. This is a parcel in active recovery from repeated interventions. The risk here is management-driven rather than climate-driven: any further biomass removal in the next two to three years will delay recovery significantly. The other three forest parcels (Hundred Acre Wood, Six Pine Trees, Wol's Wood) all sit at Score 6 or 7 and are functioning well. Wol's Wood shows a 4.7 percentage point canopy drop year-on-year and is worth checking on the ground, but the composite score has actually recovered from Score 3 in 2024 to Score 6 this year, so the parcel is healing.

Community diversity is the property-wide vulnerability that is invisible from the ground

The subtler risk, and the one that a walking inspection will not catch, is that community dynamics is the weakest of the four ecosystem processes across the whole grassland estate. Read down the CDI column and the numbers cluster in the 50s and 60s on the good fields, and drop into the 30s and 40s on the weaker ones. Water, energy and minerals are all working well; species diversity is the thin layer. On a non-brittle site like Devon this is the classic signature of long rest under a limited species pool: the grasses that are there grow vigorously, but the sward is not diversifying on its own. This matters because diversity is the insurance policy for the climate variability signal we already see in the weather record. A five-species sward on Peter Rabbit's Patch will hold biomass through a stress week that a fifteen-species sward would barely notice. The right response is emphatically not to buy in seed. Start with extended rest and let existing species flower and set seed, then cut hay from your most diverse paddocks (Peter Rabbit's Patch and Poohsticks Bridge are the candidates, with the highest CDI on the property) and spread it green onto the weaker fields with livestock trampling it in. A three-year on-farm seed transfer programme, done in that order, will move the CDI numbers more reliably than any purchased mix and at a fraction of the cost.

What to prepare for

In priority order: first, the four low-scoring grassland fields need a spade check and a management decision this spring. Second, Owl's Holt needs a moratorium on further biomass removal for two to three years. Third, build a drought playbook now, before you need it, that identifies which fields livestock come off first and which fields they move onto. Fourth, start the on-farm seed transfer work on the weakest ten fields, using your own diverse paddocks as the donor. None of these are emerg

Event Channel (Forest Track)

Disturbance signals detected on forest-track parcels by the event-channel detectors (PALSAR-2 year-on-year biomass change, Sentinel-1 radar step, Sentinel-2 burn-severity break, Hansen global forest change). Each detection carries an event-type token from the 15-token taxonomy. When the signal indicates biomass loss, the corresponding parcel-year enters an active recovery phase -- ecosystem function is classified as Recovering and stays there until regrowth becomes observable (typically over three or more years after the event). See the parcel-level diagnostic in Section 2 for the recovery-phase narrative per parcel and year.

Saturated = yes: the underlying PALSAR-2 pair includes at least one reading above the L-band 150 t/ha sensitivity ceiling. The reported fractional loss is a lower bound -- actual biomass loss may be larger.

Owl's Holt -- wooded_pasture

P2_HV_YOY_DROP on 2018-07-15: magnitude -1.27 dB (moderate confidence), event type biomass_drop_forest.

PALSAR-2 HV dropped -1.27 dB YoY.

PALSAR2_YOY_BIOMASS_DROP on 2020-07-15: magnitude -0.30 frac (moderate confidence), event type biomass_drop_forest.

PALSAR-2 L-band HV/HH backscatter declined 30.2% YoY, equivalent to ~14 t/ha woody biomass loss (prior 48 -> current 33 t/ha). Check for selective thinning, windthrow, drought-legacy mortality, or pest outbreak.

S1_VH_STEP_PARTIAL_HARVEST on 2022-09-30: magnitude -0.47 dB (low confidence), event type partial_harvest.

Annual mean VH dropped -0.38 dB YoY; summer-mean dropped -0.47 dB YoY.

S2_NBR_BREAK on 2025-09-15: magnitude +0.32 dNBR (moderate confidence), event type forest_severity_event.

dNBR (pre Apr-May minus post Aug-Oct) = 0.322. Threshold 0.15. NBR severity on forest -- fire, clearcut, or severe storm damage.

Hundred Acre Wood -- alley_cropping

P2_HV_YOY_DROP on 2018-07-15: magnitude -1.42 dB (moderate confidence), event type tree_row_biomass_drop.

PALSAR-2 HV dropped -1.42 dB YoY. L-band HV drop on alley cropping -- PALSAR sees tree canopy over arable alleys; this signal typically indicates tree row removal or major pruning of the overstory.

S1_VH_STEP_PARTIAL_HARVEST on 2018-09-30: magnitude -2.15 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -0.39 dB YoY; summer-mean dropped -2.15 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

P2_HV_YOY_DROP on 2020-07-15: magnitude -1.48 dB (moderate confidence), event type tree_row_biomass_drop.

PALSAR-2 HV dropped -1.48 dB YoY. L-band HV drop on alley cropping -- PALSAR sees tree canopy over arable alleys; this signal typically indicates tree row removal or major pruning of the overstory.

S1_VH_PIXEL_CONCENTRATED_DROP on 2020-08-31: magnitude -2.31 dB (p5 per-pixel YoY delta) (moderate confidence), event type row_removal.

Concentrated disturbance via p5: at least ~5 % of parcel pixels dropped 2.31 dB or more YoY (p5=-2.31, p10=-2.10). Concentrated sub-parcel VH drop -- likely localised tree row removal on alley cropping parcel.

S2_NBR_BREAK on 2020-09-15: magnitude +0.22 dNBR (moderate confidence), event type alley_crop_harvest.

dNBR (pre Apr-May minus post Aug-Oct) = 0.219. Threshold 0.15. NBR severity consistent with annual harvest of the arable crop in the alleys between tree rows. Expected annual event. Investigate only if timing or magnitude is unusual for the crop rotation.

BSI_NDMI_CO_DROP on 2020-09-30: magnitude -0.18 dNDMI (moderate confidence), event type alley_tillage_or_ploughing.

BSI zero-crossing (early -0.131 -> late 0.047); NDMI dropped -0.184. Bare-soil emergence + moisture drop in the alleys -- characteristic signature of tillage / ploughing. Relevant for soil-carbon accounting and no-till vs conventional management scoring.

S1_VH_STEP_PARTIAL_HARVEST on 2020-09-30: magnitude -1.37 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -1.29 dB YoY; summer-mean dropped -1.37 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

P2_HV_YOY_DROP on 2022-07-15: magnitude -1.02 dB (moderate confidence), event type tree_row_biomass_drop.

PALSAR-2 HV dropped -1.02 dB YoY. L-band HV drop on alley cropping -- PALSAR sees tree canopy over arable alleys; this signal typically indicates tree row removal or major pruning of the overstory.

S1_VH_STEP_PARTIAL_HARVEST on 2022-09-30: magnitude -2.24 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -0.51 dB YoY; summer-mean dropped -2.24 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

S1_VH_STEP_PARTIAL_HARVEST on 2025-09-30: magnitude -1.40 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -0.81 dB YoY; summer-mean dropped -1.40 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

Six Pine Trees -- alley_cropping

P2_HV_YOY_DROP on 2020-07-15: magnitude -1.24 dB (moderate confidence), event type tree_row_biomass_drop.

PALSAR-2 HV dropped -1.24 dB YoY. L-band HV drop on alley cropping -- PALSAR sees tree canopy over arable alleys; this signal typically indicates tree row removal or major pruning of the overstory.

S1_VH_PIXEL_CONCENTRATED_DROP on 2020-08-31: magnitude -1.52 dB (p10 per-pixel YoY delta) (moderate confidence), event type row_removal.

Concentrated disturbance via p10: at least ~10 % of parcel pixels dropped 1.52 dB or more YoY (p5=-1.65, p10=-1.52). Concentrated sub-parcel VH drop -- likely localised tree row removal on alley cropping parcel.

BSI_NDMI_CO_DROP on 2020-09-30: magnitude -0.13 dNDMI (moderate confidence), event type alley_tillage_or_ploughing.

BSI zero-crossing (early -0.087 -> late 0.036); NDMI dropped -0.128. Bare-soil emergence + moisture drop in the alleys -- characteristic signature of tillage / ploughing. Relevant for soil-carbon accounting and no-till vs conventional management scoring.

S1_VH_STEP_PARTIAL_HARVEST on 2020-09-30: magnitude -1.29 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -1.08 dB YoY; summer-mean dropped -1.29 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

S2_NBR_BREAK on 2021-09-15: magnitude +0.37 dNBR (moderate confidence), event type alley_crop_harvest.

dNBR (pre Apr-May minus post Aug-Oct) = 0.375. Threshold 0.15. NBR severity consistent with annual harvest of the arable crop in the alleys between tree rows. Expected annual event. Investigate only if timing or magnitude is unusual for the crop rotation.

BSI_NDMI_CO_DROP on 2022-09-30: magnitude -0.35 dNDMI (moderate confidence), event type alley_tillage_or_ploughing.

BSI zero-crossing (early -0.312 -> late 0.045); NDMI dropped -0.353. Bare-soil emergence + moisture drop in the alleys -- characteristic signature of tillage / ploughing. Relevant for soil-carbon accounting and no-till vs conventional management scoring.

S1_VH_STEP_PARTIAL_HARVEST on 2022-09-30: magnitude -2.14 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -0.32 dB YoY; summer-mean dropped -2.14 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

S1_VH_STEP_PARTIAL_HARVEST on 2025-09-30: magnitude -0.75 dB (low confidence), event type alley_crop_change_or_row_work.

Annual mean VH dropped -0.75 dB YoY; summer-mean dropped -0.60 dB YoY. Parcel-mean VH drop on alley cropping -- could be arable crop harvest (seasonal), row maintenance, or tree thinning. Magnitude + timing narrows the interpretation.

Wol's Wood -- wooded_pasture

P2_HV_YOY_DROP on 2021-07-15: magnitude -1.47 dB (moderate confidence), event type biomass_drop_forest.

PALSAR-2 HV dropped -1.47 dB YoY.

PALSAR2_YOY_BIOMASS_DROP on 2021-07-15: magnitude -0.37 frac (low confidence), event type biomass_drop_forest.

PALSAR-2 L-band HV/HH backscatter declined 37.5% YoY, equivalent to ~60 t/ha woody biomass loss (prior 161 -> current 101 t/ha). Pair includes saturated AGB reading(s) (>=150 t/ha); fractional magnitude is a lower bound -- actual biomass loss may be larger. Check for selective thinning, windthrow, drought-legacy mortality, or pest outbreak.

Note: the PALSAR-2 readings underlying this trigger sit above the L-band sensitivity ceiling. The reported fractional loss is a lower bound -- actual biomass loss may be larger.

PALSAR2_YOY_BIOMASS_DROP on 2022-07-15: magnitude -0.18 frac (moderate confidence), event type biomass_drop_forest.

PALSAR-2 L-band HV/HH backscatter declined 17.8% YoY, equivalent to ~18 t/ha woody biomass loss (prior 101 -> current 83 t/ha). Check for selective thinning, windthrow, drought-legacy mortality, or pest outbreak.

Where the risk assessment identifies what could go wrong, this section identifies what could go right. Every diagnostic constraint is also an opportunity, a field that is underperforming its landscape position has the most room to improve. The opportunities below are ranked by impact and feasibility, drawing on the same data used throughout this report.

Quick Wins

Fields where small management changes could shift the score within one to two growing seasons. These are the opportunities with the fastest payback, fields close to an EDX band boundary, fields with fixable water constraints, or fields where the strongest performer’s approach could be replicated.

Strategic Investments

Landscape-scale interventions with compound returns over a 1-5 year horizon. These require more planning and investment than the quick wins above, but address root causes rather than symptoms. The table below names each investment, the fields or area in scope, and the reason it is being recommended. "Process Constraint" entries refer to the site-wide limiting ecosystem process (water, energy, mineral or community dynamics) that is currently capping overall ecosystem function, the highest-leverage intervention available on this land.

Ecosystem Service Indicators

Healthy ecosystems generate measurable outcomes beyond agricultural production , carbon sequestration, habitat improvement, and water quality protection. This section identifies what the land is delivering and where improvement trajectories could strengthen the ecosystem service profile.

All indicators are satellite-derived and indicative. They demonstrate the direction and magnitude of ecosystem service delivery but are not verified measurements under any payment scheme or certification standard.

Opportunity Map

Fields ranked by opportunity score, the combination of proximity to a band boundary, water infrastructure potential, tree integration suitability, and diversity uplift headroom.

The highest-impact move is closing the diversity gap on the weakest third of the grassland

The single largest upside on this property sits in roughly a dozen grassland parcels where community dynamics is the drag on everything else. Water and mineral cycling on these fields are working well, the biology just does not yet have the species toolkit to convert that into peak production and resilience. Fix that and the whole property lifts. The pattern is clear in the numbers. Three Blind Mice Meadow reads at Land Health Score 3 (mid) with community diversity at 30 percent, Goldilocks Field at Land Health Score 3 (low) with diversity at 33 percent, and Old MacDonald's Farmyard at Land Health Score 3 (low) with diversity at 35 percent. In every one of these cases the water cycle is functioning at 64 to 68 percent and the mineral cycle at 39 to 42 percent, so the machinery for growth is present. What is missing is the range of plants that would let the sward respond to variable weather, cycle nutrients efficiently, and hold ground under grazing pressure. Lift community diversity on these fields from the low-30s into the 50s and the composite Score moves from band 3 to band 5 without any other intervention. The realistic upside on the weakest twelve parcels is roughly 10 to 15 Score points over three to four seasons. The route to that upside follows the standard recovery hierarchy, and the good news is that it costs almost nothing. Start with rest, extend recovery periods on Three Blind Mice, Goldilocks and Old MacDonald's Farmyard so the existing seed bank can express, flower and self-seed. Follow with mob grazing to trample seed into the surface and break any thatch layer. Defer one or two paddocks per season for full seed set, then cut hay with ripe seed heads from the strongest diversity paddocks on the property (Peter Rabbit's Patch, Poohsticks Bridge, Wee Willie Winkie's Meadow) and spread it onto the weaker fields with livestock to trample it in. Purchased seed is the last resort, and on this property with 38 grassland parcels the on-farm donor material is abundant, there is no need to buy anything in for two to three years.

Owl's Holt is the second-highest-leverage opportunity, and it is a forest question, not a grassland one

The wooded pasture at Owl's Holt is the one parcel where the trajectory has genuinely weakened, moving from Land Health Score 6 in 2019 and 2020 down to Land Health Score 3 (low) in 2025. The disturbance signals across 2018 to 2025 show a sequence of biomass drops, a partial harvest signature in 2022, and a burn-ratio break in 2025, with canopy cover now at roughly 67 percent and dropping. Energy flow reads at 20 percent, which is the limiting process by a wide margin. Mineral cycling and water cycling on the parcel are still functioning at 80 percent, so the soil and hydrology are intact. What has weakened is the canopy itself and the productive tree layer that drives everything else in a wooded pasture system. The opportunity here is to decide what Owl's Holt is meant to be over the next decade and manage accordingly. If it is intended as wooded pasture, active canopy recovery through underplanting, browse control and a rest period from stock during establishment will lift the parcel back toward Land Health Score 6 within three to five years. If the intention is a different regime altogether (more open silvopasture, or conversion toward alley-cropping alongside the neighbouring Hundred Acre Wood and Six Pine Trees), that is a strategic decision worth taking deliberately rather than by drift. Either way, this is the parcel where a specific intervention plan will pay back most visibly in the next assessment cycle.

The alley-cropping parcels are the property's flagship and they can be pushed further

Hundred Acre Wood at Land Health Score 7 (mid) and Six Pine Trees at Land Health Score 7 (mid) are already reading in the healthy range for their reference state. Water cycling is at 92 and 100 percent, mineral cycling in the mid-60s, community diversity at 69 percent on both. The limiting process on each is energy flow, sitting at 60 and 67 percent, which is characteristic of alley-cropping systems where the tree rows are still building canopy volume alongside the crop alleys. The eight-year record shows both parcels have held Score 7 to 9 consistently, with the small dip to Score 7 in 2025 tracking a late-season row work signature rather than any underlying decline. The upside on these two parcels is more modest in Score points (perhaps 2 to 3 points, into band 8) but it is worth pursuing because it demonstrates what the property can be. The lever is tree row biomass: as the rows mature and canopy volume rebuilds between harvest cycles, energy flow will climb into the 70s and pull the composite Score with it. The management question is whether the current row-work rotation (visible in the 2018, 2020, 2022 and 2025 disturbance signals) allows enough recovery time between interventions. Stretching the interval by a year or two, or staggering the work so that at any given time three-quarters of the rows are in full canopy, would let the energy flow score settle at its higher band.

The realistic five-year picture

Taken together, the grassland diversity work, the Owl's Holt canopy decision, and the alley-cropping refinement give the property a coherent five-year improvement plan. On the grassland side, the weakest twelve fields lift from band 3 and 4 into band 5 and 6, and the strong fields in band 6 and 7 hold or tick up as the whole rotation gets more forage-diverse. Wol's Wood, currently at Land Health Score 6 (mid) after a 2021 to 2022 biomass drop, will continue its natural recovery without intervention (it has already climbed from Score 3 in 2024 back to Score 6). The forest track parcels stabilise at Score 7 to 8, and the site-wide grassland aggregate moves from its current

Regime-specific Opportunities (Forest Track)

Each regime has its own ecological levers. The paragraphs below set out where the headroom sits for each forest-track regime present on this property -- generic for the regime, applicable across the parcels listed in each header. These complement the at-site quick-wins above; they describe the structural moves that bring a site closer to the upper end of what the regime can achieve, rather than just shifting a single year's score.

Alley cropping (Hundred Acre Wood, Six Pine Trees)

Alley cropping rewards canopy density. Once the tree rows are established, the lever is on the alleys: a multi-species cover crop rotation (legume + cereal + brassica) in the alley keeps the soil covered between cash-crop years and feeds the trees through root exudates. Widen the tree belts on the windward edge to reduce in-row evapotranspiration losses. This regime grows fastest on CDI and MCI as the trees mature -- expect a rising EHI trajectory through year 15.

Wood-pasture (Owl's Holt, Wol's Wood)

Wood-pasture's strength is in legacy standards over a managed sward. The opportunity is to plant successor cohorts before the existing veterans thin the canopy through senescence: 10-20 trees/ha in tree shelters, managed for 5-10 years until they're above browse height. Rotational grazing maintains the sward; pollarding the standards (where culturally appropriate) extends standard lifespan by decades.

The trajectory classification answers one question: across the 8 years of assessment (2018-2025), is the ecosystem getting better, holding steady, or declining? This is the multi-year signal that distinguishes a single year’s weather noise from a real change in land condition.

Steady (Mid)

The land is holding steady at a mid-range level of function (Land Health Score 5.6). There is capacity for improvement, the diagnostic identifies what is holding the system back.

Data Sources

Scoring Framework

Land Health Scoring Framework

EcoIntel scores four ecosystem processes (Energy Flow, Water Cycling, Mineral Cycling, Community Dynamics) using weighted composites of optical indices, radar structure, and soil/litter proxies. Process scores (0-100%) are converted to a 9-level EDX classification. An 8-model weather-corrected ensemble using spectral, temporal, radar, topographic, and climate predictors. Models G and H incorporate growing-season stress weeks and evapotranspiration ratio to separate weather effects from ecosystem health. Cross-validated performance: R²=0.55, MAE=11 points, r=0.79.

Confidence Assessment

Confidence reflects the length of the assessment record and the availability of calibration data. Longer records (5+ years) provide HIGH confidence because they capture inter-annual variability and reveal genuine trends rather than single-year snapshots.

Assessment period: 8 years (2018-2025). Confidence: HIGH.

What Remote Sensing Can and Cannot Detect

Ecological Knowledge Base

The diagnostic interpretations in this report draw on a curated knowledge library of ecological principles. These include:

• Aspect-based seasonal management, how solar angle, slope, and aspect influence grazing timing, recovery periods, and drought vulnerability across the landscape.
• Brittleness ecology, the relationship between rainfall variability and ecosystem management requirements, following the Savory brittleness continuum.
• Diagnostic matrix framework, structured gap-pattern analysis linking process scores to root causes and management prescriptions by farming system.
• Keyline design principles. Yeomans-based water harvesting geometry for landscape water management.
• Soil management, soil health indicators, compaction dynamics, and organic carbon management principles.
• Vegetation indicator ecology, ecological interpretation of spectral indices and their relationship to ecosystem processes.
• Regional geology and soils, soil type characteristics and their implications for land management.

These principles are applied programmatically through the diagnostic matrix and inform the site-specific interpretations throughout this report. The knowledge base is maintained by Ecological Intelligence and draws on published ecological science.

Land Health Score

The headline metric, a property's overall ecological condition, given as a level from 1 (Collapsed) to 9 (Flourishing) with its band label.

Band

The name attached to each level: Collapsed, Depleted, Degraded, Stressed, Transitional, Recovering, Healthy, Thriving, Flourishing. Each band has one fixed colour.

EDX, Ecological Diagnostic Index

The underlying 0-100% index from which the Land Health Score level is derived. Used in methodology only.

EHI, Ecological Health Index

The composite that combines the four ecosystem-process scores into the EDX value.

Ecosystem processes

The four functional lenses assessed on the same nine-level scale: Water Cycle, Energy Flow, Mineral Cycle and Community Dynamics.

Evidenced · Positioned · Baseline · Documented

Confidence language for each finding, from multiple corroborating signals (Evidenced) through to recorded but not yet corroborated (Documented). This report never uses pass / fail.

VVB, Validation & Verification Body

An accredited third party that verifies carbon or biodiversity claims for market use.

EDX Land Health Score

The Land Health Score classifies each property into one of nine bands. EDX is the technical name for the band number, so “EDX8 Thriving” is the same as “Land Health Score Level 8”. The entries below describe each band in detail: the ecological characteristics that define it, the typical process score ranges, and the practical steps required to move up to the next band. For an at-a-glance comparison across all nine bands see Section 1.4.1 of the Master Report; for this site’s current band see Section 2.2 of the Master Report.

See the concept introduction in Section 1.4.1 of the Master Report and Section 2.2 of the Master Report for the site-specific reading.

EDX9, Flourishing

Ecosystems not only resilient but actively improved by disturbance, with highly efficient water infiltration, negligible erosion, vigorous canopy with strong solar energy capture, and diverse communities where rare species thrive. Water cycles effectively with minimal runoff, soils remain stable under stress, and functional groups are vigorous across the full diversity spectrum. This represents the pinnacle of ecological health where the system builds capacity through interaction with its environment.

Path to improvement: EDX9 represents optimal function. Maintain through adaptive management that responds to system feedback, protect rare species habitat, continue monitoring for early warning signals, and share knowledge with broader community to support regional ecosystem health.

EDX8, Thriving

Ecosystem processes are efficient and mutually reinforcing, creating robust ecological health that recovers quickly from disturbance. Good water infiltration with rare erosion events, stable soils showing no active degradation, high photosynthetic biomass production, and well-structured communities with low undesirable species presence. Systems at this level maintain function through normal climate variability and disturbance events.

Path to improvement: To reach EDX9: Enhance habitat complexity for rare species, eliminate remaining stress points in seasonal dips, fine-tune intervention timing to phenological and moisture cycles, increase functional group diversity in weak areas, and build deeper soil organic matter reserves through strategic carbon inputs.

EDX7, Healthy

Good infiltration, stable soils, strong canopy growth, and healthy community dynamics characterize this band, representing solid ecosystem function suitable for sustained productivity. Water cycles are mostly effective with occasional limitations, soils are predominantly stable, photosynthesis is robust with only short stress-related dips, and functional groups are healthy with rare species appearing occasionally. This is the threshold where regenerative management typically aims to maintain or exceed.

Path to improvement: To reach EDX8: Address seasonal stress periods with better recovery management, increase litter cover uniformity across landscape, strengthen water infiltration in limited areas, boost functional diversity in weaker zones, and refine disturbance timing to match plant vigor cycles for faster recovery.

EDX6, Recovering

Ecosystem cycles are mostly working but with limited resilience and patchy diversity, indicating improvement from lower states but not yet fully functional. Some runoff events occur during heavy rainfall, minor soil instability is beginning to show, canopy exhibits evident seasonal stress dips, and some functional groups show weakness or patchiness. Land in this band is on a positive trajectory but requires continued management attention.

Path to improvement: To reach EDX7: Reduce bare ground exposure through improved canopy cover and understorey density, extend non-intervention periods between operations, address weak functional groups through enrichment planting or habitat creation, improve water distribution to eliminate dry spots, and build soil organic matter through increased litter retention and reduced soil disturbance.

EDX5, Transitional

Some ecosystem processes are holding while others are weakening, creating uneven canopy cover and diversity across the landscape. Runoff is frequent during storms, localized erosion and soil capping appear in vulnerable areas, canopy is uneven with variable vigor, and undesirable species are beginning to increase. This band represents a critical threshold where management decisions will determine whether the system improves toward EDX6 or weakens toward EDX4.

Path to improvement: To reach EDX6: Urgent need to stop degradation trend. Immediately reduce soil disturbance, dramatically increase ground cover through enrichment planting and assisted natural regeneration, address erosion hotspots with targeted interventions, extend non-intervention periods significantly, and reduce harvesting pressure to allow ecosystem recovery. This is the last easy intervention point before major restoration becomes necessary.

EDX4, Stressed

Patchy vegetation cover, stuttering ecosystem cycles, and weakening functional group integrity characterize this vulnerable state. Water infiltration is poor with frequent sheet flow across the surface, pedestals begin to appear around plant bases indicating active soil loss, canopy is thin with patchy litter distribution, and key functional groups are noticeably weakening. Systems in this band are highly vulnerable to further degradation without significant management intervention.

Path to improvement: To reach EDX5: Major management redesign required. Cease all extractive operations and implement canopy retention, establish emergency ground cover through pioneer nurse species, address all visible erosion with mechanical and biological fixes, implement non-intervention zones for worst areas, introduce missing functional groups through assisted natural regeneration, and develop long-term soil rebuilding strategy. Expect 3-5 year recovery timeline with intensive inputs.

EDX3, Degraded

Poor water infiltration, visible erosion signals, low photosynthetic capacity, and rising dominance of undesirable species indicate significant ecosystem dysfunction. Regular runoff and rill formation occur, erosion indicators are common across the landscape, biomass production is low with slow recovery from disturbance, and undesirable species are becoming common while rare species are rarely seen. Land in this band requires comprehensive management redesign to prevent further decline.

Path to improvement: To reach EDX4: Comprehensive restoration program essential. Halt all extraction immediately, implement mechanical erosion control structures, establish pioneer nurse species for canopy rebuilding and soil stabilisation urgently, protect remaining seed trees as mycorrhizal refugia, consider importing topsoil for worst areas, develop 5-10 year restoration plan with staged interventions, seek expert guidance and potentially external funding. Economic returns unlikely for many years - focus must be on stopping collapse.

EDX2, Depleted

Severe weakening of water and mineral cycles, weak canopy, and failing diversity indicate land on the edge of collapse requiring urgent intervention. Little water infiltrates with most rainfall lost to runoff, active erosion with widespread soil surface capping, low photosynthetic activity producing minimal biomass, and functional groups actively failing with sharply reduced diversity. Without immediate management changes, systems in this band are likely to collapse to EDX1.

Path to improvement: To reach EDX3: Emergency restoration required. Total cessation of all disturbance mandatory, intensive mechanical stabilisation of erosion features, emergency planting of nurse species and pioneer trees with mycorrhizal inoculation where networks have been destroyed, potential need for irrigation support in establishment phase, soil amendment programs to restart biological activity, professional restoration expertise essential. Timeline 10+ years, significant investment required. Consider whether restoration is economically viable or if alternative land use needed.

EDX1, Collapsed

Water runs off immediately, severe soil erosion is active, canopy is nearly absent or dominated by standing dead material, and ecological communities have collapsed toward a handful of stress-tolerant species. Flashy water loss occurs with every rainfall event, erosion is severe and ongoing, bare ground or dead vegetation dominate the landscape, and biological diversity has effectively collapsed. This represents complete ecosystem dysfunction requiring intensive, long-term restoration intervention.

Path to improvement: To reach EDX2: Requires intensive, long-term restoration commitment. Engineering solutions essential for hydrological stabilisation - terracing, check dams, retention structures. Imported soil substrate and mycorrhizal inoculum likely necessary. Phased assisted regeneration with pioneer nurse species and intensive irrigation for establishment. May require 15-20+ years and investment exceeding land value. Alternative consideration: managed retreat to less intensive land use, conservation easement, or habitat restoration with public funding support. Traditional productivity may not be recoverable.

Other Terms

Brittleness

See the concept introduction in Section 1.4.3 of the Master Report and Section 3.5 of the Master Report for the site-specific reading.

Understanding Brittleness

All terrestrial environments fall somewhere along a continuum from non-brittle to very brittle.⁴ Environments can be classified along this continuum according to how well humidity is distributed throughout the year, and how quickly dead vegetation breaks down, rapidly through biological decay in non-brittle environments, or slowly through weathering and physical breakdown in brittle ones. This distinction is fundamental because it determines which management tools will be effective and which will cause harm.

In non-brittle environments (1-3 on the scale), reliable year-round moisture supports continuous biological decomposition. Dead plant material breaks down rapidly through fungal and invertebrate activity. Rest, the absence of disturbance, is a powerful regeneration tool because biological processes operate continuously. In brittle environments (7-10), moisture is erratic and unreliable. Dead material accumulates rather than decomposing, creating fuel loads. Rest alone cannot regenerate these landscapes, planned disturbance (including animal impact) is required to cycle nutrients.

Key Management Principle

One way to think about regeneration is as cycles of impact and rest. The impact must deliver a well-timed disturbance that creates maximum positive stress. The right period of recovery and rest can then work with the consequence of the impact, plant life and soil life will now lean in.

Very non-brittle (1-2)

In very non-brittle environments, rainfall is highly reliable and biological decomposition runs continuously through the year. Risk sits at the opposite extreme to brittle land: undisturbed rest combined with high productivity can produce rank growth and litter mats, so the management lever is selective disturbance and species diversity rather than rest.

Non-brittle (2-4)

In non-brittle environments, biological processes work continuously to build soil health. The balance tips towards rest. Longer recovery periods between disturbances allow fungi, invertebrates, and mycorrhizal networks to do the heavy lifting of decomposition and nutrient cycling.

Semi-brittle (4-6)

In semi-brittle environments, the balance between impact and rest shifts. Seasonal moisture patterns mean biological processes slow during dry periods. Time disturbances to coincide with reliable moisture windows so that recovery can begin immediately.

Brittle (6-8)

In brittle environments, rest alone cannot regenerate the land. Without disturbance, dead material accumulates rather than decomposing, creating fuel loads. Planned impact, including animal impact, is required to cycle nutrients and break down standing dead material.

Very brittle (8-10)

In very brittle environments, active intervention is essential. Passive restoration cannot reverse degradation. Water harvesting, nurse species, and soil rehabilitation are required. All interventions are opportunistic; pre-position for deployment when rains arrive.

Recovery Periods by Land State

Permanent Grassland

• Grassland: Recovery between grazing events typically 30-90 days depending on season and growth rate.
• Longer rest in the growing season (60-90 days) allows root reserves to rebuild and seed heads to set.
• Shorter rest in dormancy (30-45 days) prevents excessive litter accumulation that can smother new growth.
• Soil biology responds rapidly, fungal networks can re-establish within one growing season if compaction is avoided.

Wood Pasture

• Silvopasture: Trees provide the long-term structural framework; grazing manages the understorey.
• Recovery between grazing events: 45-120 days to protect tree regeneration and understorey diversity.
• Canopy interventions (thinning, pollarding) on longer cycles: 5-15 years for broadleaf, 15-25 for oak.
• Mycorrhizal networks connecting trees and grasses are the engine of nutrient cycling, minimise soil disturbance.

Woodland

• Woodland: Recovery operates on longer timescales than open ground.
• Understorey recovery: 2-5 growing seasons after coppicing or selective thinning.
• Canopy closure after gap creation: 10-25 years depending on species and light availability.
• Deadwood retention is critical, fungi decompose fallen wood over 5-15 years, recycling nutrients into the soil.

How the Score is Calculated

EcoIntel computes brittleness from reanalysis climate data. Precipitation CV (coefficient of variation) measures month-to-month rainfall variability across all assessment years. A low CV means rainfall is evenly distributed; a high CV means it arrives in bursts separated by dry periods.

The precipitation CV is converted to a raw brittleness score using a piecewise mapping, then adjusted for ecoregion. The zone baseline reflects the regional climate norm. The final score blends the precipitation-derived value (70%) with the zone baseline (30%).

The brittleness score and precipitation CV are related but distinct measures. The CV is a pure statistical measure of rainfall variability. The brittleness score incorporates the CV but also adjusts for regional context, a CV of 0.5 in Atlantic Britain (where the baseline expectation is reliable rainfall) has different ecological implications than the same CV in the Mediterranean (where seasonal drought is the norm). The score reflects the ecological meaning of the variability, not just the variability itself.

For general illustration, the chart below shows how synthetic daily rainfall patterns differ across brittleness levels. Non-brittle climates (green) have consistent small rainfall events throughout the year. Semi-brittle climates (gold) show distinct wet and dry seasons. Brittle climates (orange) have long dry periods punctuated by intense downpours.

How to read this table alongside the headline score: the table shows the RAW brittleness score derived from CV alone. The score reported in the property profile is the FINAL ecoregion-adjusted score, blending the raw value (70%) with the regional zone baseline (30%). A site whose raw value lands in one band can be reported in an adjacent band once the regional context is applied; the headline category in the property profile is always the final classification.

This Strategic Action Brief is one of four deliverables in the EcoIntel Land Health Report suite. The demonstration property is Wilder Wood Farm; the same analysis applies to any property with at least 1 hectare and 5 years of satellite-observable history.

• Same satellite stack, same scoring engine, same prose.
• Typical turnaround: normally within hours but within 2 working days.

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Land Health Reports are produced by EcoIntel’s analytical pipeline: 12-platform satellite data integration with AI-synthesised ecological interpretation, calibrated to your property’s regime and ecoregion.