Duncan Golicher
There is clearly growing awareness of the threats posed to ecosystems through human activity
Applied conservation may need to focus on the most threatened ecosystems.
Intuitively, “fragile” ecosystems are most at risk e.g Martorell and Peters (2009)
But what do we mean by a fragile ecosystem?
A good review of concepts is provided by Nilsson and Grelsson (1995)
Two main approaches to the concept of fragility.
The first approach is more difficult to use.
How do we really know exactly how an ecosystem might change naturally?
How well are the complex dynamics of an ecosystem truly understood?
The second approach is rather more intuitive. Think of changes that cause a potential shock.
Note that deliberate, planned land use change falls into a different category. This is habitat (or ecosystem) loss.
Pimm (1991) distinguished three forms of lack of fragility.
However stability (or fragility) is defined any measure of it must have a temporal component. In other words it must be based on measures taken at a minimum of two points in time.
Ecosystems may appear stable for centuries, but highly fragile in the short-term.
Coniferous forests can suddenly burn, then recover rather quickly..
Grasslands may be affected by sudden drought then green up, when the rains come back.
Flash floods may affect rivers, which then go back to more normal rates of flow.
Deserts may change quickly after unusual rains then dry up again leaving the same vegetation in place.
Hutchinson stated that ’lakes seem, on the scale of years or of human life spans, permanent features of landscapes, but they are geologically transitory, usually born of catastrophes, to mature and die quietly and imperceptibly
Ecosystems can appear fragile at small spatial scales may be stable at larger spatial scales.
The abundances of some species in an ecosystem may change but the relative abundance of higher taxonomic, morphological and functional groups may be stable.
Even if the abundances of species in an ecosystem fluctuates, the species composition (total species list) may remain constant over time.
(Owen-Smith 2019)
This could be thought of as having three dimensions (Wilson et al. 2005)
Exposure
Intensity
Impact
Exposure might be estimated either as the probability of a threatening process affecting an area over a specified time or the expected time until an area is affected. This is also often just called risk
Intensity could include measures of the magnitude, the frequency, and the duration of the risk. For biodiversity, the intensity of a threat can take many forms, including population sizes and fluctuations, amount of timber extracted per hectare of a forest type, density of an invasive plant species. Different exposures will have different intensities effects.
Impact is the direct effects of some threatening process on particular features. Impacts might be referred to as outcomes or specific risks.
Managers may be unaware of, or underestimate, the capacity of an ecosystem to rebound. I.e. Not take into account long term stability in terms of resistance, resilience and persistence. Management only focussed on risk may not be adaptive management.
Carpenter et al. (2015)
Chuvieco et al. (2014) The most vulnerable forests were found to be the rain forest of the Amazon Basin, Central Africa and Southeast Asia, the temperate forest of Europe, South America and north-east America, and the ecological corridors of Central America and Southeast Asia. The lowest vulnerability was observed in boreal regions, particularly those already affected by fires or having low biodiversity, agricultural regions of Australia, India, Latin America and Central Asia.
Tundra tends to be relatively stable.
For example. “Monitoring aimed at showing the fragility of an arctic tundra/goose grazing system concluded that the system was surprisingly stable”A limited effect of grazing on microbial respiration is consistent with a lack of significant differences in soil organic matter quantity and quality. The observed cycling was less than the natural variation within contrasting vegetation types" Strebel et al. (2010)
“Major factors that constrain tropical soil fertility and sustainable agriculture are low nutrient capital, moisture stress, erosion, high P fixation, high acidity with aluminium toxicity, and low soil biodiversity” (Cardoso and Kuyper 2006)
In the Mediterranean, the development of aquaculture along the coasts appears as a source of disturbance to the littoral ecosystems, and in particular to Posidonia oceanica seagrass meadows.(Cancemi, De Falco, and Pergent 2003)
Human disturbances impact vulnerable life history stages, reducing reproductive output and the supply of recruits essential for recovery;
Reefs can be vulnerable to the loss of few species, as niche specialization or temporal and spatial segregation makes each species unique
Many foundation species have similar sensitivity to disturbances, suggesting that entire functions can be lost to single disturbances;
Feedback loops and extinction vortices may stabilize degraded states or accelerate collapses even if stressors are removed. Mora, Graham, and Nystrom (2016)
Monitoring if Louisiana salt marsh vegetation showed both fragility and resilience after contamination by oil from the deep water horizon disaster. Silliman et al. (2012)
Rapid salt-marsh vegetation recovery (high resiience)
But also also permanent marsh area loss (low resistance)
Thresholds of oil coverage associated with severity of salt-marsh damage, with heavy oiling leading to plant mortality
Plant death on the edges of marshes more than doubled rates of shoreline erosion.
Hallmann et al. (2017) estimate more than 75 percent decline over 27 years in total flying insect biomass in protected areas
Fragility is easy to say but difficult to define in practice
Each ecosystem varies in properties
No simple solutions when ecosystems are being managed
Both space and time are needed to prevent breakdowns