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Natural resources and energy

Special

Celebrating the International

Year of Soils:

Exploring some soil biological indicators

S

oils are of central importance for delivering ecosystem

services, such as food production and climate mitigation.

These services depend heavily on carbon (C) sequestration

and nutrient cycling, processes that are governed by soil

biota or biology. Soil biology is the study of microbial and faunal

activity and ecology in soil. However, soil biology is one of the most

unexplored frontiers associated with understanding the dynamics of

soil resources and their subsequent health or quality. There is grow-

ing recognition for the need to develop sensitive indicators of soil

health and biology that reflect the effects of land management on

soil and assist land managers in promoting regenerative conserva-

tion agriculture (CA).

Producers intuitively recognised the importance of healthy soils and

have used qualitative terms (i.e. colour, taste, touch and smell) to

describe soil condition and performance for crop production since

the dawn of agriculture about 10 000 years ago. At the beginning

of the 20th century, qualitative “life measuring” descriptions, how-

ever primitive they were, gradually became replaced by analytical

procedures to assess and evaluate soil almost exclusively from the

perspective of inorganic nutrients (chemistry) and crop yield.

In this article, a few soil biological indicators are discussed, which

are part of a growing pool of analytical options gaining ground in

measuring short term changes in soil biology or health inflicted by

changes in land management. They are discussed in relation to ac-

tual field measurements done for different cropping practices evalu-

ated in the Ottosdal CA project, which is funded by the Maize Trust

(MT), implemented by the Ottosdal No-till Club and co-ordinated by

Grain SA’s CA Programme. These cropping treatments (bare soil,

monocrop, rotations, mixtures and natural grassland or veld) include

cash crops (maize, soybean and sunflower), as well as cover crops

(e.g. Dolichos lablab, grain sorghum, babala, black oats and mixtures).

Soil microbial functional diversity

Functional diversity (the diversity of species behaviours) is an indica-

tion of the biological status of soil microbial populations in soil, since

it relates to the activities of soil micro-organisms contributing to soil

biological processes. Various soil microbial activities fulfil critical

functions in the decomposition of organic matter and biogeochemi-

cal cycling of nutrients such as carbon, nitrogen and phosphorus.

The Biolog

®

system is used to determine functional diversity of mi-

crobial communities. From these results, carbon source utilisation

profiles (CSUP), i.e. the functional

diversity

of soil microbial popula-

tions, were determined by using the amount and equitability of car-

bon substrates utilised as indicators of

richness

(Shannon-Weaver

index or the number of active microbial species present) and

even-

ness

(Evenness index or microbial abun-

dance), respectively.

Figure 1

indicates differences in microbial

populations’ functional diversity between

the different crop practices or treatments

at Ottosdal. Three main groups are distin-

guished by the results: Blue circle enclosing

bare soil and veld treatments; green circle

enclosing treatments with maize; and red

circle enclosing treatments with lablab.

Significant differences exist between the

amount and types of carbon sources uti-

lised by soil microbial populations present

in bare soil and veld (natural grassland),

lablab, grain sorghum on babala and babala

on maize treatments. The number of active

microbial species present in veld and bare

soil, maize monoculture and maize-soybean

crop treatments were low compared to the

rest (

Graph 1

). Microbial abundance was

significantly higher in lablab on sunhennop

than in the bare soil and veld treatments

(

Graph 2

). Microbial communities present

in the latter treatments are thus less diverse

and dominated by specific microbial spe-

cies, implying a state of imbalance.

HENDRIK SMITH,

CA facilitator: Grain SA,

WILLIE PRETORIUS,

Crop Systems and Radicle Soil Health Laboratory,

JOHAN HABIG,

researcher: ARC-Plant Protection Research Institute,

GERRIE TRYTSMAN,

researcher: ARC-Animal Production Institute and

LIESL WIESE,

researcher: ARC-Institute for Soil, Climate and Water

54

November 2015

Figure 1: Ordination plot illustrating the differences in average CSUP between crop treatments.