Abstract

Background: Environmental offset programs for threatened plant species can be limited by the capacity to propagate sufficient plants for establishing offset plantations. This study describes the use of clonal propagation techniques for an offset program that propagated two species impacted by a landslide and road works. Materials and Methods: Cuttings were collected from Pomaderris clivicola (Rhamnaceae) and Bertya pedicellata (Euphorbiaceae) on 9 and 7 occasions, respectively. Shoots were also initiated into tissue culture. Results: Both species proved extremely difficult to propagate from cuttings and tissue culture. Rooting frequencies for P. clivicola cuttings were 4.3%. Repeated harvests of cuttings from the impacted plant population over more than 2 years eventually provided most of the P. clivicola plants required for the offset planting. However, the offset population of P. clivicola also had to be supplemented with some plants produced by tissue culture and with one plant that was excavated from the impacted population. Rooting frequencies for B. pedicellata cuttings were only 1.3%. A combination of cutting propagation and tissue culture did not produce sufficient B. pedicellata plants for the offset planting, but the offset population was supplemented with 27 plants that were excavated during road works. Conclusion: Success in producing the offset plants depended ultimately on a combination of (a) Cutting propagation, (b) Tissue culture propagation and (c) Whole plant excavation and translocation. This case study highlights challenges and successes in propagating poorly-known species for an environmental offset program within a short timeframe and with little prior knowledge of suitable propagation methods.; ;

Highlights

  • Environmental offset programs for human-impacted and threatened plant populations depend upon the capacity to propagate the species, often within short timeframes and with little prior knowledge of suitable propagation methods

  • It can be determined by permit conditions that stipulate the plant parts to be collected from the impacted population and the number and genetic composition of plants that are required in the offset population[3,4,5,6]

  • Propagation from cuttings or tissue culture can provide a reproductively more-mature offset population that is of the same genetic composition as the impacted population, this plant production strategy can be challenging if shoots from the impacted population have low amenability to clonal propagation[2,9,13,14]

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Summary

Introduction

Environmental offset programs for human-impacted and threatened plant populations depend upon the capacity to propagate the species, often within short timeframes and with little prior knowledge of suitable propagation methods. The choice of propagation method can be limited by the availability of plant material, such as seeds or actively growing shoots. The choice of propagation method can be limited by the availability of plant material, such as seeds or actively growing shoots1,2 It can be determined by permit conditions that stipulate the plant parts to be collected from the impacted population and the number and genetic composition of plants that are required in the offset population[3,4,5,6]. Propagation from cuttings or tissue culture can provide a reproductively more-mature offset population that is of the same genetic composition as the impacted population, this plant production strategy can be challenging if shoots from the impacted population have low amenability to clonal propagation[2,9,13,14].

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