Seagrass restoration is possible: insights and lessons from Australia and New Zealand

Seagrasses are important marine ecosystems situated throughout the world's coastlines. They are facing declines around the world due to global and local threats such as rising ocean temperatures, coastal development and pollution from sewage outfalls and agriculture. Efforts have been made to reduce seagrass loss through reducing local and regional stressors, and through active restoration. Seagrass restoration is a rapidly maturing discipline, but improved restoration practices are needed to enhance the success of future programs. Major gaps in knowledge remain, however, prior research efforts have provided valuable insights into factors influencing the outcomes of restoration and there are now several examples of successful large-scale restoration programs. A variety of tools and techniques have recently been developed that will improve the efficiency, cost effectiveness, and scalability of restoration programs. This review describes several restoration successes in Australia and New Zealand, with a focus on emerging techniques for restoration, key considerations for future programs, and highlights the benefits of increased collaboration, Traditional Owner (First Nation) and stakeholder engagement. Combined, these lessons and emerging approaches show that seagrass restoration is possible, and efforts should be directed at upscaling seagrass restoration into the future. This is critical for the future conservation of this important ecosystem and the ecological and coastal communities they support

Seagrass restoration is possible:Insights and lessons from Australia and New Zealand

Seagrasses are important marine ecosystems situated throughout the world’s coastlines. They are facing declines around the world due to global and local threats such as rising ocean temperatures, coastal development and pollution from sewage outfalls and agriculture. Efforts have been made to reduce seagrass loss through reducing local and regional stressors, and through active restoration. Seagrass restoration is a rapidly maturing discipline, but improved restoration practices are needed to enhance the success of future programs. Major gaps in knowledge remain, however, prior research efforts have provided valuable insights into factors influencing the outcomes of restoration and there are now several examples of successful large-scale restoration programs. A variety of tools and techniques have recently been developed that will improve the efficiency, cost effectiveness, and scalability of restoration programs. This review describes several restoration successes in Australia and New Zealand, with a focus on emerging techniques for restoration, key considerations for future programs, and highlights the benefits of increased collaboration, Traditional Owner (First Nation) and stakeholder engagement. Combined, these lessons and emerging approaches show that seagrass restoration is possible, and efforts should be directed at upscaling seagrass restoration into the future. This is critical for the future conservation of this important ecosystem and the ecological and coastal communities they support

Effects of Charge State and Cationizing Agent on the Electron Capture Dissociation of a Peptide

Electron capture dissociation (ECD) is a promising method for de novo sequencing proteins and peptides and for locating the positions of labile posttranslational modifications and binding sites of noncovalently bound species. We report the ECD of a synthetic peptide containing 10 alanine residues and 6 lysine residues uniformly distributed across the sequence. ECD of the (M + 2H) 2+ produces a limited range of c (c 7 -c 15 ) and z (z 9 -z 15 ) fragment ions, but ECD of higher charge states produces a wider range of c (c 2 -c 15 ) and z (z 2 -z 6 , z 9 -z 15 ) ions. Although mass spectrometry (MS) and tandem mass spectrometry (MS/MS) have been used to characterize peptides for more than three decades, 1,2 the developments of electrospray ionization (ESI) 3 and matrix-assisted laser desorption/ionization 4 have dramatically expanded the size and type of molecules amenable to characterization by MS/MS. For example, ESI has been used to form intact gas-phase ions from virus particles (4.0 × 10 7 Da) 5 and DNA molecules as large as 1.2 × 10 8 Da. 6 ESI-MS and ESI-MS/MS experiments can be performed using as little as 10 -18 mol of sample. 7 For these measurements, Fourier transform (FT) MS has the advantages of ultrahigh resolution, multichannel detection, and MS n capabilities. 8,9 Dissociation methods in FTMS, including collisionally activated dissociation (CAD), 10 surface-induced dissociation, 11,12 infrared multiphoton dissociation, 13 and blackbody infrared radiative dissociation, 14,15 have been used to obtain sequence information and locations of posttranslational modifications (PTMs) in biomolecules. With these activation methods, the most labile bonds within an ion are typically cleaved. This often produces incomplete sequence coverage, the loss of PTMs, and a lack of backbone cleavages within regions enclosed by disulfide bridges. The recently developed method of electron capture dissociation (ECD), [16][17][18][19][20][21][22][23][24][25

NACA Technical Notes

Report presenting an investigation to determine the effects of some of the basic parameters on the thrust of a simple downward-directed jet beneath a flat plate in a static-thrust facility. Some of the variables investigated included the size and shape of the flat plate, aspect ratio of the plate, distance of the flat plate and nozzle exit above the ground, and surface conditions of the ground

NACA Technical Notes

Report of an investigation in a static-test facility to determine some of the effects of propeller position and overlap on the slipstream deflection characteristics of a configuration equipped with a sliding and Fowler flap. An investigation of a leading-edge slat, nacelle size, flap segmentation, and number of propellers was also conducted. Results regarding the effect of number of propellers, effect of vertical position of propeller, effect of extending nacelles through flaps, effect of chordwise position of the propellers, effect of propeller overlap, effect of position and deflection of a leading-edge slat, propeller static-thrust efficiency in ground effect, and effect of nacelle size are provided