Economic native plants of New Zealand

The known and potential uses of New Zealand native plants and the products obtained from them are reviewed. Introduced species are not included.     

Movement of exotic plants into coastal native forests from gardens in northern New Zealand

The anti-predator behaviours of a New Zealand freshwater crayfish (Paranephrops zealandicus) to the native long-finned eel (Anguilla dieffenbachii) and the introduced brown trout (Salmo trutta) were investigated. Crayfish modified their behaviour in the presence of both trout and eels. However, a significantly greater number of defensive chela displays and swimming responses were made to eels than trout. Crayfish were able to use chemical cues from skin mucus to detect eels but not trout. Paranephrops zealandicus is able to make some appropriate defensive behavioural responses to the introduced brown trout as well as to its native predator, the long-finned eel. However, crayfish may be at greater risk from the introduced predator because of their apparent inability to detect trout using non-contact chemical cues. This may be a reflection of the different co-evolutionary histories crayfish have had with trout and eels.     

Root site occupancy modelling of young New Zealand native plants: implications for soil reinforcement

Plants are widely used in soil conservation to control and prevent erosion on hillslopes and on riverbanks. Previous research has shown the mechanical root reinforcement on soil stability can be considerable. However, land and forest managers still require information and simple tools to enable them to determine how and when a species becomes effective in terms of soil stabilisation. This paper uses root length data from a trial of young New Zealand trees and shrubs to develop a simple model to account for the spatial occupancy of a planting site by roots, and by implication their potential strength contribution to soil reinforcement. It is developed by calculating root surface area in contact with the soil to obtain an effective radius of the root spread about the stem. The approach generates a set of coefficients that are unique to a species for a given site which can then be used in the generalised model to predict root site occupancy, which is taken as a proxy for when soil reinforcement is attained. This information can then be used to assess effectiveness of different species mixes in planting plans.     

Direct seeding of indigenous tree and shrub species into New Zealand hill country pasture

Summary Our study aimed to examine the applicability of a native plant restoration technique involving close grazing, blanket herbicide spraying and mob stocking (to trample the seed into the soil) for establishing New Zealand native tree and shrub species into exotic hill country pasture. This approach represents an alternative to the usual spaced-planting of seedlings in the context of an indigenous vegetation restoration programme. Field-collected seed of Cabbage Tree ( Cordyline australis ), Kahikatea ( Dacrycarpus dacrydioides ), Kanuka ( Kunzea ericoides ), Karamu ( Coprosma robusta ), Kohuhu ( Pittosporum tenuifolium ), Koromiko ( Hebe stricta ), and Manuka ( Leptospermum scoparium ) were germination tested in the laboratory, and broadcast sown in two field experiments in spring 2001 and autumn 2002. The spring-sown experiment tested the effect of mob stocking and the autumn-sown experiment tested the effect of mob stocking and sowing rate. Laboratory germination varied widely among species (0–88%). In the field, the two shrubs, Koromiko and Karamu, established densities of up to 5 and 1.2 plants/m², respectively, after 2.5 years. Autumn emergence for these two species strongly related to sowing rate. Three tree species, Cabbage Tree, Kahikatea and Manuka, emerged in the field but did not survive beyond 6 months. Mob stocking was effective in spring but not autumn sowing, implicating soil moisture content as an important factor in germination success. The study demonstrated that the direct seeding technique was successful for two shrub species, highlighting the potential for development of a cost-effective native plant restoration approach.     

Performance of five arid land shrub species in direct seeding: implications for seed-based restoration

Direct seeding is one of the most feasible techniques in practical, logistical, and economic terms for large-scale restoration of arid lands. However, several factors are still under study to enhance the outcomes of this restoration alternative, with species selection being a pivotal component. To evaluate differences in the performance of species in direct seeding, we selected five shrubs from the arid region known as “Monte Desert” in Argentina: Atriplex lampa, Hyalis argentea, Larrea divaricata, Neltuma flexuosa var. depressa, and Parkinsonia praecox. Direct seeding was carried out in furrows (4.0 m long, 0.5 m wide, and 0.4 m deep) with seeds previously treated to dormancy alleviation and with a density of 250 seeds/m². We evaluated results in 12 furrows, where topsoil and hydrogel were deposited. The biological variables considered were seedling emergence, seedlings establishment regarding sowed seeds, and seedling success (survival in relation to emerged seedlings) after almost 3 years. The species with the highest emergence and establishment rates was A. lampa (50.16 and 23.75%, respectively). L. divaricata showed the lowest values for these variables (2.17 and 0.83%, respectively). On the other hand, the survival of N. flexuosa seedlings was >2× that of L. divaricata (65.02 vs. 30.36%). We discuss the notable differences in species performance and the possible role of furrows in the results.     

Risk assessment model for the introduction of non‐native freshwater fish into New Zealand

A risk assessment model was developed to score the potential risk for both the establishment and impact of introduced freshwater fish species in New Zealand. Although based on similar models developed for Australia and the UK, it is customised to a New Zealand context in which the risk of a site‐specific ecological impact is of more concern than the potential for a species to spread rapidly and widely (i.e. its invasiveness). The model was calibrated using data on 21 introduced fish species already present in New Zealand and tested on eight species not present but for which a decision on introduction has been made using other methods. Threshold scores for risk of establishment, risk of impact and overall risk of causing ecological damage were set based on current knowledge and incorporated into a decision support system to provide managers with a numerical (vs subjective) basis for deciding on whether or not to permit the entry of a new species. The model assists in decision‐making on the introduction of new species and also provides a means of assessing the ecological risk posed by the further spread of those introduced fish already present.     

Roadside revegetation with native plants: Experimental seeding and transplanting of stem cuttings

Questions: Can we use local native plants for roadside revegetation? What cultural methods help enhance the process? Location: Trans Canada Highway, Terra Nova National Park, Newfoundland. Objectives: To (1) test stratification requirements for seed ger‐mination, (2) determine if germination, survival and growth of seedlings and stem cuttings of selected plants can be increased by mulching treatments and (3) identify native plants and cultural treatments useful for revegetation. Methods: We tested seed germination of Kalmia angustifoliaIris versicolorJuncus effususEriophorum vaginatum, Clintonia borealis and Cornus canadensis in a greenhouse experiment. We conducted field experiments of roadside revegetation using seeds of K. angustifolia, I. versicolorJ. effusus and E. vaginatum, as well as seedlings of I. versicolor and rooted stem cuttings of Emptrum nigrum and Juniperus communis after hay‐mat mulch and organic matter mulch application. Results: Stratified seeds of K. angustifoliaI. versicolor, J. effusus and E. vaginatum germinated successfully in the greenhouse, whereas C. borealis and C. canadensis seeds did not. Along roadsides, only I. versicolor seeds germinated. Iris versicolor cover increased significantly in organic matter mulch compared to hay‐mat mulch and control. Transplanted I. versicolor seedlings had high survival in all treatments but growth was reduced in organic matter mulch. Survival and growth of stem cuttings of E. nigrum and J. communis were significantly increased on hay‐mat mulch. Application: Rooted stem cuttings of E. nigrum and J. communis planted on hay‐mat mulch can be used as a practical method of roadside revegetation. These shrubs have low structure, are evergreen, and exhibit stress‐tolerance properties, which make them ideal species for roadside revegetation. They are also non‐palatable to wildlife. Roadside ditches can be revegetated by seeds or seedlings of I. versicolor. Robust roots and rhizomes of this plant may provide soil stability and dark green leaves and attractive flowers create aesthetically pleasing vegetation cover.     

Assessing significance for biodiversity conservation on private land in New Zealand

The assessment of ecological significance is a key part of a territorial local authority’s (TLA) responsibility to provide for the protection of areas of significant indigenous vegetation and significant habitats of indigenous fauna as required under Section 6(c) of the Resource Management Act (RMA) 1991. While a number of methods have been used to achieve this, these have been largely unpublished and there is considerable variability in the approach taken by different TLAs. We propose four criteria (rarity and distinctiveness, representativeness, ecological context, and sustainability) for assessing significance of indigenous biodiversity in terms of RMA Section 6(c). These criteria could form the basis for a consistent national approach to significance assessment. These criteria have been developed from early assessment schemes such as the Protected Natural Areas Programme. While there is no one “right” system for conservation assessment, we hope this paper will stimulate discussion amongst the ecological community on the best ways to undertake significance assessment.     

Seed bed treatment effects on vegetation and seedling establishment in a New Zealand pasture one year after seeding with native woody species

Summary Efforts to re‐establish indigenous forests in pastoral New Zealand have increased as the value of native biodiversity has been realized. Direct seeding of woody species is preferable to transplanting, as labour and material costs are less. However, the success rate of direct seeding in pasture has been variable due to intense competition from adventive species. We initiated an experiment in pasture plots adjacent to a forest fragment where seed bed treatments (increasing in degree of disturbance from herbicide application to turf removal and topsoil removal) in combination with mulch treatments (wood chip shavings with and without forest floor organic material) were seeded with a mixture of New Zealand lowland forest species. The objective of the study was to determine if early successional plant communities, and ultimately seedling establishment, differed as a result of seed bed preparation after 1 year. Coprosma robusta (Karamu) and Kunzea ericoides (Kanuka) seedlings established on plots in significant numbers: both species were most abundant on topsoil‐removed plots where bare substrate was greatest and plant cover least. Both seed bed treatments and mulching treatments led to measurable differences in overall composition of early successional plant communities. However, absence of plant cover and low soil fertility (both associated with the topsoil‐removed treatment) were the most important factors in seedling success.     

Determining variation in the success of New Zealand land birds

The New Zealand avifauna has changed considerably since the arrival of humans approximately 1000 years ago. The extinction of native species followed by their replacement with introduced exotic species is recognized as having greatly reduced the distinctiveness of the avifauna. Using phylogenetically independent methods, I tested whether life history and ecological correlates of extinction, introduction and persistence were significant across species and within taxa. Extinct land bird species were, on average, and independent of phylogenetic relatedness, larger-bodied than extant species. Introduction success was found to be significantly associated with increasing species body size, generation time and indices of human effort. In contrast, the geographical distribution of extant land birds was correlated with traits associated with high population growth rates (i.e. small, rapidly developing species, with high fecundity). My results suggest that selection pressures have changed significantly since the arrival of human colonists in New Zealand and that these changes have favoured different types of land birds, to the general detriment of endemic species. Comparative methods that explicitly examine historical changes are necessary to elucidate the changing roles of biological and extrinsic traits in the differential success of species in any assemblage.     

Some issues and options for the conservation of native biodiversity in rural New Zealand

Summary For the 70% of New Zealand under private ownership, native biodiversity conservation has to occur within a landscape that must also provide a productive return to land owners. Recent New Zealand legislation, especially the Resource Management Act 1991, promotes sustainable management on private land by allowing for the economic and cultural well-being of local communities while providing for the protection of natural resources including native biodiversity. We suggest that, to effectively conserve native biodiversity in rural landscapes, we need to consider four key issues: (i) what might be realistic goals for native biodiversity conservation; (ii) how might we better arrange different land uses to meet both native biodiversity and production goals; (iii) what is the optimum arrangement of native biodiversity; and (iv) how native biodiversity conservation can improve productive returns to land managers. Options to enhance native biodiversity conservation include a variety of incentives (e.g. management agreements, financial incentives and regulatory systems) and onsite management options (e.g. remnant management, restoration plantings, weed and pest control, use of native species for commercial and amenity purposes, use of exotic species to facilitate native biodiversity). The importance of taking a landscape-based rather than a paddock-based approach to management is emphasized.     

Fusaria and Fusarium toxins in New Zealand maize plants

A time course study was made of the development of Fusarium infection and the appearance of the three Fusarium toxins, nivalenol (NV), deoxynivalenol (DON) and zearalenone (ZEN), in various fractions of maize plants from two sites in New Zealand, one in the Manawatu region and one in the Waikato. Fusarium infection was seen in leaf axil fractions in January, at the time of tassel emergence, and was detectable in stalks, leaf blades, rachis and peduncles during February and in kernels in April. NV, DON and ZEN were only detectable some time after infection was demonstrable. NV, in high concentrations relative to DON (up to 287 mg/kg for NV and up to 8 mg/kg for DON), was found in fractions from the Manawatu site where F. crookwellense and F. culmorum were the predominant toxigenic species. NV and DON at similar levels (up to 25 mg/kg) were found in fractions from the Waikato site at which F. graminearum and F. subglutinans predominated. Highest levels of NV and DON were in rachis and peduncle. ZEN was found most consistently in leaf axils and blades at both sites (up to 8 mg/kg at the Manawatu site and up to 75 mg/kg at the Waikato site) but at times there were high levels in rachis fractions (up to 417 mg/kg at the Manawatu site). This revised version was published online in June 2006 with corrections to the Cover Date.     

Upscaling restoration of native biodiversity: A New Zealand perspective

Efforts are being made to upscale restoration of New Zealand's native ecosystems. Success depends, however, on consideration of several key issues that need to be built into restoration planning, implementation and monitoring. This study makes eight recommendations to improve the prospect of obtaining the hoped‐for biodiversity conservation outcomes.     

Integration of alien plants into a native flower-pollinator visitation web

Introduced alien species influence many ecosystem services, including pollination of plants by animals. We extend the scope of recent 'single species' studies by analysing how alien plant species integrate themselves into a native flower visitation web. Historical records for a community in central USA show that 456 plant species received visits from 1429 insect and 1 hummingbird species, yielding 15 265 unique interactions. Aliens comprised 12.3% of all plant species, whereas only a few insects were alien. On average, the flowers of alien plants were visited by significantly fewer animal species than those of native plants. Most of these visitors were generalists, visiting many other plant species. The web of interactions between flowers and visitors was less richly connected for alien plants than for natives; nonetheless, aliens were well integrated into the native web. Because most visitors appear to be pollinators, this integration implies possible competitive and facilitative interactions between native and alien plants, mediated through animal visitors to flowers.     

Quantitative analyses of shade-shoot architecture of conifers native to New Zealand

Shoot architecture was quantified by measuring the "maximum silhouette area ratio" (R_max). R_max was calculated from the maximum silhouette area (or projected area) of the intact shoot, divided by the silhouette area of the leaves or phylloclades (leaf-like flattened stems) when they are removed from the shoot and laid out flat. Like conifers of the Northern Hemisphere (NH) with non-appressed foliage, the R_max of shade-adapted shoots ranged from 0.5 to 1.0 in New Zealand (NZ) conifers with non-appressed foliage. Defining a "leaf" to mean either a true leaf or a phylloclade, the following was found: leaf area/leaf dry weight, leaf area/shoot dry weight, and leaf dry weight/shoot dry weight, were all similar in the shade-shoots of NZ and NH conifers. None of these variables were significantly correlated with R_max in the NZ conifers, unless species with leaves averaging less than 4 mm² in size were excluded from the analyses. Foliage dry weight/shoot projected area was strongly correlated with R_max. NZ conifers had both smaller and larger mean leaf sizes in comparison to NH conifers. The mean projected area per shade-adapted leaf of NZ conifers varied from 2.7 to 436 mm². In NH conifers, the mean projected area per shade leaf varied from 12 to 83 mm². Except for the strikingly larger range in leaf size in NZ conifers, the data support a hypothesis of strong convergent evolution of shade-shoot architecture in NZ and NH conifers. The results are discussed in relation to photosynthesis, stand production, and the ecological distribution of conifers.     

Alien and native plants show contrasting responses to climate and land use in Europe

Aim We tested whether the distribution and cover of alien plant species in Europe was related to human disturbance and microclimate. Location Surveys were conducted at 13 sites across Europe, each containing a pair of landscapes with different land‐use intensities. Methods Sampling locations were chosen based on land use and microclimate at two scales: land use was characterized at the patch and landscape scale; climate was expressed as regional and local temperature. The slope of each sample location was derived from a digital elevation model. Cover of plant species was measured using point counts and analysed using mixed effect models. Species were classified as native, archaeophytes and neophytes (pre‐ versus post‐ad 1500 immigrants). Due to the zero inflation observed in the alien groups, their cover was analysed conditional on their presence. Results Anthropogenic disturbance was a significant explanatory variable, increasing the presence and cover of alien species and decreasing the cover of native species. Alien presence was increased in sites under agricultural management, while their cover responded to land use at both local and landscape scales (and to their interaction), such that only natural habitats in semi‐natural landscapes had low alien cover. Microclimate was important for neophytes, with presence concentrated around mesic conditions. Slope was relevant for archaeophytes and native species, suppressing the former group and promoting the latter one. Main conclusions We found that, at the European scale, the distribution of alien plants is related to anthropogenic disturbance more than to microclimatic differences. The presence of neophytes, however, was influenced by climate at local and regional scales, with the highest incidence under mesic conditions. The different patterns observed for the presence and cover of alien species suggest different mechanisms acting during their establishment and spread. They also suggest that to counteract the expansion of alien species natural habitats may need to be maintained at landscape scales.