Abstract:1. The relationship between biodiversity and ecosystem functioning is typically positive but saturating, suggesting widespread functional redundancy within ecological communities. However, theory predicts that apparent redundancy can be reduced or removed when systems are perturbed, or when multifunctionality (the simultaneous delivery of multiple functions) is considered.2. We used manipulative experiments to test whether higher levels of dung beetle species richness enhanced individual functions and multifun… Show more
“…Some important factors influencing the rate of dung removal could be recognized, although the highest explanatory capacities corresponded to the combined effects of several types of variables, where the three types of variables exercise a joint and indivisible effect on dung removal (fastest under summer conditions with high temperatures and assemblages with a high biomass). In experimental as well as field studies, dung beetle diversity is identified as a key factor in explaining ecological functions, such as dung removal or soil perturbation (Rosenlew & Roslin, ; Beynon et al., ; Braga et al., ; Manning et al., ). In our study, the main predictor was the total volume, represented by dung beetles collected in the traps in which dung removal was measured (TIE traps).…”
Section: Discussionmentioning
confidence: 99%
“…Most literature about dung beetle removal is focused on experimental or mesocosmos designs. Several studies have estimated dung removal efficiency and other ecological functions according to the (low) number, identity, and functional characteristics of selected species (Horgan, ; Finn & Giller, ; Slade et al., ; Rosenlew & Roslin, ; Nervo et al., , ; Tixier et al., ; Yoshihara & Sato, ; Manning et al., ). However, aside the importance of dung removal to understand nutrient cycling and ecosystem functioning, not many studies have directly estimated dung removal in field samples (Holter, ; Lee & Wall, ), and only few have done this under neotropical forest conditions (Herrick & Lal, ; Andresen, ; Amézquita & Favila, ; Braga et al., ; Batilani‐Filho & Hernández, ).…”
Dung consumption and removal is a fundamental ecological process carried out by dung beetles that drive soil nutrient cycling and associated ecosystem services. In this study, the removal rate of small droppings by dung beetles was estimated in natural subtropical rainforests of southern Brazil located along an elevational gradient, in order to understand the factors influencing variation in dung removal. To do that, the comparative explanatory capacity of three main types of variables was quantified: assemblage characteristics, local climatic and habitat conditions, and seasonal variation. The complete disappearance of dung within 48 h after deposition occurs in 73% of occasions. The highest explanatory capacity correspond to the combined effects of the three types of variables; however, average air temperature during the sampling period, total volume of dung beetles collected in the traps in which dung removal was measured, and the seasonal transition from summer to winter were the most important and representative predictors of dung removal. Thus, the dung nutrient incorporation into the soil will most likely be greater during spring‐summer conditions, when the air temperature at the time of dung deposition is high and the biomass of the dung beetle assemblage is bigger.
“…Some important factors influencing the rate of dung removal could be recognized, although the highest explanatory capacities corresponded to the combined effects of several types of variables, where the three types of variables exercise a joint and indivisible effect on dung removal (fastest under summer conditions with high temperatures and assemblages with a high biomass). In experimental as well as field studies, dung beetle diversity is identified as a key factor in explaining ecological functions, such as dung removal or soil perturbation (Rosenlew & Roslin, ; Beynon et al., ; Braga et al., ; Manning et al., ). In our study, the main predictor was the total volume, represented by dung beetles collected in the traps in which dung removal was measured (TIE traps).…”
Section: Discussionmentioning
confidence: 99%
“…Most literature about dung beetle removal is focused on experimental or mesocosmos designs. Several studies have estimated dung removal efficiency and other ecological functions according to the (low) number, identity, and functional characteristics of selected species (Horgan, ; Finn & Giller, ; Slade et al., ; Rosenlew & Roslin, ; Nervo et al., , ; Tixier et al., ; Yoshihara & Sato, ; Manning et al., ). However, aside the importance of dung removal to understand nutrient cycling and ecosystem functioning, not many studies have directly estimated dung removal in field samples (Holter, ; Lee & Wall, ), and only few have done this under neotropical forest conditions (Herrick & Lal, ; Andresen, ; Amézquita & Favila, ; Braga et al., ; Batilani‐Filho & Hernández, ).…”
Dung consumption and removal is a fundamental ecological process carried out by dung beetles that drive soil nutrient cycling and associated ecosystem services. In this study, the removal rate of small droppings by dung beetles was estimated in natural subtropical rainforests of southern Brazil located along an elevational gradient, in order to understand the factors influencing variation in dung removal. To do that, the comparative explanatory capacity of three main types of variables was quantified: assemblage characteristics, local climatic and habitat conditions, and seasonal variation. The complete disappearance of dung within 48 h after deposition occurs in 73% of occasions. The highest explanatory capacity correspond to the combined effects of the three types of variables; however, average air temperature during the sampling period, total volume of dung beetles collected in the traps in which dung removal was measured, and the seasonal transition from summer to winter were the most important and representative predictors of dung removal. Thus, the dung nutrient incorporation into the soil will most likely be greater during spring‐summer conditions, when the air temperature at the time of dung deposition is high and the biomass of the dung beetle assemblage is bigger.
“…Although limited in factors such as scale/replication, time frame, geographic range and dung beetle species, our results add to the literature showing that there are important ecosystem service benefits from dung beetles (e.g. Slade et al ., ; Beynon et al ., ; Manning et al ., ; Manning et al ., ; Piccini et al ., ). These findings are relevant both to agricultural systems where native dung beetle faunas are at risk from intensification of agriculture (Hutton & Giller, ) or systems where there are naturally impoverished dung beetle faunas, with active release programmes aiming to increase species richness (Edwards, ; Forgie et al ., ).…”
Section: Discussionmentioning
confidence: 99%
“…If an entire country has a naturally impoverished pastoral dung beetle fauna, then many species of dung beetle may require to be introduced to achieve improvements in ecosystem services over seasons and in pastures that will vary in factors such as farming types, soils, or climates (Tyndale-Biscoe, 1994;Edwards, 2009). Furthermore, evidence suggests that more diverse dung beetle communities can provide better benefits to ecosystem services than comparatively species-poor communities, but that species composition effects can be complex and warrant further study (Slade et al, 2007;Beynon et al, 2015;Manning et al, 2016;Manning et al, 2017;Piccini et al, 2017;Slade et al, 2017).…”
1. Whether the release of non‐native insect species benefits or harms ecosystem services has been the subject of debate. In New Zealand, the release of new non‐native dung beetle species was intended to enhance ecosystem services but concerns were raised over possible negative effects.
2. Field cage trials used three newly released dung beetle species to investigate two concerns: that soil disturbance from dung beetle activity increases soil losses in runoff after rainfall; and that dung burial increases survival of infective parasitic nematodes on pasture.
3. Three treatments – dung + beetles, dung‐only, and controls (without dung or beetles) – were applied on each of three soil types with different permeability: sandy loam, clay loam, and compacted clay.
4. Dung beetle activity resulted in significant reductions of 49% and 81% in mean surface runoff volume, depending on simulated rainfall intensity. Amounts of sediment in the runoff did not change under an extreme rainfall simulation, but in a less extreme rainfall simulation the presence of dung beetles resulted in a 97% reduction in mean sediment amount in runoff.
5. The numbers of infective third‐stage nematode larvae recovered from foliage varied considerably between soil types and through time; however, dung beetle activity reduced overall mean nematode numbers on grass around the dung pats by 71%.
6. This study adds to global evidence that dung beetles can improve agricultural ecosystem services by providing data on services that have rarely been investigated: reduced runoff/soil losses through increased soil porosity, and reductions in parasitic nematodes.
“…A relatively small sample size, and variability in remaining dung mass (likely caused by the colonization of soil fauna) meant that we could not make any meaningful post-hoc corrections for differences in dung quality. More precise estimates of dung removal, including use of dry mass (Manning et al , 2017), or loss-on-ignition (Menéndez et al , 2016), would permit better tests of whether dung decomposition is impaired by anthelmintic residues, but either approach is destructive and would not allow us to make long-term estimates. Despite variability in initial dung conditions, we found that dung was fully degraded the following spring, regardless of the addition of beetles or the presence of moxidectin residues.…”
10 11 1. Macrocyclic lactones (MLs) are a class of chemical compounds administered to 12 livestock for parasite control. These compounds are poorly metabolized and are 13 predominately excreted in dung. 14 152. When coprophagous insects such as dung beetles (Coleoptera: Scarabaeoidea) are 16 exposed to ML residues, lethal and sublethal effects are often observed. Indirectly 17 this can lead to ML residues impairing ecosystem functions that underpin production.
18A strategy to reduce these negative effects involves selecting compounds that offer 19 lower risk to non-target invertebrates such as the ML moxidectin. 20 21 3. Considering two dung beetle species with differing sensitivities to agricultural 22 intensification, we asked whether exposure to moxidectin residues influenced 23 survival, reproductive output, and functioning (short-and long-term estimates of dung 24 removal).25 26 4. When exposed to moxidectin, adults of the sensitive species (Geotrupes spiniger 27 Marsham) experienced a 43% reduction in survival. In contrast, survival of the non-28 sensitive species (Aphodius rufipes L.) was unaffected. We were unable to determine 29 whether exposure affected reproductive output of either species.30 31 5. We found little evidence to suggest moxidectin impaired dung removal. We found 32 however, that high densities of a species with relatively low functional importance (A.33 rufipes) can compensate for the loss of a functionally dominant species (G. spiniger). 34 Over a longer timeframe, earthworms fully decomposed dung irrespective of 35 moxidectin residues.36
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