Ecology. Michael Begon
href="#fb3_img_img_072b1e84-3b50-5785-aa5d-26cb2bb168de.gif" alt="Schematic illustration of a phylogenetic split bisecting insect and bird biotas into northern and southern assemblages in New Zealand. (a, b) Glaciation of the alpine region of the South Island of New Zealand which is hypothesised to be responsible for fracturing the ancestral biota into north and south lineages that have subsequently diverged. Green shading represents lowlands. (c–f) North–south phylogeographic breaks for alpine birds and insects with dendrograms showing phylogenetic relationships and approximate divergence times."/>
Figure 1.20 A phylogenetic split bisecting insect and bird biotas into northern and southern assemblages in New Zealand. (a, b) Glaciation of the alpine region of the South Island of New Zealand which is hypothesised to be responsible for fracturing the ancestral biota into north and south lineages that have subsequently diverged. Green shading represents lowlands. (c–f) North–south phylogeographic breaks for alpine birds and insects with dendrograms showing phylogenetic relationships and approximate divergence times. Sampling sites are shown as circles, the shading shows approximate taxon ranges, and the dotted square represents a particularly highly glaciated narrow alpine neck.
Source: After Wallis et al. (2016).
APPLICATION 1.5 Human history and species invasions
In this section on the role of history in the determination of species distributions, it would be misleading only to consider 'natural' historical factors. Human history has had equally profound effects on the distribution of species around the globe. The world has shrunk as travel has boomed and, just like us, animals, plants and microorganisms have become globetrotters, introduced to new locations on purpose or as accidental tourists.
Only about 10% of invaders become established, and of these, about 10% spread and have significant, sometimes disastrous, consequences (Townsend, 2008). The introduction in the 1950s of Nile perch (Lates niloticus) to establish a commercial fishery in Lake Victoria in East Africa, for example, is held responsible for the extinction or near‐extinction of several hundred native fish species. An equally striking plant example is provided by the neotropical Parthenium weed (Parthenium hysterophorus) that has invaded large areas of a number of continents (Figure 1.21), generally by accident, and is responsible for the degradation of grasslands and of many cropping and livestock systems. Its success as an invader can be attributed to tolerance of a wide range of physicochemical conditions, escape from natural predators in non‐native regions, high competitiveness against other plants (including the release of allelopathic chemicals into the soil) and high genetic diversity, among other factors (Bajwa et al., 2016). Finally, prominent among imported human disease organisms are HIV, influenza and zika viruses.
Figure 1.21 The invasion of Parthenium weed. This weed is invasive in the countries shaded or circled in red. Blue‐shaded countries represent populations of the weed that may be establishing in Europe. Countries shaded green are considered to be within its invasive range.
Source: From Bajwa et al. (2016).
homogenisation of the biota
A profound consequence of global transport and past colonialism has been homogenisation of the biota. The same set of human camp followers now occur in widely separated regions – house sparrows, cockroaches, rats and mice, salmonid fish and game animals, domestic animals and crop plants (with their associated pests and diseases) (Townsend, 2008). Because native species often fare badly in the face of this onslaught, many parts of North America and the southern hemisphere now reflect a European legacy more closely than their native heritage. A graphic example of biotic homogenisation is provided at both ends of the trade link between the Great Lakes of North America and the Baltic Sea. Often spread in the ballast water of ships moving along this route, a third of the 170 species of invasive fish, molluscs and crustaceans in the Great Lakes are from the Baltic, and a third of the 100 invaders in the Baltic Sea come from the Great Lakes. Furthermore, enhanced shipping promoted by recent expansions of the Suez and Panama Canals can be expected to escalate marine invasions at regional and continental scales, while increases in internet‐based trade in pets and other exotic organisms is providing novel pathways that will be difficult to regulate (Ricciardi et al., 2017). We take this case up again in Section 6.6.2.
economic consequences of invasions
Invaders can have far‐reaching economic as well as ecological consequences. Table 1.1 categorises the tens of thousands of exotic invaders in the USA into taxonomic groupings and lists these in order of their estimated annual costs (in terms of economic damage done and costs of control). Overall, pests of crop plants, including weeds, insects and pathogens are the most expensive, with rats some way behind but responsible for the destruction of stored grains, starting fires by gnawing through electrical wires, polluting foodstuffs, spreading diseases and preying on native animals. Imported human disease organisms are also very expensive to treat and result in 40 000 deaths per year. Ecological knowledge is needed to predict future invasions that are likely to have damaging consequences so that the invaders can be confronted, particularly via biosecurity at national borders. Despite their obvious deleterious effects, the importance of biological invasions seems not to be well understood by the public or fully accepted by decision makers (Courchamp et al., 2017). Ecologists have much to contribute in this arena.
Table 1.1 Estimated annual costs (billions of US dollars) associated with damage caused and management costs of invaders in the USA. Taxonomic groupings are ordered in terms of the total costs associated with them. Source: After Pimentel et al. (2000).
| Type of organism | Number of invaders | Major culprits | Loss and damage | Control costs | Total costs |
|---|---|---|---|---|---|
| Microbes (pathogens) | >20 000 | Crop pathogens | 32.1 | 9.1 | 41.2 |
| Mammals | 20 | Rats and cats | 37.2 | Na | 37.2 |
| Plants | 5 000 | Crop weeds | 24.4 | 9.7 | 34.1 |
| Arthropods | 4 500 | Crop pests | 17.6 | 2.4 | 20.0 |
| Birds | 97 | Pigeons | 1.9 | NA | 1.9 |
| Molluscs | 88 | Asian clams, zebra mussels |
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