Grevillea robusta is widely interplanted with crops in Maragua subcounty, a practice that enhances biomass quantities in farmlands. However, quick tools for estimating biomass of such trees are lacking resulting in undervaluation of the farm product. This study sought to develop allometric equations for estimating tree biomass using diameter at breast height (DBH) and tree height as predictor variables. Tree biomass was computed using thirty-three (33) trees randomly selected from 12 one hectare plots established in each of the four agroecological zones (AEZs). DBH of all Grevillea robusta trees per plot was measured and three trees were selected for destructive sampling to cover the variety of tree sizes. Regression analysis was used to develop equations relating DBH/tree height to biomass based on linear, exponential, power, and polynomial functions. The polynomial and the power equations had the highest R2, lowest SEE, and MRE values, while DBH was the most suitable parameter for estimating tree biomass. The tree stem, branches, foliage, and roots biomass comprised 56.89%, 14.11%, 6.67%, and 22.32% of the total tree biomass, respectively. The mean tree biomass density (12.430±1.84 ton ha−1) showed no significant difference (p=0.09) across AEZs implying no difference in G. robusta agroforestry stocks across the AEZ. The allometric equations will support marketing of tree products by farmers and therefore better conservation and management of the tree resource.

1. Introduction

Trees in agricultural ecosystems offset pressure on forest resources in conventional forests and therefore play a major role in sustaining the productivity of agricultural and forested landscapes. They are a source of livelihood for the rural communities providing wood and nonwood products like resin, honey, medicine, vegetables, among others and are also important in conservation of biological diversity, water, and soil conservation [1]. They represent a vital source of food for many of the world’s poorest people, providing both stable and supplemental foods, fodder and fuel for lighting, and cooking and food processing. Besides, they are also important in biological diversity conservation and mitigating climate change through carbon sequestration [2].

Quantification of the amount of biomass and/or carbon stored in trees presently is an important component in the implementation of the emerging carbon credit such as Reducing Emissions from Deforestation and Degradation (REDD+) [3]. Developing countries including Kenya can benefit from REDD+ related mechanisms by providing accurate information about their forest and tree resources. REDD+ requires countries to establish measurement, reporting, and verification (MRV) methods [4]. This may consists of inventory of forests/trees in sampled plots and application of appropriate allometric equations to estimate biomass [2]. Biomass estimates eventually are converted into carbon and carbon dioxide (CO2) equivalents.

Most of the small scale farmers in Maragua integrate trees (mainly Grevillea robusta) with crops in their farms. The specific economic values of the trees planted in agricultural landscapes have not been fully explored. Since no marketing guidelines have been developed for the different tree products, prices of the products are normally determined by agreements between the seller and the buyer, and this varies from area to another, size of tree or product, and the targeted use of the product. In many cases, such negotiations do not favor the farmer and lowers the value of the tree, thus demotivating farmers from planting trees. A method that helps establish biomass stocks and provides accurate information about the available wood resources from this species would help in its management and conservation and would enhance the livelihoods of the farmers.

Some allometric equations have been developed to estimate tree biomass quantities using easily measurable parameters such as DBH and height [13]. Henry et al. [1] and Kuya et al. [5] constructed equations for estimating tree biomass in agricultural landscapes of western Kenya while Kinyanjui et al. [6] constructed an equation for inventory of the above ground biomass in the Mau Forest Ecosystem of Kenya. Mugo et al. [7] predicted stem diameter of open grown trees in western Kenya. Since tree allometry varies from site to site [8], such equations may not be appropriate for the conditions of Maragua subcounty in terms of agro ecological zonation and the purpose for which the trees are grown. Here, a variety of wood products are marketed for various uses including timber, firewood, pole wood, and fencing and some leaves have been used as livestock fodder. Hence, to meet the study area specific needs for tree products and tree components, it was necessary that equations for estimating G. robusta biomass quantities in the farming landscapes of Maragua subcounty are developed.

The purpose of this study was to develop equations relating tree biomass with easily measurable parameters of diameter at breast height (DBH) and height as a quick tool for valuation of tree products. The study also sought to assess variations of G. robusta biomass among agroecological zones of the study area as a basis for developing tree resource management plans.

2. Materials and Methods

2.1. Study Area

The study was done in Maragua subcounty of Murang’a county in central Kenya (Figure 1). The area covers 839 Km2 [9], between longitude 36° 30′E and 37°30′E and latitude 00°30′S and 1°S. The study area consists of four upper midland agroecological zones (AEZ) as illustrated in Table 1. Such variations of altitude and climate are expected to influence allometry and also biomass productivity of G. robusta trees.

2.2. Physical and Topographic Features

The study area is a major source of numerous springs and rivers that drain into River Tana through rivers Maragua, Irati, Sabasaba, Kabuku, Makindi, Thuki, Thamuru, and Thika [9]. The geology of the subcounty consists of volcanic rocks of the Pleistocene age and basement system rock of Achaean type. Volcanic rocks occupy the western part of the county bordering the Aberdare ranges while rocks of the basement system are in the eastern part. Porous beds and disconformities within the volcanic rock system form important aquifers, collecting, and moving ground water, thus regulating water supply from wells and boreholes. In the study area Jaetzold et al. [10] classified and described soils in AEZ as shown in Table 2.

2.3. Land Use Activities

Farmers in the study area have actively adopted agroforestry [11]. Land use systems range from subsistence small holder farms to more cash crop oriented farms which relatively range from 1.5 to 2 acres. Woody vegetation forms part of the agricultural landscape which varies from single tree to small stands that consists of mainly exotic trees and isolated indigenous trees managed in different ways [11]. Trees are grown around the homesteads, in woodlots and croplands, and along farm boundaries. Githiomi et al. [11] further stated that trees and shrubs are grown around the homestead, in woodlots and cropland, and along farm boundaries and that woodlots are in small mono specific clusters of trees mainly in lower areas of the study area. According to Kuya et al. [5], such land use activities influence the biomass of agricultural landscapes in different ways depending on management activities.

2.4. Sampling Design

Stratified systematic sampling was used on a Geographical Information System (GIS) platform to select sampling sites in each of the AEZs. Each AEZ was divided into three equal polygons and the centre of each polygon was used as the reference data collection point (Figure 2). The position of the data collection point identified on the GIS map was recorded (Table 3), transferred into a GPS, and traced to the ground. The GPS readings were based on the UTM/UPS format in UTM zone 37S. A one hectare (100 x 100 m) plot was established at the reference point aligned to the North-South and East-West grids. All the G. robusta trees in the plot were recorded for diameter at 1.3 from the ground (DBH) and total height. Three G. robusta trees in each plot were selected for destructive sampling based on a proportional allocation among size classes identified in the plot.

2.5. Processing of Destructively Sampled Trees
2.5.1. Destructive Sampling

All the G. robusta trees selected for destructive sampling were categorized into DBH classes. The selected trees were uprooted onto tarpaulin sheets spread on felling direction (to avoid loss of foliage), leaves stripped off and debranched, and total tree length/height (HT) measured using a linear tape. Each of the trees was then divided into components (trunk, branches, foliage, and roots) and the trunk was cross cut to manageable sizes. The tree components were weighed in the field and their fresh weight was recorded. Samples were taken from the different components of the tree and their fresh weight was taken. The samples were subsequently oven-dried in the laboratory at 105°C as guided by [12].

Similarly the branches were trimmed, cross cut, and classified into four diameter classes as 0 < D < 2 cm (Class 1), 2 ≤ D < 5 cm (Class 11), 5 ≤ D < 10 cm (Class 111), and D≥ 10 cm (Class IV) for easy of weighing. Their weights were taken for green weight to the nearest 0.1 kg. The heavier ones were measured as individual billets while the lighter ones were bundled together and weighed for their green weight. Aliquots were taken and labeled and their green weight was recorded to the nearest 0.01gm kept in bags and taken to the laboratory for oven-dry (105°C) weight measurement. The foliage was collected on to the tarpaulin sheet, bundled into gunny bags whose weights were known, and weighed to the nearest 0.1kg. Their green weights were calculated as the difference between the gross weight and the weight of the empty gunny bags and recorded. A sample of the foliage was taken from the combined mass of the foliage, weighed, recorded to the nearest 0.01gm, and oven-dried (70°C).

Excavation of the tree was done manually until all the roots were removed. The taproot was followed to its endpoint and root length recorded. Soil embedded in the stump joints and on root surface was removed by use of a brush and water. The roots were classified into size classes as (Class 1) 0 < D < 2 cm, (Class 11) 2 ≤ D < 10 cm, and (Class 111) D ≥10 cm for ease of weighing. Roots were weighed by size classes for green weight and recorded. An aliquot of each root size class was extracted and weighed for green weight, recorded, tagged, packaged, and taken to the laboratory to oven-dry at 105°C. In all the cases, the aliquots were left in the oven to dry and changes in dry weight were monitored on a daily basis until they reached a constant weight.

2.5.2. Biomass Measurement

The aliquot’s green and oven-dry weights were used to get the dry-green weight ratios. These were subsequently used to convert the green weight of the tree component (trunks, branches, foliage, or roots) to dry weight, which is the component’s biomass. The total aboveground (AGB) biomass was obtained by getting the sum of the biomass of the trunk, branches, and foliage. Similarly the total belowground (BGB) biomass was obtained by summing up all the dry weights of all the root sections of that given tree. Finally the total tree biomass (TTB) was obtained by adding up aboveground and belowground biomass. Scatter plots and function graphs were used in assessing the relationships between easily measurable variables of DBH and HT together with a combination of DBH and HT against total tree biomass and tree component biomass

2.5.3. Development of Biomass Equations

Thirty-three destructively sampled trees were used to develop the biomass estimation allometric equations. The measured predictor variables DBH, height (Ht), and product of DBH and HT (DBHHt) for each of the destructively sampled trees were regressed to the dry weight (biomass) of the total tree biomass (TTB) or component biomass [(AGB), (BGB) branches biomass (BR), and foliage biomass (F)].

Scatter plots were used in illustrating the relationships between total tree and tree component biomass with the easily measurable variables. To derive the equation for each of the dependent variable (TTB, AGB, BGB, BR, and F) the regression functions (exponential, linear, polynomial, and power) were superimposed on the scatter plot graphs. The selection of the best fit equation was based on the lowest standard error of the estimate (SEE) which is the standard deviation of the residuals: the lowest residual mean error (RME) and the highest coefficient of determination (R2).

2.5.4. Validation of Developed Allometric Equations

The mean differences between predicted and observed biomass were used to test the suitability of the equation. Simple linear regression analysis between observed and predicted values of the equations quantifies the tendency of residuals whereby R2 and mean standard error (MSE) indicate the precision of the estimates. Residual plots were also used to assist in the evaluation of the equations. Bias% was computed as ((predicted biomass-measured biomass)/measured biomass) 100 [13].

Finally the developed equation for total tree biomass was compared with several equations in similar management units but different geographical areas. The two sets of biomass values were subjected to a paired t test [14] to find if differences occur in each biomass estimate comparison.

3. Results

3.1. Preliminary Findings of the Dataset

A total of 1,090 trees were measured for DBH in the twelve (12) plots 222 in AEZ 1, 308 in AEZ2, 292 in AEZ 3, and 268 in AEZ 4. The values for DBH ranged from 1cm to 39.5cm with a mean of 11.08 cm in AEZ1, 11.51 cm in AEZ 2, 10.07 cm in AEZ 2, and 12.14 cm in AEZ 4. Height values ranged from 6.0m to 24.8m with a mean of 11.67m in AEZ 4, 13.32m in AEZ 3, 14.03m in AEZ 2, and 11.42m in AEZ 1. Out of the 1090 trees measured for DBH, 33 trees were destructively sampled for biomass measurements.

3.2. Percentage Contributions of Different Tree Components Biomass

The summary distribution of the total tree biomass and tree biomass components of the thirty-three destructively sampled trees of different sizes recorded in the study area are as shown in Tables 4 and 5. The total tree biomass (TTB) for the 33 trees was 6,335.89 kg distributed as follows: stem/trunk (56.89%), branches (14.11%), foliage (6.67%), and roots (22.33%). Thus aboveground biomass (AGB) comprised 77.74% while belowground biomass (BGB) was 22.33%. These are the proportions of biomass available for specific uses, e.g., timber (stem biomass), fuel wood (branches biomass), mulch/livestock feed/green manure (foliage biomass), and soil organic carbon services (roots).

The stem comprises the largest percentage of the total tree biomass (Table 5) while foliage has the least biomass contribution and this is in agreement with similar studies [1, 5, 15]. The 22.33% proportion of BGB is close to the IPCC default value for BGB which is taken as 24% [16]. The slight variations in allocation among AEZ could be a justification for development of very specific allometric equations for each of the AEZ. For example, the results indicated a slight increase in BGB/AGB ratio with altitude rise from UM1 (0.219) to UM4 (0.293). Such information on component ratios among G. robusta and which is based on tree allometry variations requires further research and supports its conservation and usage.

3.3. Illustrations of Biomass Estimation from Various Functions

Various functions were plotted and the biomass estimates done for each function. The goodness of fit in each regression was illustrated by the coefficient of determination (R2 value) which explains how close the measured data are to the fitted regression line [14]. These illustrations are shown in Figures 3, 4, and 5.

A comparison of functions for estimating TTB from DBH illustrates that the exponential function overestimates DBH for a tree of 35cm DBH. Though the other three functions have a near similar estimate, the R2 values favor the power function (R2 = 0.97) and the polynomial function (R2= 0.93). Though the linear function gives relatives good R2 value, foresters have disqualified linear relationships because they do not illustrate the ideal relationship between predictor variables and biomass or volume over a wide diameter size distribution [8, 16].

Estimation of total tree biomass from height varied greatly among functions making it difficult to select the ideal function. The R2 values were also lower compared to those of using DBH as a predictor variable. The same trend was noted in estimating ABG from tree height. Noting that height measurement in forests is difficult and the fact that farmers sell trees while standing, the use of tree height may increase tree biomass or volume estimation costs, while not increasing accuracy of estimates. As such trials of height as a biomass-predictor variable were discarded in favor of DBH which is easy to measure and can be measured with high levels of accuracy [6, 8].

DBH gives a good estimate of AGB based on R2 values with 0.98 for the power function and 0.94 for the polynomial function. Kuya [5] identified power functions as most ideal for estimating AGB in western Kenya while Henry et al. [1] preferred polynomial functions. It has been found that either of these functions is ideal based on the diameter size distribution [8]. Kuya [5] preferred power functions because of the large DBH size distribution which disqualifies polynomial functions which often have two turning points [14] and may not define the biomass-predictor relationship over a wide range of diameter sizes. In this case where G. robusta does not grow to large sizes in the study area, either a polynomial or a power function becomes ideal based on this criteria of choice.

3.4. Choice of Equation Based on Standard Error of Estimate and Mean Residual Error

Apart from the coefficient of determination, the standard error of estimate (SEE) and the mean residual error (MRE) have been used in choice of appropriate regression equations [14]. The SEE is a measure of the accuracy of predictions made with a regression line and the lower the value, the better the accuracy of an allometric equation [8]. Zar [14] also explains the mean residual error as another measure of the accuracy of a regression equation. Since residuals are differences between the data points and the regression line, the mean residual error refers to the error that is not explained by the regression line.

The choice of equation based on the three statistics is illustrated for the various biomass components in Table 6

Though linear functions had the least MRE for TTB and BGB, their previously described limitations [8, 14] disqualifies them. The polynomial functions have very small MRE values in all estimated biomass components of TTB (0.15kg), AGB (0.002Kg), and BGB (0.1Kg) illustrating their appropriateness based on this second selection criteria. Exponential functions have large mean bias in all functions and this further illustrates their inappropriateness in this selection. A bias of less than 5% of the total tree biomass is within acceptable range [16, 17] and would provide the farmers with the real value of the tree. In this case the polynomial function is very accurate with very minimal bias within the range of diameter sizes tested.

Based on the SEE, the polynomial function gave the lowest values at 1.33 for TTB, 0.99 for ABG, and 0.5 for BGB. This compared well with the power function which had 1.34 for TTB, 0.99 for AGB, and 0.51 for BGB. In this third selection criteria, the polynomial function again takes best preference.

Based on the statistics, Table 7 shows the list of preferred equations for estimating the different tree biomass components. Though all the preferred equations are polynomial functions, it should be noted that the power functions were the next best alternative and their application has already been illustrated for agroforestry species of western Kenya [5]. The limitation of two turning points observed in polynomial functions [14] may not apply in the study area where G robusta grows because the trees do not grow beyond the 40cm DBH size that was used in this study. It is however recommended that such equations should not be applied where trees of bigger sizes grow.

3.5. Validation of Developed Allometric Equations

Validation of the equations based on the bias of the equation in estimating specific diameter sizes is illustrated in residual plots used to assist in validation which are shown in Figure 6.

A second validation to compare biomass estimates from the preferred equation and that of similar studies shows that the developed equation compares well with other equations developed in agroforestry conditions of Kenya [1, 5] and Rwanda [18] but is not applicable in biomes far from the study area [19]. This finding illustrates that the process of destructive sampling to develop new allometric equations within a small geographical range may not enhance accuracy of estimates and an equation applicable in a similar land and tree management activity may as well be applicable in another one. The results are illustrated in Table 8.

3.6. Biomass Stocks among Agroecological Zones

Based on the allometric equations, the average TTB for G. robusta trees generated in each of the AEZ studied is as shown in Table 9. The TTB stock for each AEZ was 13. 926 tonha−1, 13.109 tonha−1, 10.869 tonha−1, and 11.827 tonha−1 in UM1, UM2, UM3, and UM4, respectively. Variability of tree biomass between the four agroecological zones showed no significant difference (p-value > 0.05) implying that though there could be a slight difference in the allometry of the tree species among AEZ, the total biomass does not vary. This also explains that the management of G robusta trees in the agricultural landscapes of the four AEZ does not differ and the farmers can form a marketing unit despite their different AEZ and their production quotas can be the same.

The average biomass stock of 12.43 ton/ha in the study compares well with the findings of Albrecht [20], 2-22 ton/ha, Henry [1], 9–11ton/ha, and Kuya [5], 16 ton/ha, all of which are for agricultural landscapes. This finding gives a better glimpse of the tree component in agricultural landscapes and is a good guide for the development of carbon stock factors in agricultural landscapes [21]. With this moderate stock, the farmers are able to practice agricultural activities while maintaining a tree cover in the farms which stabilizes the agricultural landscapes and reduces pressure for wood products from adjacent forests.

4. Conclusion and Recommendations

This study has developed a quick tool for estimating biomass from G. robusta trees in agricultural landscapes of Maragua county. The allometric equations allow better marketing of the trees and their components and will favor farmers who will get better value from their trees. The findings illustrate no much variations in stocking among the study strata and also comparing with studies in similar agricultural setups. Therefore the study illustrates the usability of general allometric equations which eliminate the expensive processes of destructive sampling. As such the developed equations are ideal for a wide range of application in areas of Kenya where G. robusta grows without any need to develop other equations.

The study identified only small sized G. robusta trees and the size limitation is influenced by their growth characteristics and the market conditions. The study proposes a validation of the allometric equations in cases where bigger sized trees exist. Similarly the small sample size used in this study may have not captured enough information on the allometry of the tree and a collation of this data and other existing datasets can help compare characteristics of allometry that may influence the equation used



See Table 10.


See Tables 11, 12, 13, 14, 15, 16, 17, and 18.


See Table 19.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.


The research was done as a part of a Master’s thesis and was financed by the first author.

Conflicts of Interest

The authors have no conflicts of interest in the manuscripts and therefore do declare that there are no conflicts of interest regarding the publication of this paper.


The authors wish to acknowledge the Department of Natural Resources in Karatina University where the student is registered for providing supervision and guidelines. The authors would also like to thank Kenya Forest Service (KFS) authorities for giving a permission to conduct the study using their staff members and the farmers who allowed uprooting of trees in their farms.