RESEARCH NOTES Consistency in hand-searching for terrestrial snails J.F. Ward-Booth and G.B.J. Dussart Canterbury Christ Church University College, Canterbury, CT1 1QU email: [email protected] A range of techniques are available for sampling terrestrial molluscs. Soil and litter can be sieved and examined under the microscope to find micro-molluscs which mainly comprise adults 3 mm1 Hand searching is often used in conjunction with litter and soil sampling.2 For example, hand searching has been used to sample quantitatively snail species richness above ground level in Madagascan rainforests.3 However, when undertaking ecological monitoring in habitats of restricted size, the removal of litter and soil samples can be destructive and consequently interfere with the objectives of the investigation, in which case, hand-searching may be the only option. Field surveys may be separated by time and geography. For example, distributions of Cepaea nemoralis (L.) in Dorset were compared with those of Cyril Diver, collected seventy years earlier.4 By contrast, in a different sampling exercise,5 three observers searched one hectare at different geographic locations. In his 1938 paper, Boycott6 summarised a lifetime of malacological field studies in which he had hand searched sites all over Britain over a long period of time. In these and other studies, there is a tacit assumption that hand searching is done consistently over time and space. The aim of this study was therefore to investigate the consistency of hand-searching for macromolluscs in an agricultural area of South East England. Two aspects were of interest. Firstly, do different observers find similar amounts and types of molluscs in replicated sampling; secondly does a single observer find similar results across replicated samples? It was also intended to investigate ancillary factors which could affect sampling performance e.g. time of day. Sampling comprised intense fifteen-minute hand searches for macromolluscs (adults 3mm maximum shell length) across 1 3 metre areas of field margin on 27/9/1996. Eighteen field margins of varying soil type, topography and land use were included. For most investigations, there were three replicates giving a total of 45 minutes at each site. Molluscs were collected in the field by hand and with forceps, sorted in the laboratory and counted. The few slugs found were not included in analyses. Data were recorded for (i) live snails (‘snails’) (ii) dead empty shells (‘shells’) and (iii) snails plus shells (‘snails+shells’). When appropriate, data were log10(x 1) transformed to normality. In order to investigate the consistency of inter-operator performance, four operators were used. Operator A was an experienced malacologist with knowledge of the area. Operator B was an experienced malacologist without such knowledge. Operator C had a little experience of field malacology and D was inexperienced. The operators made contemporaneous, 15-minute hand searches for macromolluscs on adjacent, and apparently similar areas at each of ten sites J. Moll. Stud. (2001), 67, 502–506 (soil temperature 13–17C; relative humidity 52–66%) The ten sites covered a range of habitat types in order to include a range of snails densities. After sorting and counting, the collected material was grouped into four size classes by operator A in the laboratory. In order to investigate the consistency of single operator performance, operator A made three replicated 15-minute searches at each of the ten sites previously mentioned between 11–14th of August 1997. In order to investigate the effect of vegetation type on operator performance, operator A carried out three replicated 15 minute searches at each of four sites along a ditch on clay soil with varying amounts of vegetation. Sampling took place on 2–3/07/1997 (temperature 14–15C; humidity 90–100 % with light drizzle). Molluscs were collected, sorted, counted and marked with nail varnish before being randomly distributed back in the same area. The procedure was repeated so that each animal could have been captured three times. Operator performance at each site was expressed as:Number of macromolluscs caught three times Total number of individual macromolluscs found 100 This was not treated as a formal mark-recapture experiment as there was no intention to estimate population density. An experiment to compare sampling performance for night-time sampling compared with day-time sampling was conducted. Operator A carried out ten 15-minute daytime searches along seventy metres of ditch on the margin of a field of hay on clay soil between 09:30 and 13:00 on 01/09/1997. During similar weather conditions, adjacent, similar areas were sampled at night with a torch between 20:30 and 24:00 on 03/09/1997. There was a time lapse to allow the snails to resettle. During the investigation of inter-operator performance, 40.1% of the 1981 snails and shells found in this experiment were collected by operator A and 75% of operator A’s data lie above the median of operators B, C and D (Fig.1a). 53.6% of the snails shells were found at site 10. Here, molluscs were so abundant that handling became a limiting factor for all operators. Operator A and site 10 were obviously exceptional. When site 10 was omitted from the data set (Fig.1b) there was no significant variation in the performance of the operators (F2,16 1.9 P 0.17) but significant differences between the sites (F8,16 15.3 P 0.001) (log10 transformed data). These results were confirmed by tests for concordance which showed highly significant agreements between the site ranking by all the operators for each of ‘snails’, ‘shells’ and ‘snails shells’ (P 0.005 in each case). Between 3 and 7 species were found at each of the 10 sites. © The Malacological Society of London 2001 RESEARCH NOTES Operator D with no experience of field malacology found fewer species than A, B or C. Indeed, 75% of the other searchers’ data lay above this operator’s median. The null hypothesis was rejected for all four operators across sites 1 to 10 inclusive (Operators F3,27 7.3 P 0.001; Sites F9,27 3.1 P 0.01). However, there was no significant difference between the two most experienced operators in the number of species found (F1,9 4.4 P 0.05). All operators collected similar numbers of snails in the four size categories across ten sites (F3,9 3.0 P 0.05) but there was significant variability in the numbers of snails caught (F3,9 22.9 P 0.001). The peak abundance of 5–10 mm sized molluscs (Fig. 2) perhaps reflects the fact that this category includes adults of a small species (Oxychilus helveticus Blum, adult shell breadth 8–10 mm) and juveniles of a large species (C. nemoralis L. adult shell breadth 18–25 mm). Few molluscs in the smallest size category were found, which could be due to lack of acuity in the method or because the smaller molluscs were actually absent. In a separate investigation on a cold day in January 1998 however, a 15m2 site was hand searched for four hours and 489 juvenile ( 5mm) Monarcha cantiana (Montagu) were found. During the investigation of single operator performance, analysis of log10 transformed data for numbers of individual molluscs showed no significant variation between operator A’s replicates but as expected, there was variation between sites (Table 1). When the effect of vegetation on operator performance was investigated, there was no significant variation in the mean number of species recorded between sampling sessions for snails (F2, 3 2.1 P 0.21) or shells (F2, 3 4.2 P 0.07). The percentage of shells and snails found on all three occasions varied depending on the circumstances (Table 2). As might be expected, sites which were easiest to search gave the highest yield of thrice-caught molluscs . Thirteen species of snail were found during night sampling and eleven species by day. The difference comprised one shell of Cernuella virgata (da Costa) and one live Helix aspersa (Müller). The animals were contagiously distributed and Wilcoxon paired-rank test showed that although more animals were found in daylight, the differences between night and day sampling were not significant for snails (W 14 n10 P 0.20) and shells (W 9.5 n10 P 0.10). However, there was a significant difference for snails shells (W 7 n10 P 0.05). Mating molluscs were only seen at night. In later, comparable hand searches by day across this field margin from June 1996 to July 1997, sixteen species of macromolluscs were caught, with three species being recorded only once. Aegopinella nitidula (Draparnaud) is a small, brown, discoid, snail 8–10 mm. broad.7 When dead and in the soil it is Figure 1. a. Box and whisper plot to compare collecting capability of four operators at ten different sites. b. The same data, recalculated without the extreme values from Site 10. 503 RESEARCH NOTES difficult to find at night. Data for this species were somewhat variable between samples. However, when A. nitidula was removed from the data set, analysis of variance of log10 transformed data showed no significant differences between the mean number of snails found by day and by night (F1,9 4.8 P 0.05). Methods for quantitatively sampling terrestrial molluscan populations have been reviewed.8 Where a complete species list is the prime objective, for example in a taxonomically focussed study, extraction of molluscs from soil and litter is essential. However, there are sampling problems. For example, there can be large differences in results from bulkand hand-sorted samples of molluscan communities from Pleistocene deposits.1 Despite these seminal works, there seems to be little research which compares the performance of different operators in hand searching for terrestrial snails, or which has quantitatively assessed factors such as day and night sampling. Although soil and litter sieving are a preferred approach, in some situations, removal of soil and litter may not be appropriate. Constraints of time, money and ecological strategy may limit the investigator to hand-searching, for example where the experimental design dictates repeated visits to the same, small habitat. In the study described here, a number of parameters of hand-searching were investigated. Table 1. Consistency of performance of operator A; results of two factor analysis of variance for sites of varied topography. Operator A’s replicates snails shells snails shells F2, 9 0.21 P 0.81 F2, 9 0.44 P 0.65 F2, 9 0.54 P 0.59 Sites F2, 9 21.0 P 0.001 F2, 9 10.8 P 0.001 F2, 9 25.4 P 0.001 For total abundance of molluscs, the experienced operator who was familiar with the area found more snails than the other operators. Vegetation form and density was important; sites with thick, tufted vegetation might need bigger search areas or longer times in order to improve consistency in numbers of animals collected. Depending on the location, between 47 and 73% of the molluscs were found in three successive searches on different days; in total however, fewer animals were found in each successive search. The number of species recorded was not similarly affected, ‘more of the same’ being found by different operators. Although snails tended to quit areas of recently disturbed vegetation, no species was outstanding in this respect. The two experienced operators found statistically similar numbers of species across the ten sites. Despite the different soils, typography and land use, these sites would appear to support a similar number of niches throughout the year9 As might have been expected, the operator with no experience of field malacology found fewer molluscs in terms of both species and abundance. Although training of operators in species recognition is beneficial, our research indicates that such training need not be too prolonged, since both the experienced and the relatively inexperienced operators, unfamiliar with the area, had similar results. In one sense, operator A was too efficient. Mary Seddon (pers.comm.) has provided a week’s training course before using local labour in fixed time, hand-searches for snails in the eastern African rainforest. Where the objective of a survey is a comparative investigation of, say, anthropogenic environmental impact in different habitats, it might be necessary to address the issue of hyper- or hypo-efficient searchers. If the objective was to obtain a complete species list, then other sampling methods would be used and attention would focus on these highly efficient operators. With respect to mollusc size, a large number (489) of small juvenile M. cantiana were found in mid-winter. It thus appears that it is possible to successfully hand search for juve- Table 2. Yield of snails shells during three searches of sites with differing vegetation. Samples were marked and returned to the site. Site character In all cases, the dominant vegetation in the immediate sampling area comprised grass. All samples were taken in the same locality. Searching % found three times % of first batch found three times Number of molluscs Chalk soil on the edge of a wheat crop; sampling in a ditch with small grass patches 2–3 cm apart. Easy 72.6 91.8 124 Sandy soil on the edge of a wood; when the grass in this flat area was parted by hand, patches of soil were revealed Medium 54.2 82.1 24 Clay soil on the edge of a hay field; grass tufts were growing densely in this ditch but could be parted to reveal small areas of soil Medium/ difficult 51.1 73.1 45 Sandy soil adjacent to a hay field; growing on an extensive flat area, the grass grew in tufts which were too dense to reveal soil when parted. Difficult 46.9 72.2 81 504 RESEARCH NOTES Figure 2. Size comparison of number of shells and snails collected by four different operators searching the same ten sites. nile macro-molluscs above ground level, even in inclement weather. The distribution of live animals was contagious but dead shells were more evenly distributed. When close to the earth, A. nitidula was found more easily in daylight. Night-time sampling recorded two more species, and some mating molluscs were seen, including two pairs of M. cantiana and two pairs of Arion ater (Linné). The results reported here indicate that in general, unless mating observations are required, most sampling could be undertaken during daylight. At sites with abundant molluscs, the less experienced operators focussed on the most abundant species, with the result that they slightly underestimated species richness. There was also a considerable difference in the rate of collection of snails by the operators (ranging from 20.6 to 52.9 snails per minute). Here, dexterity influenced the results and created statistically significant variation between operators. A shorter search time might ease the problem but also result in a reduction in the number of species found. A compromise might be to increase the number of samples taken but to reduce the time spent on each one. In conclusion, it can be observed that almost every malacologist with an interest in terrestrial molluscs at some time undertakes hand searches,10 and this paper attempts to answer the question ‘How reliable is such a searching technique?’. The answer seems to be ‘It depends.’ Even minute hand searching will be unlikely to reveal micromolluscs such as Vertigo moulinsiana and is therefore inadequate for some investigations eg. demographic studies. However, timed hand searching produced consistent results for snails 3mm in that, depending on experience, operators found similar numbers of snails and all operators ranked sites similarly on snail abundance. Except for the untrained operator, similar numbers of species were found across the sites, and all operators found similar size ranges. Small, juvenile snails were found by intensive hand-searching, even in poor weather. Unless there is a specific need to investigate aspects such as nocturnal behaviour, night searching conveyed little benefit over intensive daytime searching. On the basis of these results, we suggest that hand searching can be useful in situations where more destructive sampling cannot be used or for comparative investigations which involve a range of personnel; for example, assessment of changes in land use on macromolluscan communities in remote locations. However, care should be taken to arrange training such that there are neither hyper-efficient, or hypoefficient searchers on the team. 505 REFERENCES 1. SPARKS, B.W. 1959. Proc. Linn. Soc. London, 60: 71–173. 2. CODDINGTON, J. A., GRISWOLD, C. E., DAVILA, D.S., PENARANDA, E. & LARCHER, S.F. 1991. In: The unity of evolutionary biology (E. Dudley, ed.) Fourth International Congress of Systematic and Evolutionary Biology. Portland, Oregon: 44–60. 3. EMBERTON, C., PEARCE, T.A., & RANDALANA, R. 1996. Malacologia, 38: 203–212. RESEARCH NOTES 4. CAMERON, R. 2000. Bull. Brit. Ecol. Soc., 31: p.23. 5. CAMERON, R., MYLONAS, M. & VARDINOYANNIS, K. 2000. J. Moll. Stud., 66: 131–142. 6. BOYCOTT, A.E. 1934. J. Ecol., 22: 1–35. 7. KERNEY, M.P. & CAMERON, G.R. 1979. A field guide to land snails of Britain and North-West Europe. Harper Collins, London. 8. BISHOP, M. 1977. Malacologia, 16: 61–66. 9. WARD-BOOTH, J.F. & PAGLIA, A. & DUSSART, G.B.J. 1996. In: I. Henderson (ed.) Slug and snail pests in agriculture (British Crop Protection Council Symposium Proceedings), 66: 125–131. 10. MENEZ, A. 2001. J. Conch., 37: 171–175. 506
© Copyright 2026 Paperzz