The best instream structure for a particular location will depend on the purpose of the structure and the local conditions.
Order of preference for road crossing design
An instream structure should:
The diagram above shows the order of preference for road crossing design, based on the degree of connectivity each design facilitates.
See section 4 of the New Zealand Fish Passage Guidelines for design guidance on new and replacement instream structures.
A process to guide the design and construction of new structures in streams is set out below.
See section 3 and 4 of the New Zealand Fish Passage Guidelines.
Culverts are commonly used to allow a stream to flow under a road or other structure. In most locations they can be designed, installed and maintained to provide for fish passage. Culverts must not impede fish passage unless an exemption has been approved by DOC.
There are three general approaches for accommodating fish passage in culverts.
See section 4.5 of the New Zealand Fish Passage Guidelines.
Weirs are used for a variety of purposes, such as managing water intakes and gauging flows, but they often impede the movement of fish. Where possible, weirs should be built as full river width with a natural rock-ramp fishway, instead of a conventional solid weir structure.
If it is not practical to build a rock-ramp fishway, a V-shaped broad crested weir with a baffled surface or a weir with a bypass channel should be considered.
Good design principles include:
Design features to avoid:
See section 4.7 of the New Zealand Fish Passage Guidelines.
Fords are the least preferred type of river or stream modification because they often hinder or block fish passage. Fords combine many of the negative aspects of culverts and weirs (like fast-flowing, shallow water, a sharp crest and a steep downstream face). Fords also modify the stream bed and allow vehicles and animals to enter a waterway.
It is best practice to avoid using fords for stream crossings if possible. But if a ford is the only viable option, it should be designed with features that allow fish to pass. These include ensuring a continuous pathway for fish passage is maintained across the structure at all flows.
Causeway ford designs that incorporate culverts are the minimum standard for fords – these should follow the guidance for culvert design. A ford must not impede fish passage unless an exemption has been approved by DOC.
See section 4.6 of the New Zealand Fish Passage Guidelines.
Flood gates and tide gates are used to control fluctuations in water flow during floods and tides. All tide and flood gates are considered barriers to fish passage. They can significantly disrupt movements of freshwater fish and invertebrates as well as the habitats upstream.
The characteristics of tide and flood gates that present problems for the movement of fish include:
When flood or tide gates are required, best practice is to install automated active gates that close only when the water level reaches a critical height. If operational constraints mean that the use of automated gate systems is not possible, the minimum standard is to install self-regulating ‘fish friendly’ gates. These gates should be kept open as far as possible for as long as possible (usually with a designed stiffener), particularly on the incoming tide as this is when most juvenile fish are moving upstream.
As well as improving fish passage, fish friendly gates allow better water movement up and downstream, and help to reduce the impacts on habitats (like salt marshes) upstream of the gate.
See section 4.8 of the New Zealand Fish Passage Guidelines.
A pump station is a site that hosts one or more motorised pumps that push water over or through a stop bank to prevent land from flooding.
A range of fish friendly pumps are available that can provide fish passage.
See section 4.9 of the New Zealand Fish Passage Guidelines and Improving fish passage at pump stations (PDF, 543K) for advice.
Stormwater management ponds/wetlands are designed to reduce downstream flooding and erosion in urban and other highly modified catchments.
When creating new stormwater management systems, the recommended best practice is to:
In general, fish should be excluded from these systems due to poor habitat quality.
See section 4.10 of the New Zealand Fish Passage Guidelines.
Water intakes located within waterways that support freshwater fish need to be designed to prevent impingement and/or entrainment of fish. All new dams or diversion structures need to apply to DOC to determine if a fish facility is required.
Good design should consider a whole of intake design approach including:
If all criteria can not be met then consideration should be given to further strengthen some criteria over others.
See fish screen design for water intakes resources for more guidance.
Dams include any type of barrier that crosses a river or stream channel with the function of impounding or diverting water. These structures obstruct the natural free flow of water, the natural passage of fish, sediment, and other essential nutrients in river system. All new dams or diversion structures need to apply to DOC to determine if a fish facility is required.
See section 7 of the New Zealand Fish Passage Guidelines for guidance on how to provide upstream and downstream passage at dams greater than 4 m high.
Monitoring is the only way to understand how well a structure is working and ensure that any reduction in fish passage is not harming upstream or downstream communities. Monitoring is especially important when:
See Chapter 8 of the New Zealand Fish Passage Guidelines or Fish Passage Monitoring Manual for more information about monitoring techniques and methods for evaluating the success of fish passage in different circumstances. The fish passage assessment tool can also be used to monitor the structure and the risk to fish passage.