Diversidad y control biológico de insectos - CyberTesis UACh ...
Diversidad y control biológico de insectos - CyberTesis UACh ... Diversidad y control biológico de insectos - CyberTesis UACh ...
1994; Nowak et al., 2001; Tillman and Mulrooney, 2000; van den Berg et al., 1998), as well as other organisms like fish and non-target herbivores. These studies reported transient decreases in non-target numbers, specifically predators and parasitoids, immediately after λ-cyhalothrin treatment, but numbers recovered within a short period (usually 10-15 days). Our results suggest more long-term effects because the adverse effects of the insecticide were present for at least 40 days after treatment despite of the absence of barriers to movement and the fact that plots were surrounded by untreated grassland providing large sources of migrants. On the other hand, we consider that development stage of the invertebrates could explain, at least partially, these results: in the winter experiment, many individuals were immature and would have lower mobility than adults, therefore the recovery time in this season may be longer than in the spring or summer, seasons in which the most of the mentioned studies were conducted. The insecticide affected all community metrics in winter, while it affected diversity, evenness and dominance but not species richness in spring. The latter result must be interpreted cautiously, because the period between spraying and sampling in the spring experiment could have been long enough to allow migrants move from surrounded area to plots. Therefore, a negative impact of insecticide in the spring species richness could be masked by movement of these migrants. In relation to new emerging technologies, for example narrow spectrum insecticides, B. bassiana based biopesticides could play an important role because Chilean daily and beef industry can not compete with the rest of South America. Instead, it is focused in high- profit market niches such as organic or naturally raised cattle, where these new pesticides would not be allowed, in spite of they have better properties than the broad-spectrum insecticides currently used. In addition, if an IPM program is implemented for D. pallens control, many alternatives will be needed to design an robust and sustainable program. Linking between biodiversity and ecosystem functioning is accumulating support, but the issue remains unresolved (Ehrlich and Wilson, 1991). This relationship has been hypothesized to be linear (the rivet hypothesis, Ehrlich and Ehrlich, 1981), asymptotic (the redundancy hypothesis; Walker, 1992) or idiosyncratic (Lawton, 1994). Despite of these different theories, it can be argued that some level of biological diversity is necessary to maintain ecological function and resilience (Spratt 1997) but unfortunately, incomplete 113
knowledge of South Chile grassland functioning precludes us from identifying which fraction of the total diversity is needed to saturate most of the processes present in this agroecosystem. Therefore, until the trophic relationships between the different species could be revealed, we advocate for a conservative approach to diversity loss. Our studies were not designed to test hypotheses about specific functional groups or species, thus we can not identify the mechanism(s) that explain(s) the observed decreased diversity. In spite of this, we raise concerns about continued use of these kind of insecticides because several cases of natural regulation disruption have been recorded in intensified agricultural systems much before explicit mechanisms that explain natural herbivore regulation had been revealed (Hardin et al., 1995). In fact, there are several well documented cases of release of herbivore insects from control after removing their natural enemies (Hills and Taylor, 1951; Kenmore et al., 1984) or non-target herbivores acting like alternative prey when the pest is scarce and contributing to support early season build-up of generalist natural enemies (Settle et al., 1996). In an oversimplified system like pastures, any additional biodiversity loss could exacerbate this process, reduce the system stability and increase the reliance on external inputs, especially insecticides, to maintain its productivity. It remains a challenge to identify the several roles that the different species play in the pasture. However, as it was mentioned above, negative effects on ecosystem processes with declining biodiversity could be serious much before knowledge about explicit mechanisms could be gathered. Growers must be aware of how their pest practices may influence ecological processes before to make management decisions. Inundative biological control of Dalaca pallens using Beauveria bassiana spores did not affect grassland diversity and its components (species richness and evenness), at least in the short term. Lambda-cyhalothrin, one of the most common insecticides used for D. pallens control, affected all the community metrics (diversity, richness, evenness and dominance), with unknown consequences for the grassland agroecosystem. It was clear that the community-level impact of this broad- spectrum insecticide was far greater that any effect of Beauveria bassiana on arthropod community. 114
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- Page 119 and 120: Introduction. Declining diversity h
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- Page 157 and 158: BIBLIOGRAFIA Alarcón R. 1997. Resp
- Page 159 and 160: isolated from the European cockchaf
- Page 161 and 162: Hardin MR, Benrey, M Coll, WO Lamp,
- Page 163 and 164: Lockwood JA, 1993. Environmental is
- Page 165 and 166: Pimentel D, C Glenister, S Fast y D
- Page 167 and 168: Swift MJ, J Vandermeer, PS Ramakris
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- Page 175 and 176: Anexo 5. Capturas provenientes de l
- Page 177: Anexo 7. Capturas provenientes de l
knowledge of South Chile grassland functioning preclu<strong>de</strong>s us from i<strong>de</strong>ntifying which<br />
fraction of the total diversity is nee<strong>de</strong>d to saturate most of the processes present in this<br />
agroecosystem. Therefore, until the trophic relationships between the different species<br />
could be revealed, we advocate for a conservative approach to diversity loss.<br />
Our studies were not <strong>de</strong>signed to test hypotheses about specific functional groups or<br />
species, thus we can not i<strong>de</strong>ntify the mechanism(s) that explain(s) the observed <strong>de</strong>creased<br />
diversity. In spite of this, we raise concerns about continued use of these kind of<br />
insectici<strong>de</strong>s because several cases of natural regulation disruption have been recor<strong>de</strong>d in<br />
intensified agricultural systems much before explicit mechanisms that explain natural<br />
herbivore regulation had been revealed (Hardin et al., 1995). In fact, there are several well<br />
documented cases of release of herbivore insects from <strong>control</strong> after removing their natural<br />
enemies (Hills and Taylor, 1951; Kenmore et al., 1984) or non-target herbivores acting like<br />
alternative prey when the pest is scarce and contributing to support early season build-up of<br />
generalist natural enemies (Settle et al., 1996). In an oversimplified system like pastures,<br />
any additional biodiversity loss could exacerbate this process, reduce the system stability<br />
and increase the reliance on external inputs, especially insectici<strong>de</strong>s, to maintain its<br />
productivity.<br />
It remains a challenge to i<strong>de</strong>ntify the several roles that the different species play in the<br />
pasture. However, as it was mentioned above, negative effects on ecosystem processes with<br />
<strong>de</strong>clining biodiversity could be serious much before knowledge about explicit mechanisms<br />
could be gathered.<br />
Growers must be aware of how their pest practices may influence ecological processes<br />
before to make management <strong>de</strong>cisions. Inundative biological <strong>control</strong> of Dalaca pallens<br />
using Beauveria bassiana spores did not affect grassland diversity and its components<br />
(species richness and evenness), at least in the short term. Lambda-cyhalothrin, one of the<br />
most common insectici<strong>de</strong>s used for D. pallens <strong>control</strong>, affected all the community metrics<br />
(diversity, richness, evenness and dominance), with unknown consequences for the<br />
grassland agroecosystem. It was clear that the community-level impact of this broad-<br />
spectrum insectici<strong>de</strong> was far greater that any effect of Beauveria bassiana on arthropod<br />
community.<br />
114