7 Biota
Soil biota both affects and is affected by soil type. For example, Kauri trees create acidic conditions around their root zone, leading to the development of podzolic features.
7.1 Vegetation
Recording vegetation during soil survey can reveal relationships between soil and vegetation community composition and structure.
Two main options are available in New Zealand for recording vegetation data in a soils context.
- A detailed assessment of vegetation at a soil site can be made using the RECCE standard (Hurst et al. 2022). This is the method used by the NZ National Vegetation Survey, and it allows creation of a complete record of vegetation structure and species assemblage. Some elements of the RECCE standard have been adopted elsewhere in this manual, where relevant to describing the landscape and land surface (Section 4.4, Section 11.3). Note that considerable botanical experience is needed to apply the full RECCE standard correctly.
- If the soil description is being completed in the context of an LUC assessment, use the NZLRI Vegetation Descriptions available in Appendix 3 of the LUC Survey Handbook (Lynn et al. 2009). This system describes a set of 49 vegetation communities commonly found in New Zealand, grouped into five broad structural categories (grasses, crops, scrub, forest, and herbaceous). Ability to identify key local species will be required to apply the system correctly. The system can also be used for rapid vegetation assessment during other soil mapping activities.
- For rapid assessment, use the LCDB land cover codes (Section 8.1) that relate to vegetation.
Simpler systems that attempt to break vegetation communities into key structural classes are available, including the ‘Atkinson system’ recommended in the previous version of this manual. These are easy to apply but may not adequately discriminate between vegetation communities in a way that is soils-relevant.
7.2 Soil Fauna
7.2.1 Megafauna
Soil megafauna are large species that may not be directly dependant on the soil for any part of their life cycle, but still significantly and directly affect the soil, usually by mechanical disturbance or organic material addition. In New Zealand this role was largely filled by birds and reptiles before the arrival of humans. Since then, the niche has been dominated by domesticated sheep, goats and cows, as well as feral goats, pigs and rabbits. Significant increases in the volume of animal wastes added to many soils have also occurred, most intensely on land converted to pastoral agriculture.
The influence of these animals is generally captured elsewhere in a soil description (e.g. Section 10.3) and so no further morphology recording requirements are defined here.
Direct assessment of earthworm presence in the topsoil is sometimes desired (Shepherd 2000; Shepherd and Janssen 2000). Optionally, record the number of earthworms observed in a 20 x 20 cm block of A horizon. Calculate the volume of the sample examined and convert the count to a rate per cubic metre.
7.2.2 Macrofauna
Macrofauna are those soil-dwelling animals with a body width of ~2 - 20 mm. This includes some critical ‘ecosystem engineers’ such as earthworms, ants, and termites. These species are capable of moving huge volumes of soil around over time, and often alter the soil structure, particle size distribution and chemical status as they do. The influence of these animals is generally captured in a soil description as ‘secondary biological features’ (Section 17.5).
7.2.3 Meso- and Microfauna
The soil Meso- and Microfauna are much smaller, with body widths of 0.1 - 2.0 mm and < 0.1 mm respectively. They live mostly within soil pores and have little direct impact on structure. Their presence, however, is a sign that soil porosity is well enough developed to provide them with a habitat. No observational requirements are defined for Meso- or Microfauna at this time.