Pesticide Usage in Scotland: Outdoor Vegetable Crops 2017

This publication presents information from a survey of pesticide use on outdoor vegetable crops grown in Scotland during 2017.

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Appendix 5 – Standard errors

The figures presented in this report are produced from surveying a sample of holdings rather than a census of all the holdings in Scotland. Therefore the figures are estimates of the total pesticide use for Scotland and should not be interpreted as exact. To give an idea of the precision of estimates, the report includes relative standard errors ( RSE) (Table 32). Standard errors are produced using the raising factors. An overall variance is calculated by summing the variance estimates for individual strata (region and size group) multiplied by the square of their raising factors. These variance estimates include a finite population correction. The overall standard error is calculated from the overall variance by taking its square root. This method of standard estimation was implemented as it is both relatively straightforward and has advantages over ratio estimator methods when within-strata sample sizes are small.

Standard errors are expressed as percentage relative standard errors (Table 32) for both total pesticide use by area treated and for weight applied. Larger relative standard errors mean that the estimates are less precise. A relative standard error of 0 per cent would be achieved by a census. A relative standard error of 100 per cent indicates that the error in the survey is of the same order as the measurement. Relative standard errors may be reduced with larger sample sizes. However, larger relative standard errors can also result from greater variability in pesticide use among holdings.

The RSE for estimates of total pesticide use on vegetable crops (Table 32) was ten per cent for area and seven per cent for weight, compared with seven and eight per cent respectively in 2015. For constituent crop groups, the RSE varied from three to 29 per cent for area and four to 56 per cent for weight, varying with sample size and uniformity of pesticide regime encountered. For Brussels sprouts, cauliflower, leeks, lettuce, other vegetables and rhubarb, a standard error could not be calculated due to too few active ingredients being recorded; therefore pesticide estimates for these crops should be treated with caution. These standard errors, particularly at individual crop level are higher than in previous surveys. This may have been influenced by the reduced sample size which is a result of an increase in farmer non-participation rates. Higher standard errors mean that there is more uncertainty associated with estimates of pesticide use.

Table 32 Relative standard errors

Relative standard errors ( RSE) for the area treated (ha) with pesticide and for weight of active substance (kg) applied

Area SE

(%)

Weight SE (%)

Broad beans (1)

9

10

Brussel sprouts (2)

NC

NC

Cabbages (1)

3

1

Calabrese (1)

3

7

Carrots (1)

16

22

Cauliflower (2)

NC

NC

Leeks (2)

NC

NC

Lettuce (2)

NC

NC

Other vegetables (2)

NC

NC

Rhubarb (2)

NC

NC

Turnips & swedes (1)

29

56

Vining peas

5

8

All vegetable crops

10

7

(1) For these crops standard errors could not be calculated for all strata due to insufficient data in the sample, as these strata have not been used in the aggregate totals for the region the overall RSE values should be treated with caution

(2) Standard errors could not be calculated ( NC) for Brussel sprouts, cauliflower, leeks, lettuce, other vegetables and rhubarb because there were too few active substances recorded. Therefore estimates for these crops should be treated with caution

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