Effect of phorbol esters on Ca2+ sensitivity and myosin light-chain phosphorylation in airway smooth muscle

We studied in -escin-permeabilized canine tracheal smoothmuscle (CTSM) the effect of the protein kinase C (PKC) agonist phorbol12,13-dibutyrate (PDBu) on isometric force at a constant submaximalCa²⁺ concentration (i.e., theeffect on Ca²⁺ sensitivity) andregulatory myosin light-chain (rMLC) phosphorylation. PDBuincreased Ca²⁺sensitivity, an increase associated with a concentration-dependent, sustained increase in rMLC phosphorylation. PDBu altered therelationship between rMLC phosphorylation and isometric force such thatthe increase in isometric force was less than that expected for the increase in rMLC phosphorylation observed. The effect of four PKCinhibitors [calphostin C, chelerythrine chloride, apseudosubstrate inhibitor for PKC, PKC peptide-(1931) (PSSI), andstaurosporine] on PDBu-inducedCa²⁺ sensitization as well as theeffect of calphostin C and PSSI on rMLC phosphorylation weredetermined. Whereas none of these compounds prevented or reversed thePDBu-induced increase in Ca²⁺sensitivity, the PDBu-induced increase in rMLC phosphorylation wasinhibited. We conclude that PDBu increases rMLC phosphorylation byactivation of PKC but that the associated PDBu-induced increases inCa²⁺ sensitivity are mediated bymechanisms other than activation of PKC in permeabilized airway smoothmuscle.

     

The global decline of freshwater megafauna

Freshwater ecosystems are among the most diverse and dynamic ecosystems on Earth. At the same time, they are among the most threatened ecosystems but remain underrepresented in biodiversity research and conservation efforts. The rate of decline of vertebrate populations is much higher in freshwaters than in terrestrial or marine realms. Freshwater megafauna (i.e., freshwater animals that can reach a body mass ≥30 kg) are intrinsically prone to extinction due to their large body size, complex habitat requirements and slow life‐history strategies such as long life span and late maturity. However, population trends and distribution changes of freshwater megafauna, at continental or global scales, remain unclear. In the present study, we compiled population data of 126 freshwater megafauna species globally from the Living Planet Database and available literature, and distribution data of 44 species inhabiting Europe and the United States from literature and databases of the International Union for Conservation of Nature and NatureServe. We quantified changes in population abundance and distribution range of freshwater megafauna species. Globally, freshwater megafauna populations declined by 88% from 1970 to 2012, with the highest declines in the Indomalaya and Palearctic realms (?99% and ?97%, respectively). Among taxonomic groups, mega‐fishes exhibited the greatest global decline (?94%). In addition, freshwater megafauna experienced major range contractions. For example, distribution ranges of 42% of all freshwater megafauna species in Europe contracted by more than 40% of historical areas. We highlight the various sources of uncertainty in tracking changes in populations and distributions of freshwater megafauna, such as the lack of monitoring data and taxonomic and spatial biases. The detected trends emphasize the critical plight of freshwater megafauna globally and highlight the broader need for concerted, targeted and timely conservation of freshwater biodiversity.     

Freshwater megafauna diversity: Patterns,status and threats

Aim

Freshwater megafauna remain underrepresented in research and conservation, despite a disproportionately high risk of extinction due to multiple human threats. Therefore, our aims are threefold; (i) identify global patterns of freshwater megafauna richness and endemism, (ii) assess the conservation status of freshwater megafauna and (iii) demonstrate spatial and temporal patterns of human pressure throughout their distribution ranges.

Location

Global.

Methods

We identified 207 extant freshwater megafauna species, based on a 30 kg weight threshold, and mapped their distributions using HydroBASINS subcatchments (level 8). Information on conservation status and population trends for each species was extracted from the IUCN Red List website. We investigated human impacts on freshwater megafauna in space and time by examining spatial congruence between their distributions and human pressures, described by the Incident Biodiversity Threat Index and Temporal Human Pressure Index.

Results

Freshwater megafauna occur in 76% of the world’s main river basins (level 3 HydroBASINS), with species richness peaking in the Amazon, Congo, Orinoco, Mekong and Ganges‐Brahmaputra basins. Freshwater megafauna are more threatened than their smaller counterparts within the specific taxonomic groups (i.e., fishes, mammals, reptiles and amphibians). Out of the 93 freshwater megafauna species with known population trends, 71% are in decline. Meanwhile, IUCN Red List assessments reported insufficient or outdated data for 43% of all freshwater megafauna species. Since the early 1990s, human pressure has increased throughout 63% of their distribution ranges, with particularly intense impacts occurring in the Mekong and Ganges‐Brahmaputra basins.

Main conclusions

Freshwater megafauna species are threatened globally, with intense and increasing human pressures occurring in many of their biodiversity hotspots. We call for research and conservation actions for freshwater megafauna, as they are highly sensitive to present and future pressures including a massive boom in hydropower dam construction in their biodiversity hotspots.