Contents

  • Cover
  • Front matter
  • Preface
  • Scope, purpose and use
  • 1. Terminology, economic analysis, risk management
    • 1.1 Terminology
    • 1.2 Economic analysis
    • 1.3 Understanding risk
  • 2. Regulations, consents and approvals
    • 2.1 National Environmental Standards for Plantation Forestry (NES-PF)
    • 2.2 Heritage New Zealand Pouhere Taonga
    • 2.3 The Health and Safety at Work Act
    • 2.4 NZ Transport Agency approval for access onto state highways
    • 2.5 District council approval for access onto council roads
  • 3. Planning for roads
    • 3.1 Road classes
    • 3.2 Arterial roads
    • 3.3 Secondary roads
    • 3.4 Spur roads
    • 3.5 Establishment tracks
    • 3.6 Spatial information
    • 3.7 Initial field work
    • 3.8 Manual design method: Stepping out a roadline on a topo
    • 3.9 Running a grade line in the field
    • 3.10 Full road design
    • 3.11 Working with road survey data
    • 3.12 Geometric road design
    • 3.13 Curve widening
    • 3.14 Horizontal alignment
    • 3.15 Vertical alignment
    • 3.16 Calculating the safe stopping distance
    • 3.17 Setting out the roadline
  • 4. Planning for landings
    • 4.1 Common landing layouts
    • 4.2 Landing planning considerations
  • 5. Road and landing construction
    • 5.1 Soil and rock properties
    • 5.2 Managing adverse environmental effects
    • 5.3 Marking clearing widths
    • 5.4 Roadline salvage
    • 5.5 Daylighting
    • 5.6 Road formation
    • 5.7 Drainage control during earthwork construction
    • 5.8 Earthwork machinery
    • 5.9 Estimating machinery production
    • 5.10 Stabilising cut and fill slopes during construction
  • 6. Pavement design, subgrade preparation, pavement construction
    • 6.1 Traffic loading
    • 6.2 Evaluating subgrade properties
    • 6.3 Determining pavement depth
    • 6.4 Pavement material properties
    • 6.5 Compaction of subgrade and pavement
    • 6.6 Compaction equipment
    • 6.7 Pavement construction
    • 6.8 Weak subgrades
    • 6.9 Chemical stabilisation of pavement or subgrade
  • 7. Erosion, sediment and slash control structures
    • 7.1 Ditches
    • 7.2 Cut-outs
    • 7.3 Berms
    • 7.4 Drainage culverts
    • 7.5 Flumes
    • 7.6 Sediment traps and soak holes
    • 7.7 Silt fences
    • 7.8 Sediment retention ponds
    • 7.9 Debris traps
  • 8. River crossings
    • 8.1 Fish passage
    • 8.2 Selecting the location and crossing type
    • 8.3 Fords
    • 8.4 Temporary river crossings
    • 8.5 Single culvert river crossings
    • 8.6 Battery culvert river crossings
    • 8.7 Drift deck river crossings
    • 8.8 Single span bridge river crossings
    • 8.9 Prediction of flood flows, and sizing culverts
  • 9. Road maintenance, repairs and upgrades
    • 9.1 Maintenance programme
    • 9.2 Economic evaluation of road maintenance projects
    • 9.3 Managing maintenance requirements
    • 9.4 Commonly used maintenance machinery
    • 9.5 Road surface maintenance
    • 9.6 Road foundation maintenance
    • 9.7 Landing rehabilitation and decommissioning
    • 9.8 Roadside vegetation maintenance
    • 9.9 Erosion and sediment control structure maintenance
    • 9.10 River crossing maintenance
  • Forest road engineering terminology
  • References
  • Websites, resources, databases
  • Appendix: Forest Roads For High Productivity Motor Vehicles (HPMV) with Two Drive Axles Log Trucks

NZ Forest Road Engineering Manual

  1.  ›
  2. 9. Road maintenance, repairs and upgrades ›
  3. 9.7 Landing rehabilitation and decommissioning
 

9.7 Landing rehabilitation and decommissioning

This section will only discuss the engineering related rehabilitation and repairs and maintenance. For example, burning of slash will not be discussed. Refer to the Forest Practice Guide, Managing slash on landings for additional information.

Check new landings and pads after construction as part of a regular inspection programme. Landings are often built up to 8-12 months prior to harvesting, and post-construction repairs and maintenance may be required in more erosion prone areas especially after heavy rainfall. Most landings need post-harvest rehabilitation and decommissioning. The two critical components to manage are water control and slash. Poorly directed water can pond or undermine earthworks. The volume and weight of slash, including bark and the water it can contain, will also load the landing with additional weight and reduce the shear strength of the structure.

Unstable slash should be pulled back from the landing edge with an excavator. Also remove to solid ground harvesting processor generated deposits of bark where it has formed deep, wet, heavy layers where it could increase the risk of landing failure. On steep erodible slopes, if processing slash is not contained on purpose-built slash benches, it should be reduced to a level where the ground is visible through the remaining material. Install drainage and sediment control structures to improve water control and fill stability. For example, minimise the entry of stormwater into birds’ nests. Removing slash from risk prone locations can be extremely challenging to do, and in some cases is not possible. Placing the slash in the right place during harvesting not only saves costs but also eliminates or reduces a problem.

The details behind maintenance of erosion and sediment control structures are described in section 9.9.

A landing failure reduces site productivity, and can trigger environmental effects like highly erosive debris flows
Large boom excavators increase the reach and slash that can be removed
The landing has had a normal excavator complete the rehab but significant slash remains
Good example of a decommissioned landing
Good example of a decommissioned landing
Prev page Next page
Forest Owners Association

© 2025 New Zealand Forest Owners Association

Website by RS