Hostname: page-component-745bb68f8f-kw2vx Total loading time: 0 Render date: 2025-02-11T06:29:25.894Z Has data issue: false hasContentIssue false

ACCOUNTING FOR SPATIAL VARIABILITY IN FIELD EXPERIMENTS ON TEA

Published online by Cambridge University Press:  01 October 2008

T. U. S. PEIRIS*
Affiliation:
Division of Biometry, Tea Research Institute of Sri Lanka, St Coombs Estate, Talawakelle, Sri Lanka
S. SAMITA
Affiliation:
Department of Crop Science, Faculty of Agriculture, University of Peradeniya, Peradeniya, Sri Lanka
W. H. D. VERONICA
Affiliation:
Division of Biometry, Tea Research Institute of Sri Lanka, St Coombs Estate, Talawakelle, Sri Lanka Department of Crop Science, Faculty of Agriculture, University of Peradeniya, Peradeniya, Sri Lanka
*
Corresponding author. usp71@yahoo.com
Rights & Permissions [Opens in a new window]

Summary

Spatial variability among experimental units is a common problem in field experiments on tree crops such as tea (Camellia sinensis). Spatial variability is partly accounted for by blocks, but a substantial amount remains unaccounted for and this may lead to erroneous conclusions. In order to capture spatial variability in field experiments on tea, six commonly used spatial analysis techniques were investigated: Covariate method with pre-treatment yield as the covariate, Papadakis and the Modified Papadakis nearest neighbour adjustments, Moving means and Modified moving means methods, and Autoregressive method. The data from long-term fertilizer experiments and cultivar evaluation trials, conducted at different locations by the Tea Research Institute of Sri Lanka, were used in the study. Spatial techniques were evaluated by means of their relative efficiency at each location and year. Evaluation of the four neighbour methods analysed in conjunction with the pre-treatment yield, revealed that spatial variability due to both past and current conditions are operative, especially in experiments with large blocks, and could be captured simultaneously. Relative efficiencies averaging 141% clearly indicated that the neighbour techniques in combination with pre-treatment yield would be effective in controlling the experimental error in tea experiments with large blocks (nine plots per block or more). Experiments with small blocks were not affected by spatial variability due to past conditions and only that due to current conditions need to be addressed. Neighbour techniques, on their own, were found to be adequate to capture spatial variability due to current conditions. The modified Papadakis technique was found to be the best with an average relative efficiency of 145%. The techniques investigated in the study can easily be implemented using standard statistical software. The precision of tea experiments could be increased by using covariate analysis with pre-treatment yield and any one of the four nearest neighbour adjustments tested, when the block size is large; and modified Papadakis technique, on its own, when the block size is small.

Type
Research Article
Copyright
Copyright © Cambridge University Press 2008

INTRODUCTION

Tea (Camellia sinensis), a perennial tree crop, is generally cultivated in hilly areas. Consequently, field experiments on tea have large plots sited mostly on moderately to steeply sloping land. For these reasons, the variability of the terrain and the physical and chemical soil properties, across experimental sites, is generally high. Various experimental designs are used to capture this variability (Quinn and Keough, Reference Quinn and Keough2002). The randomized complete block design (RCBD) is commonly used for field experiments because of its simplicity and applicability to field conditions (Basford and Turkey, Reference Basford and Turkey1995). Other designs used often for field experiments are row and column designs such as Latin Square Design and incomplete block designs with confounded factorial effects (Pearce, Reference Pearce2002). However, the control of error variation by means of experimental designs per se does not always achieve a satisfactory level of precision in large experiments, due to spatial variability between plots within a block and between plants within a plot (Rong-Cai et al., Reference Rong-Cai, Terrance, Stanford and Bandara2004). Spatial variability should therefore be taken into account when analysing such trials to increase their precision (Singh et al., Reference Singh, Malhotra, Ceccarelli, Sarker, Grando and Erskine2003).

The efficiency of spatial techniques, relative to block designs, has been evaluated frequently (Ball et al., Reference Ball, Mulla and Konzak1993; Bartlett, Reference Bartlett1978; Cullis and Gleeson, Reference Cullis and Gleeson1989; Reference Cullis and Gleeson1991; Kempton et al., Reference Kempton, Seraphin and Sword1994; Scharf and Alley, Reference Scharf and Alley1993). However, these evaluations have been mostly of annual crop trials. When perennial crop experiments were evaluated, in any given study, only a single spatial technique had been considered vis-à-vis the conventional analysis. Also, the pattern and extent of spatial variability may differ considerably between environments (Rong-Cai et al., Reference Rong-Cai, Terrance, Stanford and Bandara2004). In tea, especially, the size of plots, blocks and consequently the size of experimental sites, varies with the type of experiment (e.g. evaluation of fertilizers, cultivars). These variations may lead to differences in the efficiency of spatial techniques. Clearly, there is a need to identify effective techniques to control spatial variability in perennial crop field experiments. The objective of this study was to assess six commonly used model-based spatial techniques and evaluate the most efficient techniques for different types of experiments under different agro-climatic conditions.

MATERIALS AND METHODS

Yield data of a cultivar evaluation trial and two long-term fertilizer trials, testing macronutrients (N, K and Mg) and micronutrients (Zn, B, Mn), conducted by the Tea Research Institute of Sri Lanka, were used for the study. The cultivar trial had been repeated at four locations and the fertilizer trials at 11 locations to cover different climatic conditions that necessitate different agronomic practices. For instance, the duration of the pruning cycle at these locations ranges from 2.5 to 5 years. Details of the experiments are given in Table 1. The cultivar trial is recorded as a RCBD. However, as a large number of genotypes were being tested, the blocks were not compact; the plots were spread-out, in groups, due to limitations imposed by the nature of the site. In effect, each block comprised of several sub-blocks of uneven size.

Table 1. Details of the experiments and their respective locations.

AER: Agro-ecological region; WU: Upcountry wet zone; WL: Low country wet zone; WM: Mid country wet zone; IU: Up country intermediate zone; IM:– Mid country intermediate zone.

At the spacing of 4′×2′.

Spatial analysis

According to Brownie et al. (Reference Brownie, Bowman and Burton1993), the linear model describing spatial trend is:

(1)

\begin{equation}
y_{ij} = \mu + \rho _i + \alpha _j + T_{ij} + \varepsilon _{ij}
\end{equation}

where, yij = the yield of jth treatment in the ith block, μ = grand mean, ρi = ith block effect, αj = jth treatment effect, Tij = trend effect representing spatial variation in the ith block and the jth plot ɛij = random error where ɛijN (0,σɛ 2).

A distinctive feature of this model is that it can be used to describe most spatial techniques. The six spatial techniques considered in the present study were:

  1. (i) Classical covariate method (CCM) where pre-treatment yield (yield over the six-month period prior to the experiment) is used as the covariate. In this technique Tij of the model (1) is defined as θ(x ijx) where xij is the pre-treatment yield of jth plot in the i th block, x is the mean of the pre-treatment yield and θ is the regression coefficient.

  2. (ii) Papadakis nearest neighbour method (PNNM) (Papadakis, Reference Papadakis1984) where Tij is defined as with CCM but xij is the mean plot residuals of eastern and western neighbours after fitting the model without accounting for spatial effect, i.e. xij = (e ij−1 + e ij+1)/2.

  3. (iii) Modified Papadakis nearest neighbour method (MPNNM) (Wilkinson et al., Reference Wilkinson, Eckert, Hancock and Mayo1983) where xij is the mean of four plot residuals of eastern and western neighbours, i.e. xij = (e ij−2 + e ij−1 + e ij+1 + e ij+2)/4.

  4. (iv) Moving average method (MAM) (Townley-Smith and Hurd, Reference Townley-Smith and Hurd1973) where xij is the arithmetic mean of two unadjusted plot yields of eastern and western nearest neighbours, i.e., xij = (y ij−1 + y ij+1)/2

  5. (v) Modified moving average method (MMAM) where xij is the arithmetic mean of four unadjusted plot yield values of eastern and western nearest neighbours, i.e. xij = (y ij−2 + y ij−1 + y ij+1 + y ij+2)/4

  6. (vi) Autoregressive method (AR(1)) (Gilmour et al., Reference Glimour, Cullis and Verbyla1997; Gleeson and Cullis, Reference Gleeson and Cullis1987). AR(1) is known to be capable of fitting the field trends directly. This technique assumes that the residuals are distributed according to spatial correlation models. The commonly used spatial correlation model for AR(1) is:

    
\begin{equation}
Cov(\varepsilon _{ij} ,\varepsilon _{ij'} ) = \sigma ^2 Corr(\varepsilon _{ij} ,\varepsilon _{ij'} ) = \sigma ^2 \rho ^{| {i - j} |}
\end{equation}

where, σ 2 is the residual variance and ρ is the autocorrelation parameter. The presence of a spatial trend suggests that the neighbouring plots tend to be more alike than those further apart (ρ > 0). In the AR(1) procedure, blocks are considered as a random factor so that only the within block spatial variability will be taken into consideration.

The residuals are usually used instead of means in nearest neighbourhood estimation. However, some studies (Lawrence and Townley-Smith, Reference Lawrence and Townley-Smith1975; Mack et al., Reference Mak, Harvey and Berdahl1978; Rosielle, Reference Rosielle1980) have suggested that means could also be potential variates to be considered in nearest neighbour estimation. This was the main reason for moving average methods to be considered in the study. Obviously it is easier to use means than residuals. Due to the undulating nature of tea experimental sites, blocks are established along the contour. Thus, often several blocks are found in a single contour with a considerable distance between blocks. As spatial adjustments cannot be done here for both north–south and east–west directions, only one direction, the direction of the block, was considered. This often happened to be the east–west direction. To determine the extent to which spatial correlations are influenced by past and current conditions, all four neighbour methods were evaluated with and without CCM.

Though CCM is considered as a spatial method in the present study, it is not an explicit spatial approach. CCM can explain non-spatial variation also and is used extensively as an error reduction technique in tea experimentation.

The calculations and analysis described above were performed with SAS Version 8.1. PROC MIXED was employed for the restricted maximum likelihood (REML) analysis of the AR(1) method and PROC GLM was used for rest of the analysis.

Efficiency of spatial methods

An appropriate measure of relative efficiency is essential to evaluate the different models. Relative efficiency measured in terms of s.e.d. seems most relevant because it is directly used for comparisons between treatments, has the same scale as the original attributes and includes the efficiency factor (Qiao et al., Reference Qiao, Basford, Delacy and Cooper2000). Therefore, relative efficiency of spatial analysis methods is computed as, s.e.d. u/s.e.d. a, where s.e.d. u and s.e.d. a are unadjusted (classical analysis) and adjusted (after taking account of spatial effect) standard error of the difference, respectively. In the case of AR(1), relative efficiency was computed using REML, where residual variance is directly estimated without explicitly considering the degrees of freedom.

Comparison of different spatial models

The comparison of models was carried out using the Akaike Information Criterion (AIC) (Akaike, Reference Akaike1974). PROC MIXED of SAS was used to compute the AIC values – the lower the AIC value, the better the model.

RESULTS

Application of CCM to the macronutrient trial showed that pre-treatment yield was a highly significant covariate (p < 0.01) at all the locations and years studied, except at Ury Estate. However, in the micronutrient trial, CCM was significant only on 9 out of 20 occasions (locations × years). The relative efficiency of CCM ranged from 100% to 145% in the macronutrient trial and 101% to 158% in the micronutrient trial, across all locations and years. CCM of course was not applicable to the cultivar evaluation trial.

In the macronutrient trial, PNNM made a significant improvement (p < 0.01) in controlling error variation at all locations and on 11 of 17 occasions. However, in the micronutrient trial, PNNM did not produce any significant improvement (p > 0.1) on almost all occasions; the exceptions were Indola in 2000 and 2003, Madulkelle in 2000 and St Coombs in 2000. In the cultivar evaluation trial, PNNM was significant only at St Joachim 1, St. Joachim 2 and Passara, in 2003. The relative efficiencies ranged from 99% to 122% in the macronutrient trial, 97% to 116% in the micronutrient trial and 102% to 115% in the cultivar trial (Table 2).

Table 2. Mean relative efficiency of spatial techniques.

Values in the parenthesis are relative efficiencies for four neighbour methods in conjunction with CCM.

NA – Not applicable.

In the macronutrient trial, MPNNM produced a significant (p < 0.05) improvement at all locations except Lumbini and Court Lodge in 2000 and Talgaswala in 2001. In the micronutrient trial too, MPNNM was significant (p < 0.05) on all occasions except Indola in 2001 and 2004 and Madulkelle in 2003. In the cultivar evaluation trial, MPNNM was effective only at St. Joachim 1 and St. Joachim 2. In the micronutrient trial, the relative efficiency of MPNNM was much higher (105–216%) than in the macronutrient trial (100–120%) and the cultivar evaluation trial (102–121%) (Table 2).

MAM gave a significant (p < 0.05) improvement in the macronutrient trial on all occasions, except Lumbini and Ury in 2000. In the micronutrient trial, MAM was not significant except on three occasions: Greenwood in 2003, Indola in 2000 and Madulkelle in 2000. In the cultivar evaluation trial, MAM was significant (p < 0.05) only at St. Joachim 1 and St. Joachim 2. The relative efficiency ranged from 103% to 143% in the macronutrient trial, 97% to 107% in the micronutrient trial and 99% to 110% in the cultivar evaluation trial (Table 2).

In the macronutrient trial, MMAM produced a significant (p < 0.05) improvement except at Houpe in 2001, Lumbini in 2000, Talgaswala in 2001 and 2002, and Ury in 2000. In the micronutrient trial, MMAM gave a significant (p < 0.05) improvement on 11 out of 20 occasions, and on seven out of 11 occasions in the cultivar evaluation trial. The relative efficiencies were 104–127%, 97–125% and 99–113% in macronutrient, micronutrient and cultivar evaluation trials respectively (Table 2).

The AR(1) method produced very little improvement except in the macronutrient trial, where it was significant (p < 0.05) on 11 out of 15 occasions and the relative efficiency ranged from 101.5% to 137% (Table 2). It is noteworthy that the Newton Raphason algorithm in PROC MIXED failed to converge on two occasions. In the other two trials, AR(1) did not produce any significant improvement. The relative efficiency was 100–105% in the cultivar evaluation trial and 99.5–102% in the micronutrient trial.

Serial correlation analysis was also performed in order to confirm the effectiveness of AR(1). In the macronutrient trial this gave a significant r = >0.33 (p < 0.05) correlation on 16 out of 17 occasions, but it was significant only on three out of 16 occasions and none in the micronutrient and cultivar evaluation trials respectively.

The four neighbour spatial methods, PNNM, MPNNM, MAM and MMAM, were also evaluated in conjunction with CCM. The combination with CCM did not bring about any change in significance of the neighbour methods in the macronutrient trial. However, in the micronutrient trial, the significance of CCM changed on 12 out of 80 occasions. CCM which was significant when applied separately, turned out to be non significant (p > 0.1) when applied in conjunction with neighbour methods. With MPNNM, the significance changed five times in 20 occasions (significant without CCM and non significant with CCM). With PNNM, MAM and MMAM there were no changes. In the macronutrient trial, CCM in conjunction with spatial methods produced relative efficiencies of 139, 137, 146 and 140% with PNNM, MPNNM, MAM and MMAM respectively. In micronutrient trials the corresponding values were 126, 158, 119 and 131% respectively (Table 2). Overall, combining with CCM did not bring about a substantial difference between neighbour methods, with respect to the number of times each method was found to be significant as well as in their relative efficiency.

According to the conventional analysis of RCBD, significant block effect was observed in 14 out of 16 occasions in large blocks (macronutrient trial). However, for small blocks (micronutrient trial), the block effect was significant only on two occasions out of 20. In cultivar trials this was 8 out of 13 occasions.

The AIC values for goodness-of-fit of different models are presented in Table 3. Low AIC values were recorded with MAM and CCM in the macronutrient trial and with MPNNM in the micronutrient and cultivar evaluation trials. Specifically, in the micronutrient trial, MPNNM exhibited highly consistent results. The pattern of AIC was exactly the same when the four methods were combined with CCM. However, AIC values decreased substantially when they were in combination with CCM, especially in the years and locations where CCM by itself was significant.

Table 3. Akaike Information Criterion (AIC) values with different methods of analysis.

Values within the parenthesis are AIC values for neighbour methods in conjunction with CCM.

NA – Not applicable.

DISCUSSION

Generally, the methods tested had a positive impact on experimental precision but with different levels of efficiency. This no doubt reflects the fact that different methods capture different aspects of spatial variability. Nevertheless, efficiency values greater than 100%, in most years and across locations, establish the potential of these methods to capture spatial variability in block designs.

The micronutrient and macronutrient experiments had a similar plot size (about 40 bushes per plot) and shape. An undulating terrain was also a common feature of the sites of both experiments. The main difference between the experiments was in the block size – five or six treatment plots per block in the micronutrient trial and nine plots per block in the macronutrient trial. Most of the methods tested were effective in the macronutrient trial where the block size was relatively large. This shows that spatial techniques can be used effectively in experiments with large blocks. However, this advantage was not seen in the cultivar evaluation trial with very large blocks containing 22 to 61 genotypes. This can be ascribed to the improper layout of the cultivar evaluation trial where a block consisted of several sub-blocks containing 2–10 plots each. The plot size was also smaller than in the nutrient trials.

In the macronutrient trial, all the methods tested were effective with CCM being the most effective. This shows that CCM is the most effective method to capture spatial variability when the block size is large (at least with nine plots per block).

MPNNM performed better than the other methods in the micronutrient trial indicating that MPNNM is effective in capturing spatial variability in small blocks. MPNNM was moderately effective in the macronutrient trial indicating that MPNNM can account for spatial variability even when the block size is large.

MAM was found to be moderately effective with large bocks but not effective with small blocks. PNNM and MMAM seem to be equally effective, at a moderate level, with large blocks as well as small blocks.

AR(1) was found to be moderately effective in the macronutrient trial but not in the micronutrient trial. AR(1) specifically accounts for linear trends. Linear trends being less likely with small blocks could explain the poor performance of AR(1) in the micronutrient trial. AR(1) being moderately effective in the macronutrient trial, and the results of the serial correlation analysis lend support to the view that a linear trend can be detected only with large blocks. It may be concluded that AR(1) is appropriate only for experiments with large blocks.

In the micronutrient trial MPNNM performed considerably better than PNNM. MPNNM uses four neighbouring plots to adjust a plot value while PNNM uses only two. Using four plots considerably reduces the probability of bias in trend estimation and is the likely basis for MPNNM's superiority.

MMAM is expected to estimate the trend better and thereby perform better than MAM. In fact this was observed in the micronutrient trial, but it was not the case in the macronutrient trial. A possible explanation is that spatial variability due to past conditions was dominant in the macronutrient trial.

Since CCM captures initial variability, it can be viewed as a method that captures spatial variability due to past conditions. The other methods tested can be considered as methods that capture the spatial variability due to current conditions or the long-term nature of the experiments.

An important finding that stems from this study is that both past and current spatial variability can be captured simultaneously. This became evident when the neighbour methods were evaluated in conjunction with CCM. When the neighbour methods were evaluated in conjunction with CCM, especially in the macronutrient trial, seven out of 14 times both CCM and neighbour methods became significant proving that past and current spatial variability are two separate aspects. However, this was not clearly evident in the micronutrient trial. In the micronutrient trial, CCM and other neighbour methods were rarely significant when analysed together. Thus it seems both aspects of spatial variability can be detected simultaneously only when the block size is large, not when it is small. In micronutrient trials, CCM was not significant when it was evaluated with other methods. This indicates that spatial variability due to past conditions is significant only when the block size is large. In fact, on 12 occasions in the micronutrient trial, CCM which was significant when analysed separately, became non significant when analysed in conjunction with the neighbour methods. However, a non significant CCM never turned significant when analysed in conjunction with neighbour methods. This also supports the contention that spatial variability due to past conditions is either not operative or cannot be detected when the block is small. In the macronutrient trial, when neighbour methods were evaluated along with CCM, the error reduction by CCM was greater than that by neighbour methods. This shows that spatial variability due to past conditions is more dominant than current spatial variability when the block size is large. On the whole, all four neighbour methods, analysed along with CCM, were more or less of the same efficiency. Therefore, any of the four neighbour methods studied could be used to increase the efficiency of field experiments on tea.

In large block experiments, comparing RCB with spatial methods, the majority of the trials with significant spatial trends also had significant RCB block effects. But in small block experiments, non significant RCB block effects had significant field trends. Though these experiments were designed assuming that major trends differences are between blocks as happened in well-designed experiments, due to the undulating nature of tea experimental sites spatial variability (specifically trends due to current conditions) with in blocks might be prominent though block size is small.

One of the results found in this study is that blocking often performs poorly in the function of reducing experimental error. It is clear that adjustment by neighbouring methods can often be effective especially on irregular experimental sites.

Inconsistency in efficiency across time suggests that the spatial variability within a block may be transient in nature. This may arise from numerous biological and/or physical phenomena that interact to influence differences in soil characteristics among plots (Smith and Casler, Reference Smith and Casler2004). Despite the transient nature of spatial variability, spatial methods evaluated in the study were found to be effective. Hence the methods evaluated have a potential use under varied conditions.

CONCLUSIONS

Spatial analysis techniques, in conjunction with the standard practice of using pre-treatment yield as a covariate (CCM), have an important role in reducing error in long-term field experiments on tea.

Spatial variability due to both past (inherent) and current conditions are encountered, especially in experiments with large blocks (nine plots per block or more). Efficiency of these experiments can be increased by addressing both aspects of spatial variability simultaneously.

Neighbour techniques in combination with CCM were effective in controlling experimental error in experiments with large blocks. Experiments with small blocks were not affected by spatial variability due to past conditions, and only that due to current conditions was operative and need to be addressed. Neighbour techniques, on their own, were found to be adequate to capture spatial variability due to current conditions; MPNNM was the most effective.

The precision of tea experiments may be increased by using CCM and any one of the four nearest neighbour adjustments tested, when the block size is large; and modified Papadakis technique (MPNNM), on its own, when the block size is small.

Acknowledgements

The authors gratefully acknowledge Dr L. S. K. Hettiarachchi, Head of the Soil and Plant Nutrition Division and Dr (Mrs) M. T. K. Gunasekara, Head of the Plant Breeding Division, and the staff of the two divisions for provision of data for the study. Very special thanks also to Dr Thilak Wettansinghe for his valuable comments, suggestions and editing the final draft of the manuscript.

References

REFERENCES

Akaike, H. (1974). A new look at the statistical model identification. Institute of Electric and Electronic Engineers Transactions on Automatic Control 19:716723.CrossRefGoogle Scholar
Ball, S. T., Mulla, D. J. and Konzak, C. F. (1993). Spatial heterogeneity affects variety trial interpretation. Crop Science 33:931935.CrossRefGoogle Scholar
Bartlett, M. S. (1978). Nearest neighbour models in the analysis of field experiments. Journal of Royal Statistical Society B 40:147174.Google Scholar
Basford, K. E. and Turkey, J. W. (1995). Inter comparing residuals to find outliers in randomized blocks. Australian Journal of Agricultural Research 46:451461.CrossRefGoogle Scholar
Brownie, C., Bowman, D. T. and Burton, J. W. (1993). Estimating spatial variation in analysis of data from yield trials: A comparison of methods. Agronomy Journal 85:12441253.CrossRefGoogle Scholar
Cullis, B. R. and Gleeson, A. C. (1989). The efficiency of neighbour analysis for replicated variety trials in Australia. Journal of Agricultural Science 113:223239.Google Scholar
Cullis, B. R. and Gleeson, A. C. (1991). Spatial analysis of field experiments – an extension to two dimensions. Biometrics 47:14491460.CrossRefGoogle Scholar
Gleeson, A. C. and Cullis, B. R. (1987). Residual maximum likelihood (REML) estimation of a neighbour model for field experiments. Biometrics 43:277288.CrossRefGoogle Scholar
Glimour, A. R., Cullis, B. R. and Verbyla, A. P. (1997). Accounting for natural and extraneous variation in the analysis of field experiments. Journal of Agricultural, Biological and Environmental Statistics 2:269293.CrossRefGoogle Scholar
Kempton, R. A., Seraphin, J. C. and Sword, A. M. (1994). Statistical analysis of two dimensional variations in variety yield trials. Journal of Agricultural Science. Cambridge 122:335342.CrossRefGoogle Scholar
Lawrence, T. and Townley-Smith, T. F. (1975). Use of moving means in grass yield trials. Canadian Journal of Plant Science 55:587592.CrossRefGoogle Scholar
Mak, C., Harvey, B. L. and Berdahl, J. D. (1978). An evaluation of control plots and moving means for error control in barley nurseries. Journal of Crop Science 18:870873.CrossRefGoogle Scholar
Papadakis, J. S. (1984). Advances in the analysis of field experiments. Proceedings of the Athens Academy 59:326342.Google Scholar
Pearce, S. C. (2002). The control of environmental variation within the experimental area. Experimental Agriculture 38:445456.CrossRefGoogle Scholar
Qiao, C. G., Basford, K. E., Delacy, I. H. and Cooper, M. (2000). Evaluation of experimental designs and spatial analysis in wheat breeding trials. Theoretical and Applied Genetics 100:916.CrossRefGoogle Scholar
Quinn, G. P. and Keough, M. J. (2002). Experimental Design and Data Analysis for Biologists. Cambridge University Press.CrossRefGoogle Scholar
Rong-Cai, Y., Terrance, Z. Ye., Stanford, F. B. and Bandara, M. (2004). Efficiency of spatial analysis of field pea variety trials. Journal of Crop Science 44:4955.Google Scholar
Rosielle, A. A. (1980). Comparison of lattice designs, check plots and moving means in Wheat breeding trials. Euphytica 29:129133.CrossRefGoogle Scholar
Scharf, P. G. and Alley, M. M. (1993). Accounting for spatial yield variability in field experiments increases statistical power. Agronomy Journal 85:12541256.CrossRefGoogle Scholar
Singh, M., Malhotra, S., Ceccarelli, S., Sarker, A., Grando, S. and Erskine, W. (2003). Spatial variability models to improve dry land field trials. Experimental Agriculture 39:151160CrossRefGoogle Scholar
Smith, K. F. and Casler, M. D. (2004). Spatial analysis of forage grass trials across locations, years and harvests. Crop Science 44:5662CrossRefGoogle Scholar
Townley-Smith, T. F. and Hurd, E. A. (1973). Use of the moving means in wheat yield trials. Canadian Journal of Plant Science 53:447450.CrossRefGoogle Scholar
Wilkinson, G. N., Eckert, S. R., Hancock, T. W. and Mayo, O. (1983). Nearest neighbour analysis of field experiments. Journal of Royal Statistical Society B 45:151211.Google Scholar
Figure 0

Table 1. Details of the experiments and their respective locations.

Figure 1

Table 2. Mean relative efficiency of spatial techniques.

Figure 2

Table 3. Akaike Information Criterion (AIC) values with different methods of analysis.