4  Deployment

Once the Mini Buoy has been assembled and the accelerometer is active, it is ready deployed at the survey location.

4.1 Installing the Mini Buoy

Mini Buoys can be used in single deployments to assess inundation characteristics at a given location, used in comparative deployments such as when comparing conditions between restoration and reference ‘natural’ sites, or used in multi-deployments to gather detailed hydrodynamic information.

Deployments should last more than 15 days to cover spring and neap tide variability. When deploying the Mini Buoy in the field, it is important to consider characteristics of the site and duration of the deployment. High-energy locations may be subject to excessive scouring that stress the Mini Buoy tether and may dislodge the anchor. At low-energy locations excessive sedimentation can bury the Mini Buoy. Using a cable tie to attach the Mini Buoy tether to an anchor buried > 0.5 m into the ground is recommended for a standard set-up. Gather the following equipment:

  • Large cable tie
  • 0.7 m length of metal rod with perforations

To install the Mini Buoy:

  1. Hammer the metal rod into the ground until 1 cm is protruding from the surface
  2. Attach the end of the fishing line chain to the anchor using the cable tie
  3. Move the Mini Buoy 360° around the anchor, and remove any obstructing objects

4.2 Survey design

Indicators selected for monitoring and reporting undertaken within the project site should be measured against a reference or control area in order to gauge progress towards the desired restored ecological state, and/or away from the undesired unrestored state. The before-after control-impact (BACI) monitoring framework107 is a simple study design which enables you to assess the overall benefits resulting from the project and to evaluate restoration sites against natural reference sites.

The net difference the project makes is calculated by assessing indicators between control (typically healthy, unimpacted reference sites where no restoration activities take place) and intervention sites (where restoration occurs). Using a BACI approach, assessments of indicators are done both before (often called the baseline condition) and after activities have taken place (Figure 17). This enables an evaluation of whether detected changes can be attributed to the intervention (restoration) activities or are due to natural processes that are occurring over the whole landscape (e.g., the impact of floods or other climate events) or to external human disturbances.

Schematic of BACI project design for carbon projects adapted from Poortinga et al. (2018).107