Chapter 3 Materials & Methods
5.3 The future of biodiversity conservation
Criticism has been raised as to the ability of scientific studies that are not hypothesis driven and experimental in nature to answer ecological questions (Lindenmayer & Likens, 2010). A concern for ‘passive’ and curiosity-driven monitoring studies is the difficulty of resolving drivers of change when there are no treatments, and it is true that most of the literature on the drivers of decline are correlational (Fox, 2013; Hardy, Sparks & Dennis, 2014). However the argument against curiosity - driven studies does not appear to consider the practical and social aspects of science, an d the fact that research is largely limited by funding. Observations need to be made first before hypotheses can be formed and experimental studies designed (Keeling, 1998), and often before research will be funded. This dataset, for example, was instrumental in obtaining funding from the Brian Mason Scientific and Technical Trust to complete digitation of the data and make it publicly available. Thus, ‘Cinderella’ science, though unglamorous (Nisbit, 2007) is still a very necessary part of conservation science. Further, a great deal of the long-term data sets used in studies of Lepidoptera decline overseas were due to the large concerted effort of volunteers and enthusiasts from overseas, and it is the massive scale of such studies that appears to make the temporal ecological modelling
worthwhile (Dennis & Sparks, 2007; Kozlov et al., 2010; Salama et al., 2007). Therefore, unpaid research has the potential to contribute a great deal to knowledge of Lepidoptera species. Indeed, the work presented here would suggest that, with the lack of research on New Zealand pollinators in general - experimental or otherwise - we cannot afford to ignore any ecological data that might help us fill the gap in knowledge of temporal trends in Lepidoptera abundance and diversity . From this perspective, community-driven research is key to the future of New Zealand biodiversity
5.4
Next steps
Increasing the number of sites and observations in the database is needed to strengthen the trends documented here. Based on the close match of the preliminary results to overseas studies, it is expected that additional observations will only enhance the current results. As with spatial studies, however, it is always possible that temporal data misses important change s if terminated too early (Keeling, 1998) or if gathered too infrequently; it was only due to occupancy modelling, for example, that the temporal declines in declines in A. caja were noticed after ineffective temporal studies (Conrad et al., 2002). Completing entry of Brian’s earlier sites is therefore important for capturing as much temporal variation as possible (Van Strein et al., 1997). A variety of assumptions also went into databasing and analyses which will need adjusting and clarifying with Brian before the tests are truly robust representations of wider trends.
Further analyses will also be worthwhile carrying out in order to bring the knowledge of New Zealand Lepidoptera closer to that of the global literature. Ordination of changes in species composition of sites could be expected to shed light on the features of sites that are hosting different levels of abundance and richness and which species are most sensitive to ongoing landscape and cli mate changes. Similarly, from a species perspective, quantifying life-history traits which may indicate risk of decline may aid conservation initiatives (Blake, Woodcock, Westbury, Sutton & Potts, 2011). It would also be interesting to focus on changes in abundance of a few rare and a few common New Zealand species: Lycaena and Zizina species would both be worthwhile, since species from this genus are also found in Britain where they have been well monitored (Léon-Cortés et al., 1999). Given Britain so far has documented greatest declines, such a comparison may indicate where our country stands in the high stakes of Lepidoptera biodiversity (New, 2004).
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