Kingdom of Saudi Arabia · National Agricultural Land Evaluation · Module 3 of 4

Land Suitability
for a Named Crop

Capability asks whether land can support farming at all. Suitability asks how well one specific crop would do on it. The same measurements are read again — this time against each crop’s own tolerance rather than a general threshold. The class is always set by the single worst factor, never by an average.

Diagnostic Factors26 across 6 groups
Result ClassesS1 → S2 → S3 → N1 → N2
How the Class is SetThe single worst factor decides
Production Systems8 assessed separately
FrameworkFAO Bulletin 55 · ALUES / Sys et al.
Capability and Suitability measure the same land qualities. What differs is the requirement they are compared against. Salinity is salinity — one measurement on a hectare. Capability asks whether that reading is a problem for farming in general. Suitability asks whether it is a problem for date palm specifically, then for tomato, then for wheat — and the answer differs for each crop, because each tolerates a different amount. Suitability does not re-measure anything. It re-reads Capability’s outputs against a crop-specific tolerance ruler.
Why 26 factors here and 19 in Capability. Suitability assesses more factors than Capability because it re-reads every land quality against each crop’s tolerance and adds crop-only requirements that do not exist at the capability stage — irrigation demand, crop nutrient requirement, and the chemical factors that only bite at crop-specific thresholds. The larger count is the design, not an inconsistency.
Capability asks

Is this measurement a problem for farming in general? Uses a general physical threshold. One class per hectare, any land use.

Suitability asks

Is this measurement a problem for this named crop? Uses a crop tolerance table. One class per hectare per crop — the same hectare can be S2 for date palm and S3 for tomato.

S–N Classes S1 — Highly Suitable S2 — Moderately Suitable S3 — Marginally Suitable N1 — Currently Not Suitable N2 — Permanently Not Suitable
Subclass letters: s soil physical z salinity / sodicity n nutrient / toxicity w water / drainage f flood hazard t terrain / topography e erosion hazard d sand drift c climate i irrigation demand ★ ★ new in Suitability
The subclass letter identifies the group, not the individual factor. With 26 factors and 10 letters, a letter cannot say which factor is binding — six factors share s, five share n, five share c. This is a known FAO limitation, handled the same way the Capability and Land Rights & Constraints modules handle it: the subclass letter travels on the map and in summary tables; the specific limiting factor is named in full in the zone record and the attribute table. A result reads S3s on a map, and “S3 — limited by rooting depth” in the location detail.

Select a diagnostic factor to view per-crop tolerance thresholds, Capability cross-reference, and assessment method.

Irrigated Open-Field
Annual crops grown in the ground, watered from a managed supply.
Minimum viable area50 ha for centre pivot · smaller for surface and drip layouts
Distinguishing featureThe reference case. Every factor is read, and the crop threshold library applies in full.
What is being evaluated
The crop species. All 26 factors are read against that crop’s own tolerances.

Irrigation method — how it changes which factors bite

Drip
Water delivered to the root zone. Foliage never wetted.
Chloride tolerance rises — SQ-B-04 and water chloride are read against the soil pathway only, not foliar burn. Slope tolerance is highest of the four methods: drip works on ground a pivot cannot cross. Highest capital cost per hectare, lowest water demand.
Sprinkler
Overhead application. Foliage is wetted at every irrigation.
Chloride and sodium become foliar risks, not just root-zone risks. FAO-29 applies stricter limits under sprinkler than surface application for the same water. Wind speed matters for distribution uniformity — a factor no current element captures.
Centre pivot
Self-propelled circular system covering 50–125 ha per unit.
Imposes a minimum area and a shape. SQ-D-01 terrain becomes binding well before it would for drip — the tower must traverse the whole circle. Sub-50 ha blocks are not viable regardless of every other factor.
Surface / flood
Water moved across the field by gravity.
Requires near-level ground: SQ-D-01 is the governing factor. Demands high water volume, so SQ-F-01 irrigation demand and the water module’s volume parameters bind hardest. Salinity accumulates faster without a controlled leaching fraction.

All 26 factors — and how delivery method changes each

System columnGoverns — can set the class on its ownConditional — depends on the system or setupDoes not applyMethod columnsAmplified — binds harder under this methodStandard — behaves as it does for the system generallyReduced — the method mitigates this factorInverted — the method turns the factor into a capabilityRead a row across: the system column is the base mark, the four method columns show how that behaviour shifts with delivery. The method marks describe the direction of effect — whether a factor bites harder or less hard under each delivery method.
Code Diagnostic factor This
system
Shift by delivery method
DripSprinkler Centre pivotSurface / flood
A · Soil Physical
SQ-A-01Available Water Capacitys
Surface applies large volumes infrequently, so the soil must store between irrigations. Drip refills the root zone daily and compensates for low holding capacity.
SQ-A-02Soil Workabilitys
Surface irrigation requires land levelling before the first crop. Workability governs the cost of that operation; the other three methods do not need it.
SQ-A-03Rooting Conditionss
SQ-A-04Surface Sealing & Crustings
Sprinkler and pivot droplets strike bare soil and drive crust formation. Drip never wets the surface between emitters.
SQ-A-05Soil Textures
Texture sets the infiltration rate, which determines furrow length and basin size in surface systems. Under drip the emitter rate is set independently of the soil.
SQ-A-06Coarse Fragmentss
Tower wheels and levelling equipment both suffer on stony ground. Drip lines are laid over it.
B · Soil Chemical
SQ-B-01Salinity (ECe)z
Sprinkler and pivot wet the foliage, adding a leaf-burn pathway to the root-zone effect. Surface accumulates salt fastest without a controlled leaching fraction. FAO-29 sets stricter limits for overhead application.
SQ-B-02Sodicity (ESP / SAR)z
Sodium collapses infiltration. That is fatal to surface irrigation, which depends on water moving across and into the profile; drip delivers under pressure to a point.
SQ-B-04Toxicity Risk (Boron)n
Boron is taken up through the root regardless of delivery method.
SQ-B-05Calcium Carbonaten
SQ-B-06Gypsum Contentn
Gypsum dissolves and can destabilise levelled basins and channels.
SQ-B-07Soil pHn
C · Water & Drainage
SQ-C-01Drainage Conditionw
Surface irrigation applies large volumes at once. Without free drainage the root zone stays saturated far longer than under any pressurised method.
SQ-C-02Flood Hazardf
SQ-C-03Waterlogging Riskw
Same reason as drainage — application volume per event drives the risk.
D · Topography & Erosion
SQ-D-01Terrain Workabilityt
The primary differentiator. Drip works on ground no other method can cross. Pivot towers must traverse the whole circle. Surface needs near-level ground and governs hardest of the four.
SQ-D-02Water Erosion Hazarde
Overhead droplet energy and surface flow both detach soil. Drip does neither.
SQ-D-03Wind Erosion Hazarde
Wind distorts sprinkler and pivot distribution uniformity as well as eroding soil — a compounding effect no current element captures.
SQ-D-04Sand Encroachment Hazardd
Emitters clog with wind-blown fines; pivot towers suffer mechanical damage from drifting sand.
E · Climate
SQ-E-01Moisture Deficit (Aridity)c
SQ-E-02Thermal Suitabilityc
SQ-E-03Radiation & Solar Energyc
SQ-E-04Length of Growing Period (LGP)c
SQ-E-05Frost Riskc
Inverted. Sprinkler and pivot systems are deliberately run during radiation frost — the latent heat released as water freezes on the plant holds tissue near 0 °C. Frost risk becomes a capability the method provides, not a limitation.
F · Crop-Specific
SQ-F-01Irrigation Demand (ETc)i
Application efficiency differs sharply: drip is the highest of the four, surface the lowest. The same crop demand becomes a different abstraction requirement.
SQ-F-02Crop Nutrient Requirementn
Fertigation through drip places nutrients in the wetted zone. Surface systems broadcast, and losses on a calcareous soil are higher.
24 factors govern this system and 2 are conditional — shown in the system column. Of the 26, eighteen behave differently depending on how water is delivered; those rows carry and open an explanation on click. The remaining eight are read identically under all four methods.
Orchard & Perennial
Tree and long-lived crops planted once and kept for decades.
Minimum viable area10 ha — harvest crews, grading and cold-chain handling do not amortise below this
Distinguishing featureThe distinguishing question is time. A 30-year planting must be matched against a water supply horizon, not just current availability.
What is being evaluated
The tree or vine species, assessed over its full productive life rather than one season.
Why the water finding binds harder here
A W2y source with a 28-year remaining horizon is adequate for an annual crop and marginal for a date palm planting that reaches full bearing at year 8 and yields for decades. The suitability class does not capture this — the water state must be read alongside it.
Rooting depth carries more weight
SQ-A-03 governs more strongly than for annuals. A shallow profile that a wheat crop tolerates for one season constrains a tree permanently, and the planting cannot be relocated.
How to readGoverns — can set the class on its ownQualifies — the hazard selects the siteConditional — depends on the system or setupDoes not apply — assessed, does not biteEvery factor is listed under exactly one heading below. The four headings together account for all 26 — a factor absent from one list appears in another.
Factors that govern this system22 of 26
SQ-A-01Available Water Capacity
SQ-A-03Rooting Conditions
SQ-A-05Soil Texture
SQ-A-06Coarse Fragments
SQ-B-01Salinity (ECe)
SQ-B-02Sodicity (ESP / SAR)
SQ-B-04Toxicity Risk (Boron)
SQ-B-05Calcium Carbonate
SQ-B-06Gypsum Content
SQ-B-07Soil pH
SQ-C-01Drainage Condition
SQ-C-02Flood Hazard
SQ-C-03Waterlogging Risk
SQ-D-01Terrain Workability
SQ-D-02Water Erosion Hazard
SQ-D-03Wind Erosion Hazard
SQ-D-04Sand Encroachment Hazard
SQ-E-02Thermal Suitability
SQ-E-03Radiation & Solar Energy
SQ-E-05Frost Risk
SQ-F-01Irrigation Demand (ETc)
SQ-F-02Crop Nutrient Requirement
Conditional — depends on the crop or the setup3 of 26
SQ-A-02Soil Workability
SQ-A-04Surface Sealing & Crusting
SQ-E-01Moisture Deficit (Aridity)
Does not apply1 of 26
SQ-E-04Length of Growing Period (LGP)
Assessed, and found not to bite. An empty cell would look unfinished; this states the question was asked.
Protected Agriculture
Greenhouse and shade-house crops grown in substrate.
Minimum viable area2 ha — high value per square metre makes small blocks commercially viable
Distinguishing feature16 of the 26 factors do not apply. Substrate cultivation bypasses the field soil entirely, which is why this system can develop land the open-field assessment rejects.
What is being evaluated
The crop species, but read against a controlled root environment rather than the field soil.
What the structure replaces
Soil physical and chemical factors are removed from the assessment because the crop never contacts the field soil. Salinity, sodicity, texture, carbonate, gypsum, pH, rooting depth and coarse fragments are all N/A — not favourable, simply not read.
What still governs
Terrain for construction, water quality for the irrigation solution, radiation, and the thermal envelope the structure must manage. Water quality governs more strictly than open field — there is no soil buffer to absorb salinity.
The consequence for land inventory
A hectare rated poor for open-field cropping on soil chemistry may be fully suitable for protected agriculture. This is the clearest case in the study of a system rescuing land another system rejects.
How to readGoverns — can set the class on its ownQualifies — the hazard selects the siteConditional — depends on the system or setupDoes not apply — assessed, does not biteEvery factor is listed under exactly one heading below. The four headings together account for all 26 — a factor absent from one list appears in another.
Factors that govern this system8 of 26
SQ-C-02Flood Hazard
SQ-D-01Terrain Workability
SQ-D-04Sand Encroachment Hazard
SQ-E-02Thermal Suitability
SQ-E-03Radiation & Solar Energy
SQ-E-05Frost Risk
SQ-F-01Irrigation Demand (ETc)
SQ-F-02Crop Nutrient Requirement
Conditional — depends on the crop or the setup2 of 26
SQ-B-04Toxicity Risk (Boron)
SQ-D-03Wind Erosion Hazard
Does not apply16 of 26
SQ-A-01Available Water Capacity
SQ-A-02Soil Workability
SQ-A-03Rooting Conditions
SQ-A-04Surface Sealing & Crusting
SQ-A-05Soil Texture
SQ-A-06Coarse Fragments
SQ-B-01Salinity (ECe)
SQ-B-02Sodicity (ESP / SAR)
SQ-B-05Calcium Carbonate
SQ-B-06Gypsum Content
SQ-B-07Soil pH
SQ-C-01Drainage Condition
SQ-C-03Waterlogging Risk
SQ-D-02Water Erosion Hazard
SQ-E-01Moisture Deficit (Aridity)
SQ-E-04Length of Growing Period (LGP)
Assessed, and found not to bite. An empty cell would look unfinished; this states the question was asked.
Rain-fed & Supplementary
Crops grown on rainfall, or on seasonal wadi flood water.
Minimum viable area20 ha — area averages year-to-year rainfall variance into a predictable return
Distinguishing featureViable only in the southwestern highlands and on wadi systems. Across most of the Kingdom rainfall alone cannot support a crop cycle.
What is being evaluated
The crop species, read against rainfall and stored soil moisture rather than a managed supply.
Flood hazard inverts here
SQ-C-02 is marked Conditional rather than Governs because spate irrigation deliberately farms wadi flood water. The same hazard that disqualifies an orchard is the water source for a spate system. The mark depends on whether the operation is designed to capture flow or to exclude it.
Moisture deficit is the binding factor
SQ-E-01 governs almost everywhere. This is the system where the version 10.1 change matters most — moisture deficit is now crop-keyed, so the threshold is the named crop’s water requirement rather than a general aridity cut.
How to readGoverns — can set the class on its ownQualifies — the hazard selects the siteConditional — depends on the system or setupDoes not apply — assessed, does not biteEvery factor is listed under exactly one heading below. The four headings together account for all 26 — a factor absent from one list appears in another.
Factors that govern this system23 of 26
SQ-A-01Available Water Capacity
SQ-A-02Soil Workability
SQ-A-03Rooting Conditions
SQ-A-04Surface Sealing & Crusting
SQ-A-05Soil Texture
SQ-A-06Coarse Fragments
SQ-B-01Salinity (ECe)
SQ-B-02Sodicity (ESP / SAR)
SQ-B-05Calcium Carbonate
SQ-B-06Gypsum Content
SQ-B-07Soil pH
SQ-C-01Drainage Condition
SQ-C-03Waterlogging Risk
SQ-D-01Terrain Workability
SQ-D-02Water Erosion Hazard
SQ-D-03Wind Erosion Hazard
SQ-D-04Sand Encroachment Hazard
SQ-E-01Moisture Deficit (Aridity)
SQ-E-02Thermal Suitability
SQ-E-03Radiation & Solar Energy
SQ-E-04Length of Growing Period (LGP)
SQ-E-05Frost Risk
SQ-F-02Crop Nutrient Requirement
Conditional — depends on the crop or the setup1 of 26
SQ-C-02Flood Hazard
Does not apply2 of 26
SQ-B-04Toxicity Risk (Boron)
SQ-F-01Irrigation Demand (ETc)
Assessed, and found not to bite. An empty cell would look unfinished; this states the question was asked.
This is the crop library. The Factors tab defines what is measured; the By Industry tab decides which factors a production system reads. This tab holds the other half of the equation — each crop’s own tolerances, the ruler that a measurement is read against. Select any crop to see its full ecological requirement record.
Status: All 63 crops now carry requirement data. 56 crops hold complete numeric S1–N thresholds — 1,268 records across 91 parameters, extracted from ALUES 0.2.1 and source-validated. 7 Saudi-priority crops hold full FAO ECOCROP ecological profiles. No crop is yet operational: production-system-specific thresholds still require Saudi calibration and expert approval before national release.

Select a crop to see its full ecological requirement record — temperature, rainfall, soil, light and production-system detail.

Aquaculture
Fish and shrimp production in ponds, tanks or cages.
Factor routing4 govern · 12 N/A · 10 conditional
What is being evaluated
Not a crop. Two things are evaluated: the site’s physical ability to hold water, and the water quality available for the species. The species set follows the water available — shrimp and marine finfish on the coast, tolerant freshwater species inland.
Factors that apply to every kind of aquaculture4
SQ-C-02Flood HazardPonds and dikes have to survive a flood. On a wadi it can also be the fill source.
SQ-D-01Terrain WorkabilityPonds need flat ground. A slope means far more earth to move.
SQ-D-04Sand Encroachment HazardDrifting sand fills ponds and blocks intakes.
SQ-E-02Thermal SuitabilityWater temperature drives growth rate and decides which species can be kept.
Factors that apply to some kinds only10
SQ-A-05Soil TextureClay holds water in and makes strong banks. Sand does neither, so a sand site needs a liner.
SQ-B-06Gypsum ContentGypsum dissolves and can undermine dikes and pond floors.
SQ-B-07Soil pHPond soil pH affects water chemistry and how well natural food grows.
SQ-C-01Drainage ConditionA pond with no liner needs ground that keeps water in. Ground that drains well lets the pond empty into the subsoil.
SQ-D-02Water Erosion HazardRunoff can breach dikes and silt up ponds.
SQ-D-03Wind Erosion HazardWind drives evaporation and blows sand into the water.
SQ-E-01Moisture Deficit (Aridity)Evaporation from an open pond is a permanent loss that has to be replaced.
SQ-E-03Radiation & Solar EnergySunlight grows the plankton in the pond. This matters most where the fish feed on it rather than on pellets.
SQ-E-04Length of Growing Period (LGP)Sets how many months a year the water is warm enough to grow stock.
SQ-E-05Frost RiskCold water stops growth and can kill warm-water species.
These bite for earthen ponds, where the ground itself holds the water. They do not bite for lined ponds, tanks or cages, where it does not.
+Elements to add for aquaculture3
SQ-D-05Coastal positionDistance to the shore and height above sea level, together. Decides whether seawater can reach the site, and whether ponds fill and drain by gravity or need pumps running all the time.
WP-A-01 · WOMarine water sourceA seventh source code for seawater. The six existing codes are all inland. Seawater does not run out, does not fall in level and is not allocated from a basin, so it cannot be recorded as any of them.
SQ-D-06Tide rangeHeight difference between high and low water. Sets how deep the pond floor must sit and whether it can be drained without pumping.
The three ways aquaculture is done
How it works
Earthen ponds are dug into the ground and banked with the excavated soil. They fill from a well, canal or wadi, and are drained to harvest.

A pond is a small living system. It is not simply a tank of water. Nutrients in the water and the bottom soil grow microscopic plants; those feed tiny animals and insect larvae; the fish eat those. So the soil is not just a container — it is the base of the food chain. This is why a pond can be fertilised: the fertiliser grows the plankton, and the plankton feeds the fish.
What a pond actually is
A rectangular basin excavated into the ground, typically 0.5–2 ha and 1–1.5 m deep. The soil dug out is used to build the banks, so the excavation and the wall come from the same operation. It is filled from a well, canal or wadi and drained completely at harvest.
The basinThe hole itself. Its floor is graded to fall gently toward the outlet so the pond can be emptied by gravity.
The dikesThe raised banks holding the water. Built from the excavated soil, compacted in layers. Wide enough on top for a vehicle on at least one side.
The inletPipe or channel bringing water in, usually with a screen to keep wild fish and debris out.
The outlet / monkA gated structure at the low point. Lets the operator drop the level, drain fully at harvest, and skim water from a chosen depth.
The pond bottomNot just a floor. Nutrients in the soil grow the plankton the fish feed on, so the bottom is a working part of the farm.
What "lined" meansLined means an impermeable barrier is installed between the water and the soil, so the soil is no longer what holds the water in. The hole, the dikes and the outlet are unchanged — only the containment moves from the ground to a manufactured layer. Common forms are a welded HDPE sheet, a bentonite clay blanket that swells and self-seals, or imported clay compacted in place. Partial lining is common — floor lined and dikes left earthen, or the reverse — which is why the sub-system does not split cleanly in two.
If the pond is not lined, the soil is what holds the water in. If it is lined, the soil only gives the pond its shape.
Why does the soil matter if you can line the pond?
A pond can be lined. If it is, the liner holds the water in and the soil no longer has to.

But clay leaks about as little as a liner does. Build on clay and the pond holds water on its own, with nothing added. Build on sand and it does not — sand leaks roughly a hundred times faster, so a liner has to go in before the pond can be used at all.
How the pond is builtWater lost through the bottom, m³/ha/yr
Unlined sand92,700–927,000
Unlined clay927–9,271
Bentonite liner927–4,636
HDPE sheet0–93
Concrete0–93
Compare it with evaporation, which takes about 22,500 m³/ha/yr in the Kingdom. On clay, what leaks through the bottom is about a quarter of that — small beside it. On sand it is 22 times more than evaporation. No water supply can keep up with that.
A liner does not remove the soil from the picture. The banks are still built from the soil dug out, and they have to hold their own weight and the water behind them. The ground still has to be firm enough to dig and shape. A liner changes none of that.

And a liner covers the pond bottom. That is where the natural food grows, so a lined pond has to be fed more to reach the same yield.
Scale and production
Typical pond0.5–2 ha each, water 1–1.5 m deep
Water — flow-through5 l/sec/ha ≈ 157,000 m³/ha/yr (FAO)
Water — recirculating≈ 21,000–34,000 m³/ha/yr in KSA conditions
Initial fill≈ 12,500 m³/ha at 1.25 m depth
Yield — natural food onlyUnder 1 t/ha/yr
Yield — water fertilised1–2 t/ha/yr
Yield — fertilised + fed3–10 t/ha/yr
The fertiliser goes into the water, not onto a crop. It blooms the plankton that the fish graze on — the three yields above are three different food sources, not three feeding rates. Fertilising roughly doubles what natural productivity alone supports; adding manufactured pellets lifts it again by several times.
Intensive shrimp3–6 t/ha/yr at 10–30 shrimp per m²
Read the two water figures carefully. They are not alternatives for the same design. The flow-through figure assumes water is discharged after a single pass; the recirculating figure assumes it is treated and returned, so only evaporation and seepage are replaced. Which one applies is an engineering choice, and it changes the abstraction licence by a factor of six.
What limits it
The soil must hold water. A pond on sandy ground leaks faster than it can be filled. That single requirement rules out most of the Kingdom’s open desert.

How much water a pond farm uses depends on how the pond is designed, not on how many fish are in it. The FAO figure of 5 l/sec/ha is for a flow-through pond, where water runs through continuously to carry waste away. That is 157,000 m³/ha/yr — about 12 complete pond exchanges a year. A pond that recirculates through a settling basin or biofilter does not need that: it only replaces what it physically loses.

In the Kingdom what it loses is mostly evaporation. At roughly 2,000–2,500 mm a year from an open surface, plus modest seepage through clay, a recirculating pond still needs 21,000–34,000 m³/ha/yr — six times less than flow-through, but far from nothing. Evaporation alone is comparable to the irrigation demand of a field crop on the same hectare.

Ground must be near level. On a slope far more earth has to be moved to get a flat basin, and draining the pond by gravity only works if the bottom sits above the outlet.
Environmental impact to watch
EffluentPond water carries feed residue, fish waste and any fertiliser added to bloom the plankton. Discharged untreated it enriches whatever receives it — the same nutrients that grow food inside the pond cause algal blooms outside it.
Soil salinisationRepeated filling and evaporation concentrates salt in and around the pond. Land beside a pond can degrade over years.
Groundwater drawIn the Kingdom the fill and makeup water is pumped. Even a recirculating pond abstracts continuously to replace evaporation, competing with irrigation on the same aquifer. A flow-through design competes six times harder.
SludgeOrganic matter accumulates on the bottom and must be removed between cycles. Where it is put matters.
How it works
Fish are held in tanks inside a building. The same water circulates continuously through filters that strip out waste and add oxygen, so only a small fraction is replaced each day. The system is engineered from end to end — nothing depends on the site’s natural conditions.
What a tank / RAS system actually is
Fish are held in tanks — usually circular, in concrete, fibreglass or coated steel — inside a building. The same water circulates continuously through a treatment loop and returns to the tank, so only a small fraction is replaced each day. RAS stands for recirculating aquaculture system.
The tanksCircular is standard: the rotating flow sweeps solids to a central drain and keeps the fish swimming evenly.
Mechanical filterScreens or a drum filter removing solid waste and uneaten feed before it breaks down.
Biological filterThe heart of the system. Bacteria growing on a high-surface-area medium convert ammonia from the fish into nitrate, which is far less toxic.
OxygenationFish at high density consume oxygen faster than the water can absorb it from air. Pure oxygen or intensive aeration is injected continuously.
DegassingStrips out carbon dioxide the fish exhale, which would otherwise acidify the water.
DisinfectionUV or ozone, controlling pathogens in a closed loop where disease would otherwise spread through the whole stock.
Is it lined? — There is nothing to line. The tank is a manufactured vessel standing on a prepared floor, and the ground beneath it carries load rather than water. The site question becomes bearing capacity, power supply and effluent disposal — not soil texture or drainage.
The site only needs to give a firm floor, an electricity supply and a drain. Nothing about the soil or climate affects the fish.
Scale and production
Water reuseLess than a tenth of what a pond of the same output would use
Stocking densityAround 70–120 kg per cubic metre
FootprintMuch less land than a pond farm needs to produce the same amount
SitingIt can be built near the market, because it does not need to be near a water source
ControlTemperature and water quality are held steady all year
What limits it
Everything has to be built and nothing comes from the site. Tanks, filters, pumps and oxygen supply all have to be installed before a single fish is stocked. This is the main reason RAS has not spread widely outside developed markets.

Power is continuous and non-negotiable. Pumps, filters and oxygenation run without pause. An interruption of hours can kill the entire stock.

It needs trained operators. The biological filter is a living system. Mismanage it and water quality collapses quickly, with no pond volume to buffer the error.
Environmental impact to watch
EnergyThe burden shifts from water to electricity. On a grid running on fossil fuel, a RAS farm carries a real carbon footprint.
Concentrated wasteVery little water leaves, but what does is highly concentrated. It has to be treated before it leaves the site. It cannot simply be discharged.
Sludge disposalSolids removed by the filters accumulate as a continuous waste stream requiring a disposal route.
BrineWhere the source is brackish or the system uses saline water, reject brine needs somewhere to go — the same problem desalination faces.
How it works
Net cages float in open coastal water. Fish are fed inside them and waste passes straight through the mesh into the sea, which dilutes it. Nothing is built on land except the shore base.
What a marine cage actually is
A net bag suspended from a floating collar in open coastal water. Fish are fed inside it, and waste passes through the mesh into the sea, which disperses it. Nothing is built on land except the shore base.
The collarA floating ring, commonly HDPE pipe, holding the cage open at the surface and providing a walkway.
The netThe containment itself. Sized by species and stocking, weighted at the base to hold shape against current.
The mooringAnchors and lines holding the cage on station. The heaviest engineering in the system, and what fails first in a storm.
Predator netAn outer net keeping seals, sharks and birds off the stock net.
Feed systemBarge or shore-fed pipework. Feeding is the main daily operation.
The shore baseJetty, feed store, handling and cold chain. This is the only part that occupies land.
Does lining apply? — The concept does not apply. The sea is the container. The site question is depth beneath the cage, current speed, shelter from storm, and what the seabed can absorb — none of which the hectare grid assesses, because the grid stops at the coast.
A cage site is judged by the water it sits in, not by any land. This study measures land only, so it cannot score cage sites.
Scale and production
DensityRoughly 100–300 kg per cubic metre of cage
Yield by cage areaCan reach 100 t/ha of cage surface
Yield by water bodyAbout 1 t/ha once the surrounding water that dilutes the waste is counted in
Site needsShelter from storms, sufficient depth beneath the cage, and current to carry waste away
Land neededOnly a base on shore, holding the feed store, jetty and handling area
What limits it
This is not a land question. The hectare grid does not reach the sea, so no cell in this study can be assessed for cage siting. It is listed here for completeness of the sector.

The site must be sheltered but not still. Too exposed and cages are lost to storms; too enclosed and waste accumulates beneath them.

Coastal space is contested. Shipping, tourism, ports and conservation designations all compete for the same water.
Environmental impact to watch
Seabed beneath the cagesUneaten feed and faeces settle directly below. Without adequate current and depth the sediment goes anoxic.
EscapesFarmed fish that escape can interbreed with or displace wild populations.
Disease and parasitesDense stock in open water can transfer disease to wild fish passing through.
Chemical useTreatments applied in the cage disperse into the surrounding water, unfiltered.
How it works
Ponds built on flat coastal land, filled with seawater pumped in from the sea. The water is cleaned on the way out and returned. This is how nearly all Saudi aquaculture is done. It looks like a pond farm and behaves like one, but it draws on the sea instead of an aquifer.
What a coastal farm actually is
A chain of ponds running from the sea and back to it: take water in, settle it, grow in it, clean it, return it.
The intakePumps or a canal bringing seawater in from beyond the surf line. On the biggest farms this is the largest single piece of engineering.
Reservoir pondsSeawater is held and settled before it reaches the fish, so sand and silt drop out first.
Grow-out pondsWhere the shrimp or fish are kept. Often round with a drain in the middle, so aerators push the waste to the centre.
Treatment pondsWater leaving the grow-out ponds is cleaned in further ponds before it goes back to the sea. On some farms this takes as much land as the production itself.
The outfallWhere treated water returns to the sea. Placed well away from the intake so the farm does not draw back its own discharge.
The sea provides the water and also receives it back. A site needs a good place to take water in and a separate place to return it.
Scale and production
Pond size1–10 ha each, often round with a centre drain
Water sourceSeawater at full strength. No fresh water is used at all
Intake scaleUp to 90 m³/second on the largest farms
Land for cleaningThe cleaning ponds can take as much land as the production ponds, or more
Shrimp yield15–20 t/ha/yr reported on Red Sea farms
SpeciesMostly shrimp, and some barramundi
What limits it
It has to be close to the sea and low down. Every metre of height and every kilometre inland adds pumping that never stops.

Flat land near the shore is limited. The coastal strip is narrow, and ports, tourism and conservation want the same ground.

Both ends have to work. A site needs somewhere to draw clean seawater from and somewhere to return it, far enough apart that the farm does not take back its own discharge.
Environmental impact to watch
Return waterEverything taken from the sea goes back to it. Cleaning it first is the whole reason treatment ponds exist.
Mangrove and shorelineCoastal habitat is easily lost to pond construction. Once cleared it does not come back quickly.
Intake and outfall placingPut them too close together and the farm recycles its own waste.
Salt in the groundPonds of seawater sitting on land will salt the soil around and beneath them.
Livestock & Grazing
Rangeland grazing, fodder production and animal husbandry.
Factor routing5 govern · 4 N/A · 17 conditional
What is being evaluated
Not a crop, and not the animal. What is assessed is the forage resource — what the land can produce and sustain — plus stock water and heat stress.
Factors that apply to every kind of livestock production5
SQ-D-02Water Erosion HazardOvergrazing strips cover and the soil washes away. The land loses what feeds the animals.
SQ-D-03Wind Erosion HazardBare rangeland blows away. Wind erosion is what turns grazing land into desert.
SQ-D-04Sand Encroachment HazardMoving sand buries the plants animals feed on.
SQ-E-01Moisture Deficit (Aridity)Rainfall decides how much grass and browse grows, and so how many animals the land can carry.
SQ-E-04Length of Growing Period (LGP)Sets how many months a year there is anything green to eat.
Factors that apply to some kinds only17
SQ-A-01Available Water CapacityThis matters where fodder is grown. Native rangeland plants already suit the soil they grow in.
SQ-A-03Rooting ConditionsThis matters for sown fodder. Native shrubs root much deeper than any crop does.
SQ-A-04Surface Sealing & CrustingA crust stops seedlings coming up when rangeland is reseeded.
SQ-A-05Soil TextureDecides what grows naturally and whether fodder can be established.
SQ-B-01Salinity (ECe)Salt limits what fodder crops will grow. Many native range plants tolerate much more of it.
SQ-B-02Sodicity (ESP / SAR)This affects sown fodder. Native plants are generally less affected by it.
SQ-B-05Calcium CarbonateIt locks up nutrients where fodder is grown. It has less effect on natural grazing.
SQ-B-06Gypsum ContentIt affects sown fodder more than it affects native plants already growing.
SQ-B-07Soil pHDecides which fodder species will establish.
SQ-C-01Drainage ConditionThis matters where fodder is irrigated. Rangeland rarely holds enough water for it to be a problem.
SQ-C-02Flood HazardFlooding damages fodder fields and fencing. On rangeland, seasonal flood water often grows the best grazing.
SQ-C-03Waterlogging RiskThis affects fodder fields. It rarely happens on dry rangeland.
SQ-D-01Terrain WorkabilityGrowing fodder needs flat ground for machinery. Animals can graze slopes that a tractor cannot cross.
SQ-E-02Thermal SuitabilityHeat limits fodder growth, and also stresses the animals themselves.
SQ-E-05Frost RiskFrost stops fodder growth and can kill young stock.
SQ-F-01Irrigation Demand (ETc)This only applies where fodder is irrigated. Natural grazing is not irrigated.
SQ-F-02Crop Nutrient RequirementThis applies to fodder crops. Native range plants already grow in poor soil.
Almost all of these bite for grown fodder and not for natural grazing. Fodder is a crop and reads the crop thresholds; rangeland is native vegetation already suited to the ground it grows on.
+Elements to add for livestock4
SQ-G-01Carrying capacityHow many animals a hectare can feed without degrading. The core measure for grazing, and unlike every other factor it is a productivity estimate rather than a threshold comparison.
SQ-G-02Stock water requirementWater for the animals to drink. Far smaller than irrigation but never zero, and it decides how far stock can range from a water point.
SQ-G-03Heat stress on animalsTemperature and humidity as the animal experiences them. All current thermal factors are read for plant growth. None asks whether the animal can tolerate the conditions.
SQ-G-04Distance to water pointHow far an animal must walk to drink. Grazing concentrates near water and degrades there first. The spacing of water points shapes the whole grazing pattern.
The three ways livestock is kept
How it works
Animals graze native plants across open country. Nothing is planted and nothing is irrigated. The herd moves to follow what has grown after rain.
Scale and inputs
Minimum areaAbout 1,000 ha — arid rangeland carries too few animals to manage smaller
StockingFew animals per hectare, and the number changes with the season and the rainfall
InputsNothing is added to the land itself
AnimalsCamels, sheep and goats
What the land givesGrass and shrub leaves that are already growing there
What limits it
Rain decides everything. A dry year means less feed, and the herd has to move or shrink.

Water points control where animals go. They gather near water and the ground there wears out first, however much grazing is left further out.

Recovery is slow. Once native cover is lost in an arid climate it does not come back in a season.
Environmental impact to watch
OvergrazingMore animals than the land can feed strips the cover and the soil goes with it.
Damage around waterThe ground near every water point is the first to be worn bare.
Loss of good speciesAnimals eat the palatable plants first, leaving the ones nothing wants.
Wind erosionOnce the cover is gone the surface starts to move.
How it works
Feed crops such as alfalfa and Rhodes grass are grown under irrigation and cut for the animals. This is crop farming. The animals are fed the cut plants, and may be kept far from the field where it grew.
Scale and inputs
What it really isIt is an irrigated crop, so it is assessed using the crop thresholds
SpeciesAlfalfa and Rhodes grass are the main ones
Water useHigh. Alfalfa is among the thirstiest crops grown in the Kingdom
Where it fitsIt is assessed in the crop section, as irrigated open-field cropping
YieldThe plants are cut and carried to the animals several times a year
What limits it
Water is the whole constraint. Fodder is grown to feed animals, but it competes directly with food crops for the same water.

It belongs with the crops. Rhodes grass already sits in the 63-crop library, so this is assessed as a crop and routed there.
Environmental impact to watch
Water useThe main concern. Fodder can use more water per hectare than the food crops beside it.
Aquifer drawWhere it runs on groundwater it draws on the same source as everything else.
Salt build-upHeavy irrigation without proper leaching concentrates salt in the soil.
How it works
Animals are kept in pens or sheds and fed on brought-in feed. The land underneath does almost nothing except hold the buildings.
Scale and inputs
What the land givesFirm level ground, and somewhere for waste water to drain
FeedAll feed is bought in, and much of it is imported
WaterWater is needed for the animals to drink and for washing the pens
AreaA small area compared with any grazing system
Where it sitsThe site is chosen for its road access and closeness to market
What limits it
Soil quality barely matters. What decides the site is water supply, road access and somewhere to put the waste.

It is a siting question. The land assessment can say the ground is firm and level. Everything else that matters sits outside this study.
Environmental impact to watch
ManureConcentrated in one place. Where it goes is the main environmental question.
Water pollutionRunoff from pens carries nutrients and bacteria into the ground and any watercourse.
Smell and fliesReal constraints on how close such a site can be to housing.
Imported feedThe environmental effect of growing the feed happens wherever it was grown. It does not show up at this site.
Agro-industry & Facilities
Processing plants, packhouses, cold stores and logistics.
Factor routing4 govern · 14 N/A · 8 conditional
What is being evaluated
Not a biological subject at all. What is assessed is the land’s ability to carry a structure and the site’s access to production and market.
Factors that apply to every kind of facility4
SQ-B-06Gypsum ContentGypsum dissolves under a building and the ground settles unevenly. Foundations crack.
SQ-C-02Flood HazardA flood ruins stock, equipment and cold rooms. The one hazard that can destroy the whole asset at once.
SQ-D-01Terrain WorkabilityBuildings and yards need flat ground. A slope means cut and fill before anything is built.
SQ-D-04Sand Encroachment HazardDrifting sand blocks yards, doors and air intakes, and never stops arriving.
Factors that apply to some kinds only8
SQ-A-05Soil TextureDecides how much the ground will carry and whether it needs improving before building.
SQ-A-06Coarse FragmentsStone makes digging harder, but it also gives a firmer base. Which matters more depends on what is being built.
SQ-B-02Sodicity (ESP / SAR)Sodic soil swells and shrinks with moisture, which moves whatever sits on it.
SQ-B-05Calcium CarbonateHard carbonate layers are difficult to dig through. Below them the ground is firm.
SQ-C-01Drainage ConditionGround that does not drain leaves standing water in yards and around foundations.
SQ-C-03Waterlogging RiskSaturated ground under a slab loses bearing strength.
SQ-D-02Water Erosion HazardRunoff can undercut access roads and hard standing.
SQ-D-03Wind Erosion HazardThis matters for open yards and anything stored outside. It does not affect enclosed buildings.
These depend on what is being built. A heavy cold store on a slab asks more of the ground than an open yard or a light shed.
+Elements to add for agro-industry4
SQ-H-01Distance to productionHow far to the farms the plant serves. The single biggest factor for a packhouse or processing plant, and nothing in the framework measures it. A perfect site far from the crop is the wrong site.
SQ-H-02Road accessConnection to a road that can take heavy vehicles. Every load in and out moves by truck. Without the road the site does not work, whatever the ground is like.
SQ-H-03Power availabilityGrid connection and reliability. Cold stores fail without continuous power. This decides the site more often than the soil does.
SQ-H-04Ground bearing capacityWhat weight the ground will carry. A geotechnical measure. The soil factors in this study describe how well the ground grows plants. None of them measures how much weight it can carry.
The land evaluation routes this activity but does not decide it. Fourteen of the twenty-six factors do not apply, because nothing is grown. What settles the site is where the crop is, where the road goes and whether the power holds.
The three kinds of facility
How it works
Fresh produce arrives from surrounding farms, is graded, washed, packed and sent out. Everything moves through quickly — the building is a building things pass through quickly, rather than somewhere they are stored.
Scale and needs
Site sizeA few hectares, including the yard and space for trucks to turn
What the ground givesFirm level ground, and drainage for the yard
TrafficBusy with trucks during harvest, and quiet the rest of the year
WaterFor washing produce and cleaning down
PositionClose to the fields, because fresh produce loses quality the further it travels
What limits it
It has to be near the crop. Fresh produce cannot travel far before grading without losing value. This decides the site more than the ground does.

The road matters more than the soil. Trucks come and go all day through harvest.

It is seasonal. The building may stand idle for months, which shapes how much is worth building.
Environmental impact to watch
Wash waterWater used on produce carries soil, and sometimes residues, and needs somewhere to go.
Waste produceRejected and trimmed material accumulates fast and rots quickly in heat.
TrafficConcentrated truck movement on rural roads during the harvest weeks.
How it works
An insulated building kept refrigerated so produce can be held rather than sold immediately. It runs continuously, whether full or not.
Scale and needs
What the ground givesGround firm enough to carry a heavy insulated building
PowerThe power must run without interruption
PositionIt can be built anywhere between the farm and the market
Running patternIt runs all year round
FailureIf the power fails for a few hours, everything stored inside can spoil
What limits it
Power decides it. An unreliable supply makes the site unusable however good the ground is.

The ground has to carry weight. A loaded cold store is heavy, and uneven settlement cracks insulated panels and lets the cold out.

Gypsum in the ground is the specific risk. It dissolves and the building settles unevenly.
Environmental impact to watch
EnergyRefrigeration runs continuously. On a fossil-fuel grid this is the main environmental burden.
RefrigerantLeaks matter far more than the volume suggests.
Heat rejectedEvery cold store pushes heat out into the air around it.
How it works
Raw product is turned into something else — dates into paste, milk into cheese, grain into flour. More machinery, more water and more waste than a packhouse.
Scale and needs
Site sizeLarger, with space for storage, waste water treatment and future expansion
WaterA lot of water is used, both for processing and for cleaning
PowerPower runs continuously, and the demand is often high
PositionIt can be built further from the fields, because processed input keeps longer than fresh produce
Running patternOften runs all year, using stored or imported input
What limits it
Water supply and effluent both have to work. A plant needs clean water in and somewhere for dirty water to go. Either one missing stops the site.

Distance to the crop matters less. Processed input travels better than fresh, so these plants have more freedom in where they sit.
Environmental impact to watch
EffluentThe main issue. Processing water carries organic load and needs treating before discharge.
Solid wastePeel, pulp, husk and rejected material, in volume, all year.
Water useCompetes with agriculture for the same supply.
OdourOrganic processing and its waste streams can carry a long way in still air.
Land Management
Restoration, dune fixation and rangeland rehabilitation.
Factor routing13 govern · 3 qualify · 10 conditional
What is being evaluated
The degraded condition itself. The worse the land, the stronger the case for intervention — the assessment selects rather than excludes.
Factors that choose the site instead of rejecting it3
SQ-D-02Water Erosion HazardreversedReversed. Water erosion is why the land needs treating. Severe erosion selects the site rather than rejecting it.
SQ-D-03Wind Erosion HazardreversedReversed. Wind erosion is the reason to plant a shelterbelt. No wind erosion, no need for one.
SQ-D-04Sand Encroachment HazardreversedReversed. Moving sand is what dune fixation exists to stop. The worse it is, the higher the priority.
For every other activity these three are damage. Here they are the reason to act. A hectare with no erosion and no moving sand is not a candidate for restoration — there is nothing to restore.
Factors that decide whether a planting will survive13
SQ-A-01Available Water CapacityWhether the soil holds enough water for a planting to survive without irrigation after the first years.
SQ-A-03Rooting ConditionsHow deep roots can go. Decides whether trees or only shallow-rooted cover will establish.
SQ-A-04Surface Sealing & CrustingA hard crust stops seed germinating. Direct seeding fails on sealed ground.
SQ-A-05Soil TextureDecides what will grow and how the surface behaves when it is disturbed.
SQ-B-01Salinity (ECe)Salt limits which species survive. Some native plants tolerate a great deal.
SQ-B-02Sodicity (ESP / SAR)Sodic soil sets hard and sheds water instead of absorbing it.
SQ-B-05Calcium CarbonateHard carbonate layers block roots and stop water moving down.
SQ-B-06Gypsum ContentGypsum layers are unstable and collapse when wetted.
SQ-B-07Soil pHDecides which species will establish and survive.
SQ-C-01Drainage ConditionWhether water sits or moves through. Both extremes limit what can be planted.
SQ-C-03Waterlogging RiskWaterlogged ground kills most dryland species.
SQ-D-01Terrain WorkabilitySteep ground is where erosion is worst, and also where planting is hardest.
SQ-E-01Moisture Deficit (Aridity)How dry it is. The main control on whether a planting survives once watering stops.
Factors that apply to some kinds only10
SQ-A-02Soil WorkabilityMatters where ground is prepared mechanically before planting.
SQ-A-06Coarse FragmentsStone makes planting slower. It also helps hold the surface in place.
SQ-B-04Toxicity Risk (Boron)Boron limits some plants. Many native species tolerate it.
SQ-C-02Flood HazardFlooding can wash away a new planting. On some sites it waters it instead.
SQ-E-02Thermal SuitabilityHeat makes it harder for a young plant to establish. Once established, it copes better.
SQ-E-03Radiation & Solar EnergySunlight is rarely a limitation anywhere in the Kingdom.
SQ-E-04Length of Growing Period (LGP)Sets the window for planting and establishment.
SQ-E-05Frost RiskFrost is a real risk in the highlands. On the plains it rarely occurs.
SQ-F-01Irrigation Demand (ETc)Only for the first years. Most plantings are watered to establish, then left.
SQ-F-02Crop Nutrient RequirementNative species are adapted to poor ground and rarely need feeding.
These depend on what is being planted and how. Direct seeding, planting nursery seedlings and simply fencing off an area to recover each ask different things of the ground.
+Elements to add for land management3
SQ-I-01Degradation severityHow far the land has already gone. The selection measure for this activity. Everywhere else a degraded reading rejects a site; here it is the reason to choose it.
SQ-I-02Natural recovery potentialWhether the land would come back on its own if left alone. Decides whether to plant, or simply to fence and wait. Cheaper and often better where seed and roots survive in the ground.
SQ-I-03Species survival without irrigationWhether a planting lives once watering stops. The crop library measures yield. Restoration only needs the plant to live, which is a different question entirely.
Here a planting counts as a success if it stays alive and covers the ground. The S1 to N2 classes were built to say how much a crop would produce. That is a different question from whether a plant survives.
Four kinds of land, four different jobs
What this land looks like
The condition being treated
Bare, loose sand that is physically travelling. Dunes and sand sheets advancing across roads, fields, canals and villages. Nothing holds the surface, so wind moves it.
Where it is found — Sand seas and their margins, and downwind of any large bare area.
How it is treated
Sand is stopped before anything is planted. Fences and mulch hold the surface still, then deep-rooted shrubs and trees are planted to keep it that way.
The work in order
The problemSand is blowing onto the land from somewhere else and burying it
First stepPut up fences and palm frond screens, and spread mulch, to stop the sand moving
ThenPlant into the surface once it has stopped moving
SpeciesPlants with deep roots that survive drought and salty ground
WateringWatered for the first few years only, then left to survive on its own
What goes wrong — Planting before the surface is held. Seedlings are buried or their roots exposed within a season.
What this land looks like
The condition being treated
Rangeland that has been grazed past recovery. The palatable plants are gone, bare ground shows between what is left, and the surface has started to seal or blow.
Where it is found — Around water points, near settlements, and anywhere stocking has stayed high through dry years.
How it is treated
Grazing is reduced or stopped so the land can recover, and native species are reseeded or planted where the seed in the soil is exhausted.
The work in order
The problemAnimals eat the plants faster than the plants can grow back
First stepReduce or stop the grazing. Nothing else works until this is done
ThenSow seed or plant seedlings where the land will not recover by itself
SpeciesNative grasses, and shrubs the animals can eat the leaves of
TimeRecovery takes several years, not one growing season
What goes wrong — Reseeding without controlling grazing. The new growth is eaten before it can set seed.
What this land looks like
The condition being treated
Ground where water is cutting the soil away. Gullies, rilled slopes and collapsing wadi banks. Every rain event takes more.
Where it is found — Sloping ground in the southwest highlands, and along wadi channels after they are cleared.
How it is treated
Water is slowed before the soil is treated. Contour banks, check dams and terracing reduce the flow, then planting holds what is left.
The work in order
The problemRain washes the soil off the land and carries it away
First stepSlow the water down using terraces, banks across the slope, and small dams
ThenPlant so the roots hold the soil in place
SpeciesPlants with deep roots and thick growth close to the ground
NoteBanks and dams fail if they are built before anyone measures how much water comes down
What goes wrong — Building structures without reducing the flow reaching them. They fill, overtop and breach.
What this land looks like
The condition being treated
Open ground that is not degrading but carries little or no vegetation. Treated to add cover, shelter and shade rather than to repair damage.
Where it is found — Around towns, along roads, beside farmland as windbreaks, and on suitable open ground.
How it is treated
Nursery seedlings are planted out and watered until their roots reach whatever moisture the site holds. After that they survive on their own or they do not.
The work in order
The problemThe land is not damaged. It simply has very few plants on it
First stepChoose plants that can live here without being watered
WateringWatered for two to three years, then left to survive on its own
SpeciesPlants native to the area, which already survive its dry climate
Test of successThe planting counts as successful if it stays alive once watering ends
What goes wrong — Choosing species that need permanent watering. They survive while irrigated and die when it ends.