Article

Earthquake-induced habitat migration in a riparian spawning fish has implications for conservation management

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Abstract

• Galaxias maculatus is a riparian spawning fish that supports an important recreational fishery in New Zealand, with spawning habitat requirements strongly structured by salinity gradients at river mouths. This study reports changes to the spawning habitat following a series of large earthquakes that resulted in the widespread deformation of ground surfaces in the vicinity of waterways. • Assessments of habitat recovery focused on two river systems, the Avon and Heathcote, with pre‐disturbance data available over a 20‐year period. Recovery dynamics were assessed by field survey and mapping of spawning habitat prior to and on seven occasions after the disturbance event. Riparian land‐use and management patterns were mapped and analysed using overlay methods in a geographical information system (GIS). • Habitat migration of up to 2 km occurred in comparison with all previous records, and several anthropogenic land uses have become threats because of changed patterns of co‐occurrence. Incompatible activities now affect more than half of the spawning habitat in both rivers, particularly in areas managed for flood control purposes and recreational use. • The results are an example of landscape‐scale responses to salinity and water‐level changes driven by tectonic dynamics. These dynamics are not the source of the stress per se; rather, they have increased the exposure of the species to pre‐existing stressors. • The case illustrates important principles for managing subtle, yet widespread, change. Adaptive conservation methods and investments in information are priorities for avoiding management failure following environmental change.

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... six months before migrating back into fresh water to mature into adults (McDowall & Eldon 1980). These characteristics have pronounced implications for conservation around the need to ensure connectivity between life stages and their associated the habitat requirement, which are susceptible to changes over time (McDowall 1992(McDowall , 1999Orchard et al. 2018b).. ...
... The reduction of lowland aquatic habitat through historical drainage (Ausseil et al. 2008;Larned et al. 2018), has undoubtedly contributed to īnanga decline. Īnanga are also reliant on riparian habitat for spawning (Benzie 1968), and this contributes to their vulnerability to land-use change (Hickford et al. 2010;Hickford & Schiel 2011;Orchard et al. 2018b). Important considerations for the recovery of īnanga populations in the contemporary environment include the condition and accessibility of instream habitat for adult fish, and the protection of spawning grounds as critical habitat for this particular life stage. ...
... Many of the known spawning sites are located close to the upstream limit of salt water in lowland tidal waterways (Burnet 1965;Taylor 2002). Recent research has found that spawning may occur over a relatively large salinity range (Orchard et al. 2018b). In some rivers this increases the size of the area that requires protection for spawning (Orchard & Hickford 2020), and is also reflected in the spatio-temporal dynamics of spawning locations which may 'move around' within a rivermouth system. ...
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Technical Report
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... For a large part of their development period this places the eggs in a terrestrial environment where they are vulnerable to a variety of anthropogenic threats (McDowall & Charteris 2006). Examples include disturbance effects associated with mowing, grazing and trampling, flood management activities such as vegetation clearance and dredging, and the construction of retaining walls and other engineering works (Hickford & Schiel 2011;Orchard et al. 2018a). ...
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Seismic shaking and tectonic deformation during strong earthquakes can trigger widespread environmental effects. The severity and extent of a given effect relates to the characteristics of the causative earthquake and the intrinsic properties of the affected media. Documentation of earthquake environmental effects in well-instrumented, historical earthquakes can enable seismologic triggering thresholds to be estimated across a spectrum of geologic, topographic and hydrologic site conditions, and implemented into seismic hazard assessments, geotechnical engineering designs, paleoseismic interpretations, and forecasts of the impacts of future earthquakes. The 2010-2011 Canterbury earthquake sequence (CES), including the moment magnitude (Mw) 7.1 Darfield earthquake and Mw 6.2, 6.0, 5.9, and 5.8 aftershocks, occurred on a suite of previously unidentified, primarily blind, active faults in the eastern South Island of New Zealand. The CES is one of Earth’s best recorded historical earthquake sequences. The location of the CES proximal to and beneath a major urban centre enabled rapid and detailed collection of vast amounts of field, geospatial, geotechnical, hydrologic, biologic, and seismologic data, and allowed incremental and cumulative environmental responses to seismic forcing to be documented throughout a protracted earthquake sequence. The CES caused multiple instances of tectonic surface deformation (≥ 3 events), surface manifestations of liquefaction (≥ 11 events), lateral spreading (≥ 6 events), rockfall (≥ 6 events), cliff collapse (≥ 3 events), subsidence (≥ 4 events), and hydrological (10s of events) and biological shifts (≥ 3 events). The terrestrial area affected by strong shaking (e.g. peak ground acceleration (PGA) ≥ 0.1-0.3 g), and the maximum distances between earthquake rupture and environmental response (Rrup), both generally increased with increased earthquake Mw, but were also influenced by earthquake location and source characteristics. However, the severity of a given environmental response at any given site related predominantly to ground shaking characteristics (PGA, peak ground velocities) and site conditions (water table depth, soil type, geomorphic and topographic setting) rather than earthquake Mw. In most cases, the most severe liquefaction, rockfall, cliff collapse, subsidence, flooding, tree damage, and biologic habitat changes were triggered by proximal, moderate magnitude (Mw ≤ 6.2) earthquakes on blind faults. CES environmental effects will be incompletely preserved in the geologic record and variably diagnostic of spatial and temporal earthquake clustering. Liquefaction feeder dikes in areas of severe and recurrent liquefaction will provide the best preserved and potentially most diagnostic CES features. Rockfall talus deposits and boulders will be well preserved and potentially diagnostic of the strong intensity of CES shaking, but challenging to decipher in terms of single versus multiple events. Most other phenomena will be transient (e.g., distal groundwater responses), not uniquely diagnostic of earthquakes (e.g., flooding), or more ambiguous (e.g. biologic changes). Preliminary paleoseismic investigations in the CES region indicate recurrence of liquefaction in susceptible sediments of ~ 100 to 300 yr, recurrence of severe rockfall event(s) of ca. 6,000 to 8,000 yr, and recurrence of surface rupturing on the largest CES source fault of ca. 20,000 to 30,000 yr. These data highlight the importance of utilizing multiple proxy datasets in paleoearthquake studies. The severity of environmental effects triggered during the strongest CES earthquakes was as great as or equivalent to any historic or prehistoric effects recorded in the geologic record. We suggest that the shaking caused by rupture of local blind faults in the CES comprised a ‘worst case’ seismic shaking scenario for parts of the Christchurch urban area. Moderate Mw blind fault earthquakes may contribute the highest proportion of seismic hazard, be the most important drivers of landscape evolution, and dominate the paleoseismic record in some locations on Earth, including locations distal from any identified active faults. A high scientific priority should be placed on improving the spatial extent and quality of ‘off-fault’ shaking records of strong earthquakes, particularly near major urban centres.
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New Zealand whitebait comprises the migratory juveniles of five species of native Galaxias. The most abundant of these is inanga, Galaxias maculatus. In 1987, the Department of Conservation (DOC) commissioned nationwide field surveys to identify (with the aim of protecting) inanga spawning sites, with data to be collated into a database administered by the National Institute of Water and Atmospheric Research Ltd (NIWA). The database currently holds 562 records from a total of 194 inanga spawning sites. Spawning sites have been located in every coastal DOC conservancy except Auckland. Further work to identify spawning sites is required, particularly in Northland, Auckland, Waikato, Wellington and Southland Conservancies. At least some protection work has been carried out in every conservancy where spawning has been located. Inanga spawning usually occurs on autumnal spring tides, with the nationwide peak spawning activity taking place 2 or 3 days after the new or full moon; however, some spawning may also occur in spring. Preferred spawning sites appear to be the banks of tidally-influenced flow-stable waterways, and tributaries and small creeks in very large catchments, often where there are embayments and confluences. Inanga spawn gregariously amongst inundated bankside vegetation. Consequently, spawning sites and eggs are prone to damage by cattle trampling or grazing. Exotic vegetation commonly associated with inanga spawning includes a number of grass and herb communities, often dominated by tall fescue (Festuca arundinacea). A wide variety of native plants are also associated with inanga spawning. These include New Zealand rush (wiwi, Juncus gregiflorus), bull rush (raupo, Typha orientalis), flax (harakeke, Phormium tenax) and toetoe (Cortaderia richardii). The spread of reed sweet grass (Glyceria maxima) and other exotic grass species unfavourable for fish spawning into spawning areas is of concern.
Article
Riparian vegetation has been compromised worldwide by anthropogenic stressors, including urbanization and livestock grazing. In New Zealand, one consequence has been a reduction in the obligate riparian spawning habitat of Galaxias maculatus. This diadromous species forms the basis of an important fishery where juveniles are caught as they migrate into freshwater. Spawning success of G. maculatus is closely associated with the nature of available riparian habitat. We used a field experiment in a rural stream to test whether livestock grazing limits egg production and whether there is a lag in increased egg production after protection from grazing because of the recovery time of riparian vegetation. In a separate experiment in an urban stream we tested whether improved riparian management can increase egg production. Livestock exclusion produced an immediate and long-lasting increase in the height and density of riparian vegetation with reduced fluctuations in the ground-level physical environment, and positive changes to the density and survival of eggs. After 4 years, egg densities in exclosures were 400 times greater than in grazed controls and egg survival had doubled. Mowing riparian vegetation 2 months prior to spawning reduced egg densities by 75% and survival by 25%. Our experiments showed that altering grazing and mowing in spawning sites produced dense riparian vegetation, that this improved the microsite environment and resulted in greatly increased egg deposition and survival over several years. This clearly indicates that the single most effective step in rehabilitating G. maculatus spawning habitat is a simple reduction in grazing/mowing pressure.
Article
1. Known diadromous fish number <250 species, and <1.5% of fish species. 2. They comprise ca. 3% of species regarded as ‘endangered’. 3. Amongst them are species of great importance to fisheries, and out of proportion to their number. 4. They occupy complexes of connected habitats between or through which passage is needed at two or more life history phases. 5. They therefore pose special problems for conservation which relate to: a. diversity of habitats; b. huge areas occupied; c. the spatial separation of the various habitats used; d. need for fish passage; e. often heavy exploitation. 6. These problems are often the opposite of those experienced with species that occupy local habitats and which are in danger of local extirpation.
Article
Several diadromous New Zealand and Australian species of Galaxias are now known, or suspected, to deposit their eggs amongst riparian vegetation or substrates either supratidally in estuaries or in forested streams in locations that are only temporarily submerged by elevated water levels. The eggs develop in a humid atmosphere and hatch when the egg deposition sites are resubmerged; a significant role for agitation in stimulating hatching seeming likely. There are risks from the eggs becoming dehydrated, and also from a failure by water to resubmerge the eggs before they have exhausted their energy resources. Hatching is triggered by elevated flows, perhaps being an outcome of agitation of the eggs. Elevated flows may also increase the rate of downstream transport of the larvae, facilitating survival during dispersal to sea from spawning sites in streams that may be long distances inland. Hatching during flood events may favour survival of the larvae because turbid flows may provide ‘cover’ for the larvae as they emigrate to sea. Risks from egg predation by aquatic predators may be replaced by risks from terrestrial predators.
Article
Mortality from predation during the early life-stages of most teleost fishes can be extreme, and many species have developed specialized spawning strategies to reduce predation. In the diadromous fish Galaxias maculatus there is terrestrial development of eggs which restricts aquatic predation, but exposes them to terrestrial predators and a more extreme physical environment. We hypothesised that exotic slugs (Milax gagates, Deroceras panormitanum and D. reticulatum) and mice (Mus musculus) reduce the survival of developing eggs and tested this using laboratory and field predation experiments and sampling. We also tested the effects of riparian vegetation composition and density on egg survival. We found that exotic slugs (M. gagates and D. panormitanum) reduced the survival of eggs in laboratory experiments, but that neither slugs nor mice affected egg survival in field experiments. Egg densities were positively associated with the stem density of riparian vegetation and the thickness of the aerial root-mat. Egg survival was also positively associated with stem density and aerial root-mat thickness, but was not density-dependent. Although predation by mice and slugs did not appear to be a major cause of egg mortality in our study locations, mortality dynamics could be different in areas with greater densities of predators. Abiotic factors are important in egg survival and these are heavily modified by the height and density of riparian vegetation. It is likely that G. maculatus egg survival, therefore, co-varies with the composition of riparian vegetation.
Article
Abstract  Spatial prioritization techniques are applied in conservation-planning initiatives to allocate conservation resources. Although typically they are based on ecological data (e.g., species, habitats, ecological processes), increasingly they also include nonecological data, mostly on the vulnerability of valued features and economic costs of implementation. Nevertheless, the effectiveness of conservation actions implemented through conservation-planning initiatives is a function of the human and social dimensions of social-ecological systems, such as stakeholders' willingness and capacity to participate. We assessed human and social factors hypothesized to define opportunities for implementing effective conservation action by individual land managers (those responsible for making day-to-day decisions on land use) and mapped these to schedule implementation of a private land conservation program. We surveyed 48 land managers who owned 301 land parcels in the Makana Municipality of the Eastern Cape province in South Africa. Psychometric statistical and cluster analyses were applied to the interview data so as to map human and social factors of conservation opportunity across a landscape of regional conservation importance. Four groups of landowners were identified, in rank order, for a phased implementation process. Furthermore, using psychometric statistical techniques, we reduced the number of interview questions from 165 to 45, which is a preliminary step toward developing surrogates for human and social factors that can be developed rapidly and complemented with measures of conservation value, vulnerability, and economic cost to more-effectively schedule conservation actions. This work provides conservation and land management professionals direction on where and how implementation of local-scale conservation should be undertaken to ensure it is feasible.
Article
Conservation assessment is a rapidly evolving discipline whose stated goal is the design of networks of protected areas that represent and ensure the persistence of nature (i.e., species, habitats, and environmental processes) by separating priority areas from the activities that degrade or destroy them. Nevertheless, despite a burgeoning scientific literature that ever refines these techniques for allocating conservation resources, it is widely believed that conservation assessments are rarely translated into actions that actually conserve nature. We reviewed the conservation assessment literature in peer-reviewed journals and conducted survey questionnaires of the authors of these studies. Two-thirds of conservation assessments published in the peer-reviewed scientific literature do not deliver conservation action, primarily because most researchers never plan for implementation. This research–implementation gap between conservation science and real-world action is a genuine phenomenon and is a specific example of the “knowing–doing gap” that is widely recognized in management science. Given the woefully inadequate resources allocated for conservation, our findings raise questions over the utility of conservation assessment science, as currently practiced, to provide useful, pragmatic solutions to conservation planning problems. A reevaluation of the conceptual and operational basis of conservation planning research is urgently required. We recommend the following actions for beginning a process for bridging the research–implementation gap in conservation planning: (1) acknowledge the research–implementation gap is real, (2) source research questions from practitioners, (3) situate research within a broader conservation planning model, (4) expand the social dimension of conservation assessments, (5) support conservation plans with transdisciplinary social learning institutions, (6) reward academics for societal engagement and implementation, and (7) train students in skills for “doing” conservation. Resumen: La evaluación de la conservación es una disciplina que evoluciona rápidamente y cuya meta es el diseño de redes de áreas protegidas que representen y aseguren la persistencia de la naturaleza (i.e., hábitats de especies y procesos ambientales) mediante la separación de áreas prioritarias de las actividades que las degradan o destruyen. Sin embargo, no obstante una creciente literatura científica que refina estas técnicas para la asignación de recursos para la conservación, es amplia la creencia de que las evaluaciones de la conservación raramente se traducen en acciones que realmente conservan la naturaleza. Revisamos la literatura sobre evaluación de la conservación en revistas con revisión por pares y aplicamos cuestionarios a los autores de estos estudios. Dos tercios de las evaluaciones de conservación publicadas en la literatura científica revisada por pares no consideran acciones de conservación, primariamente porque la mayoría de los investigadores nunca planean la implementación. Esta brecha investigación-implementación entre la ciencia de la conservación y la acción en el mundo real es un fenómeno genuino y es un ejemplo específico de la “brecha conocer-actuar” que es ampliamente reconocida en la ciencia del manejo. Debido a los recursos tristemente inadecuados que se asignan a la conservación, nuestros resultados originan preguntas sobre la utilidad de la evaluación de la conservación, como es practicada actualmente, para proporcionar soluciones pragmáticas a los problemas de planificación de la conservación. Se requiere urgentemente una reevaluación de las bases conceptuales y operativas de la investigación para la planificación de la conservación. Recomendamos las siguientes acciones para iniciar un proceso para reducir la brecha investigación-implementación en la planificación de la conservación (1) reconocer que la brecha investigación-implementación es real, (2) obtener preguntas de investigación con profesionales, (3) situar la investigación en un modelo de planificación de la conservación más amplio, (4) expandir la dimensión social de las evaluaciones de la conservación, (5) apoyar los planes de conservación con instituciones de aprendizaje social transdisciplinarias, (6) recompensar a académicos por compromisos con la sociedad y su implementación y (7) entrenar a estudiantes en habilidades para ‘hacer’ conservación.
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