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MONITORING AND PRIORITISATION OF

FLORA TRANSLOCATIONS:

A SURVEY OF OPINIONS FROM

PRACTITIONERS AND RESEARCHERS

N. Hancock1, R.V. Gallagher1 & R.O. Makinson2

1. Department of Biological Sciences, Macquarie University

2. Royal Botanic Gardens & Domain Trust, Sydney

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This document was compiled as part of a project funded by the NSW Biodiversity

Research Hub in 2013-14. It is intended to be read in conjunction with the Australian

Network for Plant Conservation publication Guidelines for the translocation of

threatened plants in Australia (Vallee et al. 2004).

Please cite this publication as:

Hancock, N., Gallagher, R.V. & Makinson, R.O. (2014). Monitoring and prioritisation

of flora translocations: a survey of opinions from practitioners and researchers.

Report to the Biodiversity Hub of the NSW Office of Environment & Heritage.

For further correspondence contact: [email protected]

mailto:[email protected]

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TABLE OF CONTENTS

Summary v

Acknowledgements v

List of Tables vi

RESULTS OF SURVEY OF PRACTITIONERS AND RESEARCHERS

Section 1 A synthesis of opinions on monitoring of flora

translocations – results from the Flora translocation

survey (2013)

1. The Flora Translocation Survey (2013)

1.1 Introduction 1

1.2 Aims and objectives of the survey 1

1.3 What is a successful translocation? 2

1.4 The importance of monitoring 2

2. Survey design

2.1 Selection of survey respondents 3

2.2 Survey format 4

2.3 Data analysis 5

3. Survey results: quantitative data

3.1 General information 5

3.2 Monitoring duration by habit groups 6

3.3 Monitoring duration by breeding system 8

3.4 Monitoring duration by planting method 10

3.5 Monitoring duration by taxonomic groups 11

3.6 Other life-cycle monitoring

3.6.1 Early survivorship 13

3.6.2 Growth 13

4. Interpretation of the quantitative data

4.1 Commonalities 14

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4.2 Considerations for interpretation of the data 14

4.3 Other comments 15

5. Other monitoring considerations

5.1 Representative sampling 15

5.2 Comparison to reference site 16

5.3 Other monitoring variables 16

5.4 Suggestions for simple, cost effective monitoring of flora

translocations 18

6. Conclusions 22

Section 2 Prioritisation of translocations

1.1 The need to prioritise 23

1.2 Decision tool for prioritising candidate species 23

1.3 Practitioner and researcher opinions on pre-translocation

assessments 27

References 32

APPENDICES

Appendix 1 Compilation of established flora translocations in Australia 34

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Summary

This document provides the results of a survey of practitioners and researchers

working within the field of flora translocations throughout Australia. Specifically,

opinions were sought on optimal strategies for monitoring translocations after they

have occurred and for which factors are most important for prioritising candidate

species. A dichotomous key containing a series of questions that need to be

addressed prior to the approval of a translocation are also provided. This key is

intended to act as a set of guiding principles for choosing between potential

candidates for translocations.

Acknowledgements

The authors would like to acknowledge the contributions of Tricia Hogbin in providing

assistance in survey design and interpretation of data. We also thank staff within the

NSW Office of Environment and Heritage, specifically Linda Bell and James Brazil-

Boast.

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LIST OF TABLES

Table 1. Preferred duration of monitoring of flora translocation projects for various

plant growth habits

Table 2. Preferred duration of monitoring of flora translocation projects for various

plant breeding systems

Table 3. Preferred duration of monitoring of flora translocation projects by planting

method

Table 4. Additional monitoring variables, rated by respondents of the Flora

translocation survey (2013)

Table 5. Responses (%) from survey participants regarding factors that should be

known before proceeding with translocation

Table 6. Responses (%) from survey participants regarding preparatory measures

that should be undertaken before proceeding with translocation

Appendix 1. Compilation of established flora translocations in Australia

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RESULTS OF SURVEY OF PRACTITIONERS AND

RESEARCHERS

SECTION 1 - A synthesis of opinions on monitoring

of flora translocations – results from the Flora translocation

survey (2013)

1. The Flora translocation survey (2013)

1.1 Introduction

Translocations intentionally move organisms from one site to another and are

broadly classified as re-introductions and augmentations (reinforcements) within an

organisms’ known distribution, and introductions and ecological replacements

beyond the known range (IUCN/SSC, 2013). Translocations are regarded as an

appropriate (but not risk free) tool, in a suite of measures aimed at the conservation

of biodiversity (IUCN/SSC, 2013).

The challenge for conservation managers is to minimise project costs but at

the same time, retain the benefits that key processes, such as monitoring, add to the

success of a translocation project. To investigate how (or if) this is being achieved,

we surveyed practitioners and researchers involved in Australian flora translocations

to gather opinions on how effectively monitoring is carried out on current projects..

The outcomes of this exploratory survey are an indication of thinking among a

selection of practitioners and researchers, constrained by questionnaire

format. They are not the whole story and are not in themselves an adequate basis

for policy or prioritisation procedures. More detailed canvassing of a wider range of

expertise holders, and deeper mining of the information sources, would be needed to

provide that basis.

1.2 Aims and objectives of the survey

The aim of the monitoring section of the Flora Translocation Survey, 2013, was to

investigate the possibility of formulating a general, cost effective monitoring guideline

that can be adapted for individual flora projects. In addition, the survey was used to

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try and find commonalities between groups of species or species’ traits that could

lead to standardised monitoring.

1.3 What is a successful translocation?

Each translocation will have its own success criteria, but generally, success is

measured by the establishment of a self-sustaining population of the focal species

(Griffith et al., 1989; Fischer & Lindenmayer, 2000). Successful flora translocations

have also been described as the ability of the translocated population to persist and

reproduce (Godefroid et al., 2011). The Australian Network for Plant Conservation

(ANPC) flora translocation guidelines further splits success into short-term and long-

term objectives (Vallee et al., 2004). The short-term goal is the successful

establishment of the translocated individuals and the long-term goals are: the

management and control of threats; the attainment of sufficient numbers to avoid

both demographic and environmental stochasticity and successful reproduction and

natural recruitment (Vallee et al., 2004).

1.4 The importance of monitoring

Monitoring is a vital component of all translocation projects and is necessary for

ensuring adaptive management and evaluating success (Vallee et al., 2004;Menges,

2008; Maschinski et al., 2012). Monitoring contributes to the success of

translocations by (Menges 2008; Monks et al. 2012):

increasing basic biological and ecological knowledge;

enabling lessons to be learnt from past successes and failures by providing

the ability to adopt adaptive management;

allowing the evaluation of experimental approaches to translocation;

allowing comparisons with reference populations.

Furthermore, monitoring allows the assessment of the growth and survivorship of the

translocated population at regular intervals and permits the mitigation of threats as

they occur, thus increasing the chances of success (Dimond & Armstrong, 2007). In

particular, detailed long-term monitoring has been identified as a means to improve

current low success rates of species relocations (Sheean et al., 2012).

Implementation of a successful translocation project is dependent on long-

term monitoring and therefore requires an allocation of resources over a sufficiently

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long period. The ANPC guidelines stipulate that a translocation should not proceed

until sufficient funding is secured for post-translocation monitoring (Vallee et al.,

2004).

The costs associated with translocations are not usually disclosed, however

Sheean et al. (2012) reported the costs of three Australian fauna species relocation

programmes: $190,000 with an additional cost of $25,000 per year for five years for

an amphibian; $600,000 for a marsupial and $300,000 for the supplementation of an

avian species (the time frame was included for the first project only). The amphibian

example suggests that whilst initial translocation costs are high, on-going monitoring

requirements also make a high proportion of overall costs. Reporting of on-going

translocation projects shows that monitoring tends to be carried out for short periods

(within three years), rather than 10+ years (Sheean et al., 2012).

2. Survey design

2.1 Selection of survey respondents

The data for this study was derived from a section of the Flora Translocation Survey,

2013, that pertained only to practitioners and researchers who have been involved in

Australian flora translocations and could nominate the specie(s) that they have

translocated. Potential participants were identified by the project collaborators and

included:

Australian State and Territory threatened species project officers;

Australian authors from the IUCN Reintroduction Specialist Group case study

reports 2011, 2010 and 2008

(http://www.iucnsscrsg.org/index.php?option=com_content&view=article&id=

192&Itemid=587;

Case study presenters at past ANPC workshops (since 2004) on

'Translocation of Threatened Plants in Australia';

Speakers at an Australian Association of Bush Regenerators seminar

3/10/13.

Authors of papers that included the terms “assisted colonisation”, “managed

translocation”, “plant” and “Australia” in titles or keywords accessed via the

Scopus Database in 2013.

http://www.iucnsscrsg.org/index.php?option=com_content&view=article&id=192&Itemid=587

http://www.iucnsscrsg.org/index.php?option=com_content&view=article&id=192&Itemid=587

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Further participation was sought by the distribution of the survey through the

email networks of the Office of the Environment and Heritage (OEH) Threatened

Species Network, the Australian Network of Plant Conservation (ANPC) and the

Ecological Consultants Association of NSW.

2.2 Survey format

The survey was conducted on-line via SurveyMonkey and comprised two sections;

(1) Quantitative answers

(2) General opinions

In part (1) respondents were asked to identify flora species they have translocated

and to answer specific questions regarding the monitoring of the translocation project

for the identified species. The basis for these questions, from which a suite of

monitoring variables was determined, was derived from the current literature (Vallee

et al., 2004; Godefroid & Vanderborght, 2011; Maschinski et al., 2012). In particular,

these questions sought to elicit opinions on which variables should be measured for

translocated populations and at what duration. It is important to note that the

information gathered in the survey is not a substitute for expert opinion, but rather

seeks to complement already established protocols for flora translocation (namely

Vallee et al., 2004).

Respondents were provided with a list of life-cycle variables and asked to identify

the ideal duration of monitoring for each variable with a choice of: (1; 2; 3; 5; 7; 10;

10+ years, not important, not applicable). Life cycle variables included:

1. Survival;

2. Flowering plants;

3. Fruiting plants;

4. Seed production;

5. Abundance of naturally recruited (or regenerated) individuals;

6. Abundance of clonal offshoots (or ramet production)

To find commonalities between groups of species or species’ traits, respondents

were asked to categorize their species into the following groups:

Habit (woody plant - short-lived < 10 years; woody plant - long-lived ≥ 10

years; non-woody plant – perennial; non-woody plant – biennial; non-woody

plant – annual)

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Breeding system (sexual; asexual; can be sexual &/or asexual; other)

Transplant method (seedling transplant; adult transplant; direct seeding)

Taxonomic (genus and species)

In addition to the above, in regard to their nominated species, respondents were

asked to provide details on the type of translocation undertaken, the conservation

status of the species at the time of translocation, publication details of the project,

the current status of the project (finished or not) and if finished, whether there is an

informal interest group maintaining some involvement.

In part (2) questions on more general aspects of monitoring, including the

effectiveness of volunteer groups and suggestions for simple, cost effective

monitoring were also asked. Each question allowed room for comments in order to

encapsulate any other monitoring variables the respondents deemed necessary.

2.4 Data analysis

For quantitative data, not every respondent answered each duration question for

each life-cycle parameter. To calculate percentages of responses for each life-cycle

measurement, where the individual measurements were skipped or allocated ‘not

applicable’, these responses were removed. Therefore, the base percentage

calculation is different for each parameter.

For the general opinion section, where closed-ended questions gave

numerous answer options, a rating average was applied to each option. The rating

average was calculated as follows:

w1*n1 + w2*n2+w3*n3

T

Where w = weight of the answer choice; n = the number of responses for that option;

T = total number of responses.

3. Survey results: quantitative data

3.1 General information

Thirty-one respondents participated in the monitoring section of the survey, yielding

data for 85 species. Thirteen species were identified more than once, two genera

(acacias and eucalypts) and two vegetation communities were identified and these

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are not included in the number of (85) species. In addition, a bibliography of

translocation reports was compiled from survey responses and is included as

Appendix 1 to this report. 83% of the species were legislatively listed in one or more

Australian jurisdictions at the time of their translocation.

Reintroductions were the most common type of translocation (32%), followed

by introductions (22%) and ecological replacements (10%), as per the IUCN

definitions that were attached to the survey (IUCN/SSC 2013). Two thirds of the

projects are not finished in terms of the time frame set in their project plans.

Overwhelmingly, respondents think that all of the life cycle measurements

suggested in this survey are important to monitor. Some respondents provided

comments that their answer depends on the species and the circumstances. In

particular, we note the comments from one respondent (who has translocated

multiple species) that their answers ‘depends on what aspect of flowering/fruiting

plants are measured (e.g. flowering or not, the number of flowers, flower to fruit ratio)

and what goals/ success criteria is set and over what time frame’. There was no

capacity within the survey to ask respondents what specific aspects of each

monitoring parameter should be recorded for each species.

3.2 Monitoring duration by habit groups

The most frequently identified ‘habit’ for translocated taxa was Woody plant - long-

lived ≥ 10 years (Table 1). Non-woody plant – biennial and non-woody plant – annual

were absent from survey responses.

Table 1. Preferred duration of monitoring of flora translocation projects for

various plant growth habits. The first row in each cell identifies the number of

years the life cycle parameter should be measured according to survey respondents

and the percentage of total responses. The second row identifies the duration for the

second highest percentage of responses. The number in brackets in the third row of

each cell is the total number of responses. For instance for woody short-lived plants

(< 10 years), 75% of respondents think that survival should be monitored for over 10

years (10+) and 25% think it should be for 10 years (4 responses).

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Woody plant -

short-lived < 10

years

Woody plant -

long-lived ≥ 10

years

Non-woody

perennial plant

Survival 10+: 75%

10: 25%

(4)

10+: 51%

5: 18%

(52)

5: 45%

10+: 39%

(44)

Flowering 5: 75%

10+: 25%

(4)

**10+: 52%

5: 23%

(49)

**10+: 44%

3: 32%

(41)

Fruiting *5: 75%

10+: 25%

(4)

**10+: 54%

5: 27%

(42)

**10+: 68%

5: 23%

(22)

Seeding 5: 75%

10+: 25%

(4)

**10+: 41%

5: 28%

(47)

5+: 29%

5: 24%

(41)

Recruitment 10+: 75%

10: 25%

(4)

10+: 53%

10: 17%

(48)

10+: 41%

5+: 27%

(44)

Clonal n/a

(0)

2: 36%

5 & 10: both 18%

(11)

***3: 50%

10 & 10+: both

12%(24)

*But would prefer 10 years. **A substantial proportion of these responses (all from one

respondent) gave a caveat that ‘it depends on the situation.’ ***This question was not

applicable to many species and the majority of the responses came from one respondent

with a caveat that this measurement is not important. N.B. where responses are low, the

majority of responses may be only one person’s view for multiple species.

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3.3 Monitoring duration by breeding system

The most frequently identified breeding system was sexual (Table 2). Ten species

were nominated as ‘sexual and possibly also asexual but not confirmed’. These

responses were included in the sexual category.

Table 2. Preferred duration of monitoring of flora translocation projects for

various plant breeding systems. The first row in each cell represents the number

of years the life cycle parameter should be measured and the percentage of

responses total responses. The second row identifies monitoring duration for the

second highest percentage of responses. The number in brackets in the third row of

each cell is the total number of responses. For instance, for sexual breeding

systems, 49% of respondents think that survival should be monitored for over 10

years and 23% think it should be for five years (79 responses).

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Sexual Asexual Can be sexual or

asexual

Survival (3) 10+: 49%

5: 23%

(79)

10+: 100%

(1)

5: 59%

10+: 32%

(22)

Flowering *10+: 48%

5: 22%

(78)

10+: 100%

(1)

3 & 5: both 30%

(20)

Fruiting *10+: 57%

**5: 28%

(55)

10+: 100%

(1)

5: 43%

10+: 36%

(14)

Seeding *10+: 33%

5: 29%

(74)

Only needs to

be done once:

100%

(1)

5: 39%

5+: 28%

(18)


5: 16%

(77)

5: 100%

(1)

5: 32%

5+ & 10+: both 26%

(19)

Clonal ***3: 37%

2: 26%

(19)

5: 100%

(1)

***3: 46%

10 & 10+: both 23%

(13)

*A substantial proportion of these responses (all from one respondent) gave a caveat

that ‘it depends on the situation.’ **53% of responses nominated 5 years but would

prefer 10 years. *** 2/3rds of responses (one respondent) noted that this

measurement is not important.

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3.4 Monitoring duration by planting method

The most frequently identified planting method was seedling transplant, followed by

adult transplant (Table 3). For the purposes of this survey, the definition of seedling

transplant was assumed to cover those plants grown by seed in a nursery or

propagated by cuttings, and then transplanted as tubestock. However, this definition

was not included in the glossary and whilst some respondents distinguished between

the two, cuttings was included in the data as a tubestock transplant. It is possible

that some respondents thought of a ‘seedling transplant’ as the digging up and

transplanting of natural plants. A small number of respondents used a combination of

planting methods and a very small number used tissue culture. Because the

combination method cannot be further split and the sample size is small respectively,

this data was not included in the analysis.

The results from the survey show that there is a large difference in monitoring

duration, depending on the planting method. Monitoring is recommended for 10+

years where seedlings are planted but only 5 years if adults are planted. It is difficult

to comprehend why there is a difference between the two groups for survival but

perhaps for the other parameters, it is assumed that the plants planted as adults are

already reproducing. Alternatively, unintended confusion surrounding the terminology

of seedling transplant may have skewed the data one way or another.

Table 3. Preferred duration of monitoring of flora translocation projects by

planting method. The first row in each cell represents the number of years the life

cycle parameter should be measured and the percentage of responses. The second

row gives the second highest percentage of responses is given. The number in

brackets in the third row of each cell is the total number of responses. For instance

55% of respondents think that where adult plants were transplanted, survival should

be monitored for five years and 22% think that it should be for more than 10 years

(18 responses).

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Seedling transplant Adult transplant

Survival 10+: 39%

5: 30%

(56)

5: 55%

10+: 22%

(18)

Flowering *10+: 52%

3: 19%

(52)

5: 50%

10+: 25%

(16)

Fruiting *10+: 69%

5: 11%

(36)

5: 70%

10+: 20%

(10)

Seeding *10+: 38%

5+: 19%

(52)

5: 60%

10+,5+, 3: 13% each

(15)


10 & 5+: both 18.5%

(54)

5: 50%

10+: 19%

(16)

Clonal **3: 59%

10, 5 & 2: 12% each

(17)

10+, **3yr & other: 22% each

10, 5 & 2: 11% each

(9)

*A substantial proportion of these responses (all from one respondent) gave a caveat

that ‘it depends on the situation.’ ** All responses from one respondent who

nominated 3 years but said that this measurement is not important.

3.5 Monitoring duration by taxonomic groups

The largest family represented in the survey was Proteaceae. Monitoring data was

recorded 23 times, for 15 species by 17 different respondents (some species were

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represented twice and some respondents nominated more than one species). The

genera represented were: Banksia, Grevillea, Lambertia and Persoonia. All species

were nominated as having a sexual breeding system (including three Grevilleas that

were described as sexual and other, possibly selfing) and all but three Grevilleas as

having a woody, long-lived (≥ 10 years) habit (two Grevilleas were woody, short lived

and one was non-woody perennial).

Overwhelmingly for the Proteaceae, respondents thought that survival,

flowering, fruiting, seeding and the abundance of naturally recruited or regenerated

individuals should be monitored for 10+ years. However, it was also noted that for

some of these answers, the monitoring time depends on what aspect is being

monitored and what goals/success criteria are to be achieved. It should also be

noted that there were only two Lambertia species and one respondent thought that

monitoring for flowering, fruiting and seeded only needed to be for five years.

Orchids were represented by six species and one group “orchids” from six

different respondents. The six species were described as non-woody perennial

plants and all but one with sexual breeding systems. The ‘orchids’ group was

described as woody, long-lived (≥ 10 years) plants that can have either sexual or

asexual breeding systems. The majority of the respondents (2/3rds) thought that

survival, flowering, fruiting and the abundance of naturally recruited or regenerated

individuals should be monitored for five years. The remaining 1/3rd of respondents

suggested 10+ years. There was no consensus on seeding monitoring duration with

suggestions ranging from 3 - 10+ years and another comment that once seeding has

occurred, there is no need to monitor again.

Four Acacia species were represented in the survey, from five respondents.

Monitoring time for each parameter was variable but there was a slight preference

for 10+ years. Accordingly, it is difficult to draw generalisations for monitoring

guidelines for this taxon from the survey responses.

Unless the responses for a taxonomic group are large, caution should be

applied to the formulation of general monitoring guidelines from the survey

responses. Only the Proteaceae and orchid species as groups gave consistent time

frames to consider using the data for general monitoring guidelines. However, the

number of species analysed in the survey are small compared to their taxonomic

groups. Furthermore, inconsistent responses were given for the same species. As an

example, two different species were nominated by three and four different

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respondents for each species. For the same species, a different monitoring time for

each parameter was suggested by the respondents.

3.6 Other life-cycle monitoring

3.6.1 Early survivorship

To assess how frequently survivorship should be monitored, we split ‘survival’

into three phases: (1) transplant shock (2) establishment success and (3) project

success. The first two phases were answered on a general basis and the results are

discussed below. The third phase was specifically for the respondent’s case study

species and these results have already been discussed.

Overall, for the early stages of survival (1 and 2), the largest percentages of

respondents recommended that plants should be monitored weekly for the first

month and then adjust for the particular species and then yearly for establishment

success.

For transplant shock, the monitoring duration suggested by respondents

varied but was most commonly cited as weekly for the first month, followed by

various time periods thereafter. Most of the suggested time periods came with

comments that it depends on the species, the environmental conditions and on-site

threatening processes. Several respondents did not directly answer the question

because they felt that it depended on too many circumstances to give a quantitative

answer. It was also mentioned that it is important that monitoring also includes the

cause of the mortality. For establishment success (the period after potential

transplant shock), there was no clear consensus how long survivorship should be

monitored. The largest percentage of respondents (35%) thought that establishment

success should be monitored yearly but it is unclear from the survey results for how

many years this should be applied.

3.6.2 Growth

Monitoring guidelines usually recommend that growth measurements are

recorded (Vallee et al., 2004; Maschinski et al., 2012), but this variable is not always

deemed necessary (Godefroid & Vanderborght, 2011). 65% of 26 respondents

recommend that growth measurements be taken. Height was the most commonly

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mentioned trait, often in conjunction with width. However, growth measurements for

grasses, orchids and herbaceous species were generally less important.

4. Interpretation of the quantitative data

4.1 Commonalities

There are several ways that the data can be interpreted to find commonalities. For

example:

Within categories. For sexual breeding systems, the survey respondents

recommended that all monitoring is done for at least 10 years, apart from

abundance of clonal offshoots (or ramet production).

Between categories. Build a profile e.g. a woody long-lived, sexually

reproducing plant should be monitored for flowering for 10+ years.

Build a profile by taxonomic group. Monitoring duration suggested for the

taxonomic groups should be cross checked with the results from the habit

(Table 1) and breeding system (Table 2) data. The results should then be

reviewed by practitioners and researchers experienced in the biology,

translocation and revegetation of these groups. For example, a Proteaceae

that is a long-lived and sexually reproduces should be monitored for survival

for 10+ years. However, for non-woody perennial, sexually reproducing

orchids, monitoring duration for survival is less definitive because the

recommended monitoring duration for these three categories varied

considerably.

4.2 Considerations for interpretation of the data

The following should be considered when interpreting the survey results:

Magnitude of the largest response. More confidence should be allocated

where the percentages of responses is large. For example, for recruitment

(abundance of naturally recruited (or regenerated) individuals), 53% of

respondents nominated a particular monitoring duration for sexual breeding

systems compared to only 32% for can be sexual or asexual. More

confidence is given to the sexual monitoring time frame.

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Number of responses: For breeding systems, there were 79 responses for

sexual compared to 1 response for other for duration of survival monitoring.

This does not mean that the response for other is wrong, but it represents

only one person’s view.

4.3 Other comments

Some additional comments from respondents on monitoring duration are added here

because they may assist in the conversion of general guidelines into more specific

ones.

If actions recommended from the results are unlikely to be carried forward and

resources aren't available, highly detailed monitoring is not important.

Once it has flowered/fruited successfully, there is no need to re-monitor this

parameter again assuming that nothing else changes.

Monitor until regular seed set - 3 seasons in a row.

To simplify monitoring, take photographs from fixed points at preferably

regular intervals.

If the aim is for a self-sustaining population, monitor for multiple generation

times for short lived plants or for at least two generations for long lived plants

to determine if recruitment is occurring and if those generations are

reproductive.

‘The survival and reproduction of new recruits should be followed until those

new recruits produce new recruits. Time frame will depend for example on

climate and frequency and timing of disturbance events.

5. Other monitoring considerations

5.1 Representative sampling

The majority of respondents believe that where the number of translocated

individuals is large and time consuming to monitor, representative samples, from

which inferences can be drawn, can be measured. This response applied to all of the

life-cycle parameters listed in this survey, apart from survival where every individual

should be measured. Two methods of representative sampling were suggested. The

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first method is a random selection of a representative suite of plants (minimum of 10

plants per site per species) and secondly, transects through populations.

5.2 Comparison to reference site

To measure the success or otherwise of a translocation project, the life-cycle

measurements should be compared to those from natural populations of the species

(Vallee et al. 2004). To gauge the level of the importance of this monitoring action,

respondents were asked if their monitoring includes comparison(s) to a reference

site (e.g. the source populations), and if so, its timing. Overall, there was support for

this action but we note that a quarter of the respondents either do not make

comparisons to the reference site and / or they do not think that this measurement is

necessary (Figure 1). Of those who do compare, there was little difference between

a monitoring duration of each time the recipient site is monitored and when key

phenological phases of the focal species occur. One respondent opined that

‘comparisons should be made initially at each phase, but it becomes less important

once translocated and reference site become similar’.

Figure 1. Frequency of comparisons of the transplant and donor sites –

percentage of responses from the Flora translocation survey (2013).

5.3 Other monitoring variables

In addition to questions on monitoring duration, survey respondents were asked to

rank several important monitoring factors that enable assessment of the success or

failure of translocations. Respondents could nominate one of the following:

Unimportant, Not important, Important Very important; N/a. The list is by no means

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complete but it provides a list of non-life cycle monitoring variables that may be

useful for prioritization if resources are limited.

Table 4. Additional monitoring variables, rated by respondents of the Flora

translocation survey (2013)

Average

rating

Make detailed notes of what went wrong 3.89

Competition from weeds and / or other natives 3.61

Disturbance(s) within the planting site (e.g. fire, storm damage) 3.46

Physical identification markers at the site are intact 3.43

Damage from disease / pathogens 3.43

Herbivory (leaf damage from both insects and grazers) 3.36

Keep the monitoring data in more than one format (e.g. enter digitally

and keep hand-written notes)

3.32

Evidence that that translocated species may have facilitated the

establishment or altered the trajectory of other species

3.21

Disturbance(s) in close proximity to the planting site 3.19

Weather conditions at the recipient site 3.11

The level of genetic variation of the translocated population compared

to the source population

2.81

From the list of factors provided (Table 4), respondents believe that making detailed

notes of what went wrong is the most important thing to monitor. Presumably,

analysis of the detailed notes and its subsequent circulation would enable lessons to

be learnt from past mistakes. As an example, a couple of comments referred to

plants being trampled, particularly during monitoring visits. It was suggested that

stepping stones or branches be positioned (at an early stage) to minimise damage to

plants (and possible recruits) from multiple visits and from visitors to the site.

Comments throughout the survey also reinforced the importance of monitoring

competition from weeds and /or other natives. The accumulation of biomass other

than the transplanted species (particularly in grassland) was seen as detrimental to

the ease of finding the location of transplants and their offspring. A regime of

18

ecological burning was suggested as an action to help with the monitoring process

and in some cases to provide a disturbance necessary for regeneration.

One useful suggestion for keeping the monitoring data in more than one

format is to email the data. Presumably this suggestion refers to data obtained whilst

still in the field. This action of course, relies on the availability of Wi-Fi connections.

Although taking weather conditions at the recipient site ranked relatively lowly,

it was commented that it can be easily achieved by approximating data from the

nearest BOM automated weather station. The usefulness of this data depends on

the existence of micro-climates at the site but nonetheless, it gives an idea of trends

across time.

Genetic considerations were poorly ranked. Comments accompanying the

monitoring section of the survey shed some light on why genetic considerations

ranked relatively poorly. Organizations often don’t have the resources to investigate

genetic factors and it is ‘expensive and time consuming’. Even organizations with

laboratories have found that one-off genetic testing is not done unless it is a large

study. One respondent opined that the genetic comparison between the source and

recipient sites is only important if large losses occur and it is known they have

occurred from specific clonal lines or parent plants. The method suggested to obtain

this information is to ensure that record keeping and tagging is of high standard. The

importance of effective tagging and detailed site maps (including safe and secure

GPS data) was also raised elsewhere in the survey as a means of effective

monitoring via easy location of transplants and their recruits.

5.4 Suggestions for simple, cost effective monitoring of flora translocations

Respondent’s suggestions of other ways to monitor translocations more efficiently

centred around four main themes:

(1) Management

Strategic leadership, coordination and support for and with practitioners by senior

federal and state ecological experts, was identified as a means to achieve a more

effective approach to all aspects of translocations. In particular, co-ordination of

19

translocations of threatened flora with similar biology and ecology was identified as a

means to stop on-ground regional practitioners operating in isolation (and hence

inefficiently). It was noted that projects can be highly dependent on motivated and

interested OEH/NPWS staff and it was implied that turnover of staff is detrimental to

project success.

(2) Circulation of reports and data

The importance of circulating all reporting aspects of translocations was evident in

the survey. Public access to reports (both successes and failures) and data was

seen as a viable way to enable learning. Where to publish to enable maximum

coverage was not well defined but more detail is given in a separate document

(Appendix 1) which lists publication details of many of the translocation projects that

were used as case studies for this survey. More consultation within the

‘translocation’ community on the subject of where data and reports can be safely

stored and easily circulated appears to be warranted. One respondent commented

‘OEH were provided with reports and follow up monitoring reports, but from

experience these can rarely be found’.

(3) Knowledge of the focal species

Detailed knowledge of biological and ecological data of the transplanted species was

identified as very important to the success of the project. Detailed knowledge was

identified as a means to facilitate more effective monitoring programs in the following

ways:

Context-specific monitoring sheets / programmes can be formulated.

The duration of recruitment monitoring can be fine-tuned e.g. ‘plant is long-

lived (>100 years) and recruitment is sporadic’ and seed bank knowledge e.g.

seed may be stored in the ground and not germinate for some years.

Success criteria can be more realistic.

Along the lines of the previous comment, and mentioned indirectly in the

survey, detailed species knowledge allows the correct ‘state variable’ to be

monitored (Lindenmayer et al., 2013). Two examples from the survey were

given: ‘If you are aiming for ecological replacement you should be measuring

the function that you are trying to affect rather than the population of the

20

translocated species (you may want to do both)’. Another example given was

where the aim of the project was the recombination of genets to facilitate

pollen (and gene) flow to maximise the potential for fertile seed production.

Therefore, the production of fertile seeds from recombination is the monitoring

target.

(1) Volunteers

The use of volunteers was highlighted by several respondents as an area where

project costs, including monitoring, can be reduced. The use of citizen science

(where the general public participate in scientific research) is increasingly being

recommended to aid in the collection of high quality empirical data (Vallee et al. ,

2004; Willis et al., 2009; Lindenmayer et al., 2013). To test the practicality of this

recommendation, survey respondents were asked their opinion on how effective

volunteers could be in long-term monitoring (assuming appropriate motivation,

training and supervision of volunteers). Respondents thought that volunteers

would be most effective in increasing the awareness of the project, leading to

better conservation outcomes (Figure 2).

Figure 2. Effectiveness of using volunteers in long-term monitoring of flora

translocation projects

Where the use of volunteers was thought to be problematic, was their inability to

suggest where adaptive management is needed and their incapacity to make other

associated observations than those on the monitoring sheet (examples given were:

the presence of pollinator species and visitations; possible new threat processes;

other ecological interactions). Failure to make these monitoring observations has

21

serious consequences. Biodiversity monitoring programs that do not include trigger

points that activate management actions when populations are declining, are thought

to contribute to extinctions at a scale ranging from local through to global

(Lindenmayer et al., 2013).

The question of how effective volunteers can be in monitoring elicited many

additional comments from respondents. Generally, the experience of those using

volunteers has been good and the question of the cost of training compared to the

benefit received produced many salient points. It was highlighted that volunteers

need good training and preferably a paid worker should also be present at the site.

Training must include protocols on the avoidance of the spread of pathogens and

damage to plants and other experimental variables. Training may be expensive so

care needs to be exercised when selecting and accepting volunteers to undertake

project work. In addition, it is important to identify appropriate existing registration

and insurance cover schemes that can take new volunteer groups under their

umbrella, to avoid the difficulties of taking out a new policy and being a disincentive

for particular projects. The goal is for highly trained and committed volunteers that

develop into a long term monitoring resource. It was suggested that the Australian

Network for Plant Conservation (ANPC) could train volunteers e.g. 1-2 day workshop

in monitoring threatened flora. Outsourced training would alleviate the time constraint

problems of government employees.

Volunteers should be engaged with the project to make the exercise

worthwhile for all concerned. One respondent said that given some ownership of the

site, volunteers have a greater capacity for undertaking monitoring and longer-term

commitments to a project than some government agencies. This was especially the

case where the tenure of the volunteer outlasts that of a ‘transient’ paid professional.

To retain the enthusiasm and engagement of volunteers, it was suggested that

support should extend to financial reimbursement such as fuel and other personal

costs. There is perhaps a fine balancing act in giving volunteers too much ownership

of a site and not enough. An example was given of a decision made by a

‘bureaucrat’ that resulted in the loss of volunteers from the system. A disagreement

such as this could stem from either a bad decision from management or a volunteer

disagreeing with the action.

22

Many volunteers currently involved in translocation projects are retired. Age of

volunteers is a consideration because trips to remote sites and those longer than a

couple of days may not be feasible. Retired (or any age demographic) volunteers are

often not available for each field trip. If volunteers are tasked with recording data that

is to be used in experimental analysis, an extra level of variability (operator error /

bias) is introduced into the data. Under these circumstances, ideally the same

volunteer should perform the monitoring each time.

Thirty two translocation projects (assuming that each species represents a

different project) currently have an informal interest group that maintain some

involvement. If citizen science / volunteering is pursued, these projects, in

conjunction with existing programs such as Landcare, Bushcare and Bird atlasing,

should be used as case studies to document and guide citizen science in monitoring.

A final comment from the survey on the subject of volunteers – ‘Community

science is a good thing. Abdicating responsibility is not’.

6. Conclusions

The purpose of this study was to investigate the possibility of formulating general

flora monitoring guidelines by analysing the results of the Flora translocation survey

(2013). Emphasis was on monitoring duration at different life-cycle events. The

results from the survey found that whilst some generalities can be made on the

duration of plant trait measurements, monitoring is context specific and any

guidelines arising from this study need to be individually adapted to each project.

However, where monitoring data is of adequate size for taxonomic groups that share

the same habit, breeding system and other biological traits, it may be worthwhile

pursuing general monitoring protocols with a working group of practitioners / experts.

The working group may then find commonalities between ‘state variables’ that can

improve the efficacy of monitoring, formulate a general monitoring guideline for the

taxa and contribute to a centralized database. Monitoring can be done via

representative sampling (for all life-cycle variables apart from survival) and the use of

volunteers is recommended, albeit with adequate training and supervision.

In addition, to basic plant measurements, there are numerous other variables that

should be monitored to confidently assess the success or otherwise of the

23

translocation project. The importance of these variables is also context dependant,

particularly in regard to the focal species and the site(s), and the survey was

therefore unable to find general commonalities. However, the survey results indicate

that ‘what went wrong’ is one of the most important factors to record and circulate

and that it is important to compare the source and transplant sites. Context

specificity was clearly a problem for many survey respondents when asked to give

their general views on monitoring.

SECTION 2 - Prioritisation of flora translocations

1.1 The need to prioritise

There is an acute need to be able to prioritise candidate species for translocation

projects. This need is present for projects with relatively short-term goals (e.g.

stabilising populations under direct threat from habitat loss) or projects with longer-

term goals (e.g. providing the ability for species to adapt to changing climates by

moving outside their current range – i.e. assisted colonisation). Funds available for

translocation are limited, and therefore, it is important to select candidate species

that have the highest likelihood of successfully established self-sustaining

populations in recipient sites.

1.2 Decision tool for prioritising candidate species

Figure 3 provides a set of guiding questions, arranged in a decision-making

framework, which were developed with close reference to the recommendations for

prioritising flora translocations developed by the Australian Network for Plant

Conservation (Guidelines for the translocation of threatened plants in Australia;

Vallee et al., 2004). The questions are applicable to all forms of translocation,

however, where special consideration may be needed for cases of assisted

colonisation for climate change adaptation additional questions have been provided.

It is recommended that the use of this decision tool is conducted by referring to the

relevant sections of Vallee et al. (2004).

24

Figure 3. Decision tool for prioritising candidate species for translocation

Q1. Is a translocation necessary to ensure the survival of the species? This

question applies in the short-term (<10 years; e.g. acute need to translocate due to

impending loss of habitat from development) or long-term (>100 years e.g. current

climate envelope of species projected to shift entirely outside current range and

species has traits associated with poor ability to adapt to climate change (see PART

A, Section 4)).

YES ………………………………… move to Q2 if: all

alternative strategies for managing the population decline of the

species have already been undertaken.

NO ………………………………… identify appropriate

alternative management action to translocation. Actions may

include: habitat protection/rehabilitation or removal of

threatening processes, or active management involving

manipulations of habitat or biotic processes (see section 2.2.1

Alternatives to translocation in Vallee et al. 2004).

Q2. Is the taxonomic status of the species certain?

YES ………………………………… move to Q3 if: the taxa is

an undisputed, formally described species.

NO ………………………………… clarification should be

sought from experienced taxonomists or population

geneticists. Uncertainty may arise if: inadequate taxonomic

work has been conducted on a species complex, the taxa is a

hybrid, subspecies or variant (see section 2.2.2 Taxonomy in

Vallee et al. 2004).

Q3. Is the distribution of the taxon adequately understood?

YES ………………………………… move to Q4 if the

following has been completed: (1) collation of all known

records for the species via herbaria, museum collections or

published plot-based studies; (2) targeted surveys of known

25

distribution have been conducted to identify potential additional

populations.

NO ………………………………… conduct desktop study

to collate distribution records in conjunction with targeted

surveys in the field (see section 2.2.3 Distribution in Vallee et

al. 2004).

Q4. Are threatening processes understood?

YES ………………………………… move to Q4a if the

following has been completed: a comprehensive assessment

of the threats affecting all remaining populations.

NO ………………………………… conduct a pre-

translocation assessment to identify key threatening

processes and options for mitigation (see section 2.2.4

Threatening processes in Vallee et al. 2004).

Q4a. Can threatening processes be controlled? For many threatened species, the

removal or management of threatening processes may be sufficient to ensure

population stability and may lead to an increase in population size, hence negating

the need for translocation. For assisted colonisation, climate change will be the

primary threatening process and it is assumed that although this cannot be

controlled, predictive tools can be used to assess the feasibility of this conservation

strategy (see PART A, Section 4 for further details).

YES ………………………………… move to Q5 if the

following has been completed: (1) active management or

removal of threatening processes such as weed invasion, or

reinstatement of appropriate disturbance regimes.

NO ………………………………… conduct a pre-

translocation assessment to identify key threatening

processes and options for mitigation (see section 2.2.4

Threatening processes in Vallee et al. 2004).

Q5. Have potential suitable recipient sites been identified?

26

YES ………………………………… move to Q6 if: (1) a number

of potential sites with secure, long-term tenure have been

identified and landholders or custodians approached for pre-

approval, (2) Existing threats to the focal species has been

removed or minimized and preparation (e.g. fencing) has been

factored into the decision, (3) sites representative of future

climate requirements

NO ………………………………… identify potential suitable

sites for translocation (see section 2.2.5 Availability of suitable

recipient sites in Vallee et al. 2004).

Q6. Have you considered the success of any previous translocation

programs? Translocations of taxonomically or functionally similar species can help

to guide the process of designing and implementing new programs.

YES ………………………………… move to Q7 if: a thorough

search of the literature and resources on translocations has

been conducted and, where relevant, primary reports have been

sourced and used to aid in the design of the current project.

(N.B. Appendix 1 of this report lists previous flora translocations

conducted in Australia).

NO ………………………………… identify previous studies

or reports of previous translocations for similar taxa; talk

with experts (see section 2.2.8 Success of past translocation

projects in Vallee et al. 2004).

Q7. Has a source of long-term financial funding been secured to complete all

aspects of the translocation?

YES ………………………………… proceed with translocation

if all questions in this checklist have been answered ‘yes’.

NO ………………………………… identify a secure source of

funding for the design, implementation and monitoring of

the project (see section 2.2.9 Resource availability and cost in

Vallee et al. 2004).

27

1.3 Practitioner and researcher opinions on pre-translocation assessments

As part of the Flora Translocation Survey 2013 (detailed in Section 1) practitioners

and researchers working on flora translocations in Australia were asked their opinion

on the importance of pre-translocation requirements and prioritisation methods.

Three questions were asked in this section and details of responses are given below.

Question 1: Can a translocation proceed before the following parameters are

known for a taxa? (n = 43 respondents). Respondents could nominate one of the

following: Important but translocation can proceed without this information; No

opinion; Translocation should not proceed without this information. Responses are

provided in Table 5.

Table 5. Responses (%) from survey participants regarding factors that should

be known before proceeding with translocation

Proceed

(%)

No opinion

(%)

Should not

proceed

(%)

Reason(s) for in-situ

decline

27.9 2.3 69.8

Disturbance factors

necessary for regeneration

are known and can occur

at the recipient site

39.5 0 60.5

Ecological relationships of

the taxon (incl. mutualisms

and dependent species)

48.8 4.7 46.5

Breeding system 53.5 4.7 41.9

Seed biology and seed

storage responses

62.8 2.3 34.9

Risks of inbreeding

depression and / or

outbreeding depression

65.1 4.7 30.2

28

Proceed

(%)

No opinion

(%)

Should not

proceed

(%)

Dispersal distance of seed

and pollen

72.1 2.3 25.6

The genetic structure

among populations

69.8 6.9 23.3

Population viability

analysis (PVA) outcomes

for source population

79.1 9.3 11.6

The genetic structure

within the existing source

population

83.7 0 16.3

Approximately 70% of respondents think that translocations should not proceed if the

reason(s) for the in-situ decline of the taxa is unknown (Table 5). The second most

important parameter was that disturbance factors that are necessary for regeneration

are known and can occur at the recipient site. Conversely, a large majority of

respondents think that knowledge of the genetic structure within the existing source

population and that population viability analysis outcomes for the source population,

while important, are not necessarily essential for translocations to proceed. As a

summary, ecological knowledge was rated relatively more important than genetic

information.

Question 2: Should a translocation proceed before the following preparatory

measures have been undertaken? (n = 42 respondents).

Respondents could nominate one of the following: Important but translocation can

proceed without this information; No opinion; Translocation should not proceed

without this information.

Table 6. Responses (%) from survey participants regarding preparatory

measures that should be undertaken before proceeding with translocation

29

Proceed

(%)

No opinion

(%)

Should not

proceed

(%)

Existing threats at the recipient site(s)

have been removed or minimized

7.1 0 92.9

Site-preparation requirements have

been factored into the project (e.g.

fencing and weed removal at the

recipient site)

7.1 0 92.9

A Translocation Proposal is prepared

and expertly assessed

19.1 0 81.0

The project has a clear monitoring

structure to assess reasons for

success / failure

23.8 0 76.2

It is determined that the translocated

species will not negatively affect

species at the recipient site(s)

(physically or genetically)

31.0 7.1 61.9

It is reasonably assured that the

recipient site will be legally protected

for the foreseeable future

35.7 0 64.3

Pollinators and dispersal agents are

present at the recipient site

42.9 0 57.1

The performance of the plants at the

recipient site can be compared to a

reference site e.g. the source

population or another wild population

52.4 2.4 45.2

A trial planting/seeding has been

undertaken

57.1 0 42.9

The recipient site(s) reflect

environment conditions expected in

the future

57.1 11.9 31.0

30

Proceed

(%)

No opinion

(%)

Should not

proceed

(%)

Multiple suitable recipient sites are

available

64.3 0 35.7

The translocation is set up as an

experiment to test specific

hypotheses (for example an

experimental factor could be planting

with and without fertilizer)

69.1 11.9 19.1

There is public support for the

translocation

73.8 11.9 14.3

Multiple source populations are

available

76.2 11.9 11.9

93% of respondents nominated that translocations should not proceed unless site

preparation requirements have been factored into the project (e.g. fencing and weed

removal at the recipient site) and that existing threats at the recipients site(s) have

been removed or minimized. Conversely, 76% of respondents think that

translocations can proceed without the availability of multiple source populations,

closely followed by 74% nominating that translocations can proceed without public

support.

Question 3: Please rank the level or urgency of the following situations in

order to prioritise for translocations approval (assuming all factors being

equal). Respondents were asked to rank the level of urgency (most urgent, urgent or

least urgent) for the following situations:

(a) The species is extinct in the wild and ex-situ material is available and can/has

been propagated;

(b) Populations of the species are few, small and declining;

(c) The species’ population(s) are currently stable but has a high risk of extinction

without human intervention;

31

Of the three possible situations, translocations that involve populations of species

that are few, small and declining were thought to be the most urgent (Figure 3).

Populations that are currently stable but have a high risk of extinction without human

intervention were considered to be the least urgent.

Figure 3. Level of urgency for prioritization of translocation approval

Respondents commented that their answers to this question were based on

assumptions such as:

threats are adequately controlled at the new site;

focal species is not naturally rare in the wild;

funding is available;

ex-situ population can continue to be maintained;

confident with climate predictions prior to utilizing ex-situ material;

no ex-situ material for (b);

acceptable systems to translocate into.

32

REFERENCES

Dimond, W. J., & Armstrong, D. P. (2007). Adaptive harvesting of source populations

for translocation: a case study with New Zealand robins. Conservation

Biology, 21, 114-24.

Fischer J. & Lindenmayer D. B. (2000) An assessment of the published results of

animal relocations. Biological Conservation, 96, 1-11.

Godefroid, S., Piazza, C., Rossi ,G., Buord, S., Stevens, A. D., Aguraiuja, R., Cowell,

C., Weekley, C. W., Vogg, G., Iriondo, J. M., Johnson, I., Dixon, B., Gordon,

D., Magnanon, S., Valentin, B., Bjureke, K., Koopman, R., Vicens, M.,

Virevaire, M. & Vanderborght, T. (2011) How successful are plant species

reintroductions? Biological Conservation, 144, 672-82.

Godefroid, S., & Vanderborght, T. (2011) Plant reintroductions: the need for a global

database. Biodiversity and Conservation, 20, 3683-8.

Griffith, B., Scott, J. M., Carpenter, J. W., & Reed, C. (1989) Translocation as a

species conservation tool: status and strategy. Science, 245, 477-80.

IUCN/SSC (2013) Guidelines for Reintroductions and Other Conservation

Translocations. Version 1.0. Gland, Switzerland: IUCN Species Survival

Commission.

Lindenmayer, D. B., Piggott, M. P., & Wintle, B. A. (2013) Counting the books while

the library burns: why conservation monitoring programs need a plan for

action. Frontiers in Ecology and the Environment, 11, 549-55.

Maschinski, J., Albrecht, M. A., Monks, L. & Haskins, K. E. (2012) Center for Plant

Conservation Best Reintroduction Practice Guidelines In Plant reintroduction

in a changing climate: promises and perils, the science and practice of

ecological restoration. Island Press, USA.

Menges E. S. (2008) Restoration demography and genetics of plants: when is a

translocation successful? Australian Journal of Botany 56, 187-96.

Monks, L., Coates, D., Bell, T., & Bowles, M. L. (2012) Determining success criteria

for reintroductions of threatened long-lived plants. In: Plant reintroduction in a

changing climate. Promises and perils (eds J. Maschinski and K. E. Haskins),

Island Press, USA.

Sheean V. A., Manning A. D. & Lindenmayer D. B. (2012) An assessment of

33

scientific approaches towards species relocations in Australia. Austral

Ecology, 37, 204-15.

Vallee L., Hogbin T., Monks L., Makinson B., Matthes M. & Rossetto M. (2004)

Guidelines for the translocation of threatened plants in Australia. Second

Edition. Australian Network for Plant Conservation, Canberra.

Willis, S. G., Hill, J. K., Thomas, C. D., Roy, D. B., Fox, R., Blakeley, D. S., &

Huntley, B. (2009) Assisted colonization in a changing climate: a test‐study

using two UK butterflies. Conservation Letters, 2, 46-52.

Appendix 1 Compilation of established flora translocations in Australia

The transfer of knowledge of prior translocations is important to the success

of future projects. Respondents from the Flora translocation survey (2013)

were asked how the availability of data can be ensured for future workers. No

single preferred repository was identified but a common theme was that it is

preferable to publish data in as many locations as possible, although the

‘grey’ literature was preferred to more formal journals. For some respondents,

this preference arises from the inaccessibility of formal journals and the

potential for misplacement of data/reports by Government Agencies that

change through time. The most often mentioned non-formal venue for

publication was the ANPC's bulletin Australasian Plant Conservation.

Respondents were also asked to provide details of where they have

lodged reports of their projects. Table 1 lists by species, details of published,

“grey” or unpublished reports, websites or locations of reports that contain

information regarding the translocation project. This information was provided

by respondents of the Flora Translocation Survey (2013) and therefore

contains various referencing styles. Table 2 lists vegetation communities and

groups of species for which information on translocations was identified in the

course of this survey and review. In addition, general publications nominated

by the survey respondents, or opportunistically found by the author, are

included at the end of the paper.

This report has not systematically searched for translocation

knowledge in the large body of forestry literature. While experimental forestry

plantings often deal with strongly selected or cross-bred genotypes, this is not

always the case – and even for those the techniques used are highly relevant

for trait selection for future assisted colonisation projects. In addition, the

projects cited below are heavily skewed towards threatened species, whereas

a large body of information on revegetation and restoration exists from which

important principles can be drawn.

34

Details of information sources and translocation details from the Flora Translocation Survey, 2013. Notes pertaining to the table: Species: Name of the species translocated. State: Distribution by State/Territory as per the Atlas of Living Australia website: http://ala.org.au. Conservation status: Survey respondents provided the conservation status or indicated (yes or no) if the species was legislatively listed at the time of translocation as ‘threatened’ (State, Commonwealth &/or IUCN) or on the non-legislative ROTAP list. Habit: Woody plant - short-lived < 10 years; Woody plant - long-lived ≥ 10 years; Non-woody plant – perennial; Non-woody plant – biennial; Non-woody plant – annual Breeding System: Sexual; Asexual; Can be sexual &/or asexual; Other Translocation type: Respondents were provided with a glossary containing descriptions of the following translocation types (IUCN/SSC (2013): Assisted colonisation (Benign introduction; Assisted migration; Managed relocation): the intentional movement and release of an organism outside its indigenous range to avoid extinction of populations of the focal species. For the purposes of this survey, it is used as a conservation strategy for species facing extreme threat from climate change. Ecological replacement (Taxon substitution; Ecological substitutes / proxies / surrogates; Subspecific substitution, Analogue species): the intentional movement and release of an organism outside its indigenous range to perform a specific ecological function. Introduction: the intentional movement and release of an organism outside its indigenous range. Reinforcement (Augmentation; Supplementation; Re-stocking; Enhancement): the intentional movement and release of an organism into an existing population of conspecifics. Reintroduction: the intentional movement and release of an organism inside its indigenous range from which it has disappeared. Method: Transplant method – method of planting: seedling transplant; adult transplant; direct seeding. For the purposes of this survey, the definition of seedling transplant was assumed to cover those plants grown by seed in a nursery or propagated by cuttings. However, this definition was not included in the glossary and some respondents distinguished between the two. Completion: Has the project finished (has formal monitoring ceased)? Group: If the project is finished, is there an informal interest group maintaining some involvement? N.B. Where the species’ translocation details are listed more than once, it is possible that they represent the same projects but note that not all details are the same.

35

http://ala.org.au/

Species State Report/citation details Conservation status

Breeding System

Habit Translocation type

Method Complete Group

Acacia aprica WA Monks L and Coates D (2002) The translocation of two critically endangered Acacia species Conservation Science Western Australia Vol 4(3) 54-61

Critically endangered: State level, Critically Endangered or Endangered: Federal level

Sexual and other (possible selfing)

Woody plant - long-lived ≥ 10 years

Introduction Seedling transplant & direct seeding

No

Acacia pubescens

NSW

1. Moore R. J. and Clements A. (June 1998) Acacia pubescens (Vent.) R. Br. (Downy Wattle) – a threatened species of western Sydney, Australia Conference documentation - Planta Europa – Second European conference on the conservation of Wild Plants, 9-14 June 1998, Uppsala, Sweden 2. Moore, R., Peakall, R. & Clements, A. (1999). Analysis of the genetic diversity of Acacia pubescens: an assessment of clonality and its conservation implications. Prepared for NSW NPWS Central Directorate, Hurstville 3. Unpublished ecological reports to the client, various government departments (inc. OEH) from ecological consultant. Consultants have given talks to various bodies (workshops, seminars, conferences)

Endangered and Vulnerable Yes

Sexual Can be sexual &/or asexual

Woody plant - long-lived ≥ 10 years As above

Reinforcement Ecological replacement

Adult transplant As above

Yes As above

Yes No

Acacia volubilis WA Limited information available from Dept. Parks and Wildlife (WA)

Critically endangered: State level, Critically


Non-woody plant -

Reinforcement Seedling transplant & plants grown

No

36


Breeding System



Endangered or Endangered: Federal level

perennial

from cuttings as well as seed

Acacia whibleyana

SA 1. Jusaitis M (2010) Augmentation of a Whibley Wattle population in South Australia by translocation IUCN "Global Re-Introduction Perspectives. 2010 Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 297-300. 2. Jusaitis M and B Sorensen (1998). Conservation Biology of Acacia whibleyana. Black Hill Flora Centre, Botanic Gardens of Adelaide. 3. Jusaitis M and B Sorensen (2007). Successful augmentation of an Acacia whibleyana (Whibley Wattle) population by translocation. Australasian Plant Conservation 16(1): 23-24 4. Jusaitis M and L Polomka (2008). Weeds and propagule type influence translocation success in the endangered Whibley Wattle, Acacia whibleyana (Leguminosae: Mimosoideae). Ecological Management & Restoration 9: 72-75

CE (IUCN) Sexual Woody plant - long-lived ≥ 10 years

Reinforcement Seedling transplant & direct seeding

Yes

Acanthocladium dockeri

NSW SA

1. Jusaitis M and M Adams (2005). Conservation implications of clonality and limited sexual reproduction in the endangered shrub Acanthocladium dockeri

Yes

Other

Non-woody plant – perennial

Reintroduction

Seedling transplant

No

Yes

37


Breeding System



(Asteraceae). Australian Journal of Botany 53: 535-544. 2. Sharp A, A Clarke, M Jusaitis, A Pieck, P Slattery and D Potter (2010). Translocations of the critically endangered spiny daisy in the Mid-north of South Australia. In PS Soorae (ed), Global Re-introduction Perspectives: 2010. Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 340-344

CE (IUCN)

Asexual

As above

Introduction

As above

Yes

As above

Allocasuarina glareicola

NSW Yes Sexual Woody plant - long-lived ≥ 10 years

Reinforcement Direct seeding

Yes Yes

Allocasuarina portuensis

NSW NPWS reports and recovery plans Yes Sexual Woody plant - long-lived ≥ 10 years

Reinforcement Seedling transplant

Yes Yes

Arachnorchis actensis now: Caladenia actensis

ACT State (E) and Commonwealth (CE)

Sexual Woody plant - long-lived ≥ 10 years

Introduction Seedling transplant but not actually planted yet

No n/a

Artanema fimbriatum

NSW QLD

http://www.rms.nsw.gov.au/roadprojects/projects/pac_hwy/coffs_harbour_ballina/devils_pulpit/public_information.html (construction documentation)

Sexual Non-woody plant -

Introduction Direct seeding

No n/a

38

http://www.rms.nsw.gov.au/roadprojects/projects/pac_hwy/coffs_harbour_ballina/devils_pulpit/public_information.html




Breeding System



perennial

Astelia alpina NSW TAS VIC

No Can be sexual &/or asexual

Non-woody plant - perennial


No Yes

Astelia psychrocharis

NSW VIC




No Yes

Baloskion australe

ACT NSW TAS VIC



Ecological replacement

Adult transplant

No Yes

Banksia anatona

WA Cochrane, J. A.; Barrett, S.; Monks, L.; et al., 2010, Partnering conservation actions. Inter situ solutions to recover threatened species in South West Western Australia, Kew Bulletin, Volume: 65 Issue: 4 Pages: 655-662

Critically Endangered EPBC


Introduction Seedling transplant

No n/a

Banksia brownii WA

1. Cochrane, J. A.; Barrett, S.; Monks, L.; et al., 2010, Partnering conservation actions. Inter situ solutions to recover threatened species in South West Western Australia, Kew Bulletin, Volume: 65 Issue: 4 Pages: 655-662 2. Internal reports for translocation approvals and monitoring reports. Overall reports to be published

Endangered EPBC Threatened State &

Sexual As above


Introduction As above

Seedling transplant As above

No As above

n/a As above

39

http://apps.webofknowledge.com/full_record.do?product=UA&search_mode=GeneralSearch&qid=1&SID=Q24M4gRs9L2euB4e73v&page=1&doc=1









Breeding System



Endangered EPBC

Banksia montana

WA 1. Sarah Barrett, Rebecca Dillon, Anne Cochrane & Leonie Monks 2011 Conservation introduction of a threatened narrow range endemic species, Banksia montana, from the Stirling Range National Park, southern Western Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2011.IUCN Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 220- 223. 2. Cochrane, J. A.; Barrett, S.; Monks, L.; et al., 2010, Partnering conservation actions. Inter situ solutions to recover threatened species in South West Western Australia, Kew Bulletin, Volume: 65 Issue: 4 Pages: 655-662 3. Internal reports for translocation approvals and monitoring reports. Overall reports to be published

Threatened State & Endangered EPBC Critically endangered

Sexual As above




No As above

n/a As above

Banksia nivea ssp. uliginosa

(see Dryandra nivea ssp uliginosa)

Brachyscome diversifolia

ACT NSW QLD SA TAS VIC

Accepted for publication in the upcoming IUCN "Global Re-Introduction Perspectives" due to come out later this year (2013)

E (SA) Sexual Non-woody plant - perennial


No No

40






Breeding System



Brachyscome muelleri

SA 1. Paper accepted for publication in the upcoming IUCN "Global Re-Introduction Perspectives" due to come out later this year (2013). 2. Jusaitis M, L Polomka and B Sorensen (2004). Habitat specificity, seed germination and experimental translocation of the endangered herb Brachycome muelleri (Asteraceae). Biological Conservation 116: 251-266. 3. Jusaitis M, B Sorensen and L Polomka (1998). Conservation Biology of Brachycome muelleri. Black Hill Flora Centre, Botanic Gardens of Adelaide.

CE (IUCN) Sexual Non-woody plant - perennial

Introduction Seedling transplant & Direct seeding

No No

Caladenia actensis See Arachnorchis actensis

Caladenia calcicola

SA VIC

Provided (initially) to research institute Endangered EPBC, listed Vic.

Sexual Non-woody plant - perennial

Reintroduction Seedling transplant

No

Caladenia concolor

NSW SA VIC

ANPC plant conservation journal Regional Reports- personal comments.

Threatened in State and vulnerable in Federal


Reinforcement No Yes

Caladenia hastata

VIC Data unpublished and held with DEPI Endangered EPBC, listed Vic.

Sexual Non-woody plant -


Yes No

41


Breeding System



perennial

Cassinia rugata TAS VIC

Data unpublished and held with DEPI Vulnerable EPBC, listed Vic.



Yes No

Celmisia pulchella

ACT NSW

No Sexual Non-woody plant - perennial


No Yes

Chorizema humile

WA Limited information available from Dept. Parks and Wildlife (WA)

Critically endangered: State, Critically Endangered or Endangered: Federal



Introduction Seedling transplant & Plants grown from cuttings as well as seed

No

Cupaniopsis newmanii

NSW QLD

http://www.tmr.qld.gov.au/~/media/Projects/B/Beechmont%20Road%20Upgrade%20Lower%20Beechmont/beechmontroadupgradecompliancereport.pdf.

Near threatened (NCA)


Reinforcement Seedling transplant from cuttings / some direct seed

No

Darwinia carnea WA Internal reports for translocation approvals and monitoring reports. Overall reports to be published

Critically endangered

Sexual Woody plant - short-lived < 10 years


Yes Yes

42


Breeding System



Darwinia ferricola

WA Dixon B 2010 Translocation of four rare ironstone endemic species onto a pre-mined area at Beenup in SW Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2010.IUCN Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 301- 305. http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation

State, IRP176 as Priority? Endangered under Commonwealth EPBC Act


Reintroduction Seedling transplant of cuttings only

Yes No

Daviesia bursarioides






No

Daviesia cunderdin






No

Dillwynia tenuifolia

NSW Yes Sexual Woody plant - long-lived ≥ 10 years

Reinforcement Direct seeding

Yes Yes

Diuris chryseopsis

ACT NSW SA TAS

ANPC plant conservation journal Regional Reports- personal comments

No Sexual Non-woody plant -

Reinforcement Adult transplant

No Yes

43


Breeding System



VIC perennial

Diuris tricolor NSW QLD

Annual monitoring reports & a paper for publication to a mining company

Yes Sexual Non-woody plant - perennial


Adult transplant

no n/a

Dodonaea subglandulifera

SA Paper accepted for publication in the upcoming IUCN "Global Re-Introduction Perspectives" due to come out later this year (2013)

V (IUCN) Sexual Woody plant - long-lived ≥ 10 years


Yes Yes

Dryandra nivea ssp uliginosa (now Banksia nivea ssp. uliginosa)

WA Dixon B 2010 Translocation of four rare ironstone endemic species onto a pre-mined area at Beenup in SW Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2010.IUCN Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 301- 305; http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation

WA State, IRP 255 as Priority? Endangered under Commonwealth EPBC Act


Reintroduction Yes No

Elaeocarpus williamsianus

NSW 1. NSW NPWS 2.

Yes Endangered

Can be sexual &/or asexual Sexual


Reintroduction Reinforcement /recombination

Seedling transplant Seedling transplant / cuttings

No As above

n/a As above

44


Breeding System



Empodisma minor

QLD No Sexual Non-woody plant - perennial


No Yes

Epacris purpurascens var purpurascens

NSW Unpublished ecological reports to the client, various government departments (inc. OEH) from ecological consultant. Consultants have given talks to various bodies (workshops, seminars, conferences)

Yes Can be sexual &/or asexual



Adult transplant

Yes No

Eremophila resinosa

WA Dixon B Translocation of the resinous Eremophila, from test tube, to a degraded bushland site in the wheatbelt of Western Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2010. IUCN Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 311- 315. http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/eremophila-translocation

State as Priority 3


Reintroduction Tissue culture & some direct seeding

No No

Fontainea oraria

NSW QLD

1. NSW NPWS 2.

Endangered Yes

Sexual As above


Reinforcement / recombination Reinforcement

Seedling transplant / cuttings Seedling transplant

No As above

n/a As above

Gentianella meulleriana

ACT NSW

No Sexual Non-woody


No Yes

45

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/eremophila-translocation




Breeding System



VIC plant - perennial

Grevillea batrachioides






No

Grevillea brachystylis ssp australis

WA Dixon B 2010 Translocation of four rare ironstone endemic species onto a pre-mined area at Beenup in SW Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2010.IUCN Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 301- 305. http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation

WA State as Priority? Endangered under Commonwealth EPBC Act



Grevillea caleyi

NSW Unlublished data on experimental translocation with OEH

Endangered State & Commonwealth


Reinforcement Seedling transplant & seed

No

Grevillea humifusa






No

46

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation


Breeding System



Grevillea iaspicula

ACT NSW

published articles by John Briggs (NSW OEH) in Australian Plant Conservation

TSC Act & EPBC - Endangered



no n/a

Grevillea parviflora ssp. parviflora

NSW

Wyong Shire Council, Donaldson Coal, Centennial Coal

Vulnerable NSW & Commonwealth

Can be sexual &/or asexual


Other - experimental translocation from a development site

Adult transplant

No

Grevillea scapigera

WA 1. Dixon, B. and Krauss, S. (2004).The Grevillea scapigera case study. Chapter 9. In Vallee, L., Hogbin, T., Monks, L., Makinson, B., Matthes, M. and Rossetto, M (2004). Guidelines for the translocation of threatened plants in Australia (2nd. Edn) pp. 65-69. Australian Network for Plant Conservation, Canberra. 2. Krauss, S.L., Dixon, B., and Dixon, K.W. (2002). Rapid genetic decline in a translocated population of the rare and endangered Grevillea scapigera (Proteaceae). Conservation Biology 16: 986-994. 3. Dixon,B. and Krauss, S. (2008). Translocation of the Corrigin grevillea in south Western Australia. Page 229-234 in - Ed. Soorae,P.S. (October 2008) Global re-introduction perspectives: Re-introduction case studies from around the

WA State and Commonwealth as Critically Endangered


Reintroduction Seedling transplant & includes tissue culture

Yes Yes

47


Breeding System



globe.ICUN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE. 4. Dixon, B. and Krauss, S. (2006). The Corrigin Grevillea: 12 years of recovery. Western Wildlife vol.10:2, p.1, 4&5. 5. http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/grevillea-translocation

Grevillea wilkinsonii

NSW 1. ANPC. 2. Partial (and only partially quantitative) results and appraisals have been presented in several conference/forum situations separately and together by John Briggs (OEH NSW) and Bob Makinson (RBG Sydney), and in one of two non-peer reviewed articles, in the (non-public) process of expert interviews for the PAS2 process (2012), and in occasional partially-minuted meetings of the recovery team for the species

TSC Act & EPBC – Endangered ROTAP

Sexual As above

Woody plant - long-lived ≥ 10 years Woody plant - short-lived ≥ 10 years

Reinforcement & Reintroduction Reinforcement

Seedling transplant Seedling transplant / cuttings

No As above

n/a Yes

Haloragis eyreana

SA 1. Jusaitis M and A Freebairn (2010). Habitat manipulation stimulates natural regeneration of Prickly Raspwort (Haloragis eyreana) on Eyre Peninsula (South Australia). Ecological Management & Restoration 11: 81-82.

CE (IUCN) Can be sexual &/or asexual


Reinforcement Seedling transplant & Direct seeding

Yes

48

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/grevillea-translocation

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/grevillea-translocation


Breeding System



2. Jusaitis M and A Freebairn (2011). Trial translocations into edaphically modified habitats enhanced the regeneration of prickly raspwort on Eyre Peninsula, South Australia. In PS Soorae (ed), Global Re-introduction Perspectives: 2011. More case studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 205-209.

Hemigenia ramosissima





Introduction & Reinforcement

Seedling transplant & Plants grown from cuttings as well as seed

No

Lachnagrostis limitanea

SA Yes Sexual Non-woody plant - perennial


Yes Yes

Lambertia fairallii

WA Cochrane, J. A.; Barrett, S.; Monks, L.; et al., 2010, Partnering conservation actions. Inter situ solutions to recover threatened species in South West Western Australia, Kew Bulletin, Volume: 65 Issue: 4 Pages: 655-662

Endangered EPBC



No n/a

Lambertia orbifolia ssp Scott River Plains

WA Dixon B 2010 Translocation of four rare ironstone endemic species onto a pre-mined area at Beenup in SW Australia In PS Soorae (ed), Global Re-introduction Perspectives: 2010.IUCN Additional case-

WA State, IRP 178 as Priority ? Endangered under



49






Breeding System



studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 301- 305. http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/beenup-translocation

Commonwealth EPBC Act

Leionema equestre

SA Jusaitis M (2011). Trial translocations of Leionema equestre on Kangaroo Island, South Australia. In PS Soorae (ed), Global Re-introduction Perspectives: 2011.IUCN More case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 210-214

E (IUCN) Sexual Non-woody plant - perennial


Yes No

Lepidium ginninderrense

ACT 1. ACT Conservation Planning and Research as unpublished reports. 2. 3

ACT and Commonwealth State (E) and Commonwealth (V) Nationally threatened

Sexual As above As above

Non-woody plant – perennial As above As above

Reintroduction - but no populations there Introduction As above

Seedling transplant As above As above

No As above No

n/a n/a

Macadamia integrifolia

NSW QLD

http://www.tmr.qld.gov.au/~/media/Projects/B/Beechmont%20Road%20Upgrade%20Lower%20Beechmont/beechmontroadupgradecompliancereport.pdf.

Vulnerable (EPBC, NCA)



No

Macrozamia pauli-guilielmi

QLD Translocation Performance Report for Macrozamia pauli-guilielmi and Acacia attenuata (Vegetation Matters 2013).

Endangered (Qld NCA, EPBC)

Sexual Woody plant - long-

Reinforcement Adult transplant, Direct

No n/a

50


Breeding System



Qld Department of Transport and Main Roads; Opus; DSEWPAC; Qld Parks and Wildlife Service, Department of Environment and Heritage Protection

lived ≥ 10 years

seeding, Seedling transplant

Marsdenia longiloba

NSW QLD

1.http://www.rms.nsw.gov.au/roadprojects/projects/pac_hwy/port_macquarie_coffs_harbour/nambucca_hds_to_urunga/project_documents/index.html (construction documentation) 2. Nambucca Shire Council

NSW Endangered, Federal Vulnerable Endangered

Sexual Can be sexual &/or asexual

Non-woody plant – perennial As above

Introduction Other

Direct seeding Adult transplant

No Yes

n/a No

Melaleuca deanei

NSW Unpublished ecological reports to the client, various government departments (inc. OEH) from ecological consultant. Consultants have given talks to various bodies (workshops, seminars, conferences)

Yes Can be sexual &/or asexual



Adult transplant

Yes No

Montia australasica

ACT NSW SA TAS VIC WA




No Yes

Muehlenbeckia tuggeranona

ACT 1. ACT Conservation Planning and Research as unpublished reports

ACT and Commonwealth

Sexual also possibly asexual but not confirmed


Reinforcement/Reintroduction - but no populations there Introduction

Adult transplant

No As above

n/a

51

http://www.rms.nsw.gov.au/roadprojects/projects/pac_hwy/port_macquarie_coffs_harbour/nambucca_hds_to_urunga/project_documents/index.html





Breeding System



2. Preliminary results unpublished, ACT Govt

State (E) and Commonwealth (E)

Can be sexual &/or asexual

As above

Seedling transplant

Oreobolus pumilio

NSW TAS VIC



No Yes

Persoonia micranthera

WA 1. Internal reports for translocation approvals and monitoring reports. Overall reports to be published 2.

critically endangered Endangered EPBC

Sexual As above




No No

n/a

Persoonia pauciflora

NSW Criticlly endangered


Not yet

Phebalium glandulosum

NSW QLD SA VIC

1. Jusaitis M (1991). Endangered Phebalium (Rutaceae) species return to South Australia. Re-introduction News No. 3: 4. 2. Jusaitis M (1991). Micropropagation of endangered Phebalium (Rutaceae) species in South Australia. Botanic Gardens Micropropagation News 1: 43-45.

E (SA) Sexual Non-woody plant - perennial


Yes Yes

52


Breeding System



3. Jusaitis M (1996). Experimental translocations of endangered Phebalium spp. (Rutaceae) in South Australia: An update. Re-introduction News No. 12: 7-8. 4. Jusaitis M (2000). The Ecology, Biology and Conservation of Threatened Phebalium Species in South Australia. Plant Biodiversity Centre, South Australia. 5. Jusaitis M (2011). Translocation of the desert Phebalium to Yookamurra Sanctuary, South Australia. In PS Soorae (ed), Global Re-introduction Perspectives: 2011. More case studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 215-219

Pimelea spicata

ACT NSW



Yes Yes

Pimelea spinescens ssp spinescens

VIC Mueck, S. 2000. Translocation of Plains Rice-flower (Pimelea spinescens ssp. spinescens), Laverton, Victoria. Ecol. Man & Restor. 1(2): 111- 116.

Critically endangered: EPBC Act and endangered: Victoria



Yes No

Prasophyllum sp Wybong

NSW (not shown in ALA)

Annual monitoring reports & a paper for publication held by a mining company



Adult transplant

no n/a

Prostanthera eurybioides

SA Jusaitis M (2010). Enhancement of Monarto Mintbush populations in South Australia by translocations. In PS Soorae (ed), IUCN

CE (IUCN) Sexual Woody plant - long-


Yes Yes

53


Breeding System



"Global Re-Introduction Perspectives: 2010. Additional case-studies from around the globe. IUCN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE, pp 306-310

lived ≥ 10 years

Psychrophyla introloba

NSW VIC




No Yes

Pterostylis arenicola

NSW SA VIC

E (SA) Can be sexual &/or asexual



No Yes

Pterostylis basaltica

VIC Data unpublished and held with DEPI Endangered EPBC, listed Vic.



Yes No

Ranunculus gunnianus


Reinforcement

Seedling transplant

No Yes

Ranunculus millanii

ACT NSW VIC



No Yes

Ranunculus pimpinellifolius

ACT NSW TAS VIC

No Sexual Non-woody plant -


No Yes

54


Breeding System



perennial

Rutidosis leptorrhynchoides

ACT NSW VIC

1. ACT Conservation Planning and Research as unpublished reports. 2.

ACT and Commonwealth Nationally threatened

Sexual As above

Woody plant - long-lived ≥ 10 years Non-woody plant - perennial

Reintroduction - but no populations there Introduction

Direct seeding & Seedling transplant As above

Yes No

Yes n/a

Senna acclinis NSW QLD

Stanwell Corporation Limited; Qld Parks and Wildlife Service, Department of Environment and Heritage Protection; Vegetation Matters

Rare (Qld Nature Conservation Act)


Reinforcement Adult transplant, Direct seeding, Seedling transplant

Yes

Swainsona recta

ACT NSW VIC

1 .ACT Conservation Planning and Research as unpublished reports 2. ANPC ?

ACT and Commonwealth TSC Act & EPBC – Endangered

Sexual As above

Woody plant - long-lived ≥ 10 years Non-woody plant – perennial

Reintroduction - but no populations there Reintroduction

Adult transplant Seedling transplant & Direct seeding

No Yes

No

55


Breeding System



3 Preliminary results unpublished, ACTEW 4.

Endangered (or threatened) under Commonwealth, NSW, ACT and Vic legislation State (E) and Commonwealth (E)

As above As above

As above As above

As above Introduction

Adult transplant Seedling transplant

No No

Will be n/a

Symonanthus bancroftii

WA 1. Bunn, E. and Dixon,B. (2008). Re-introduction of the endangered Bancroft’s Symonanthus in Western Australia. Page 224-228 in- Ed. Soorae,P.S. (October 2008) Global re-introduction perspectives: Re-introduction case studies from around the globe.ICUN/SSC Re-introduction Specialist Group, Abu Dhabi, UAE. 2. Qigang Ye, Eric Bunn, Siegfried L. Krauss, Kingsley W. Dixon 2007 Reproductive success in a reintroduced population of a critically endangered shrub, (Solanaceae) Australian Journal of Botany 55(4) 425–432. 3.http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/symonanthus-translocation

WA State and Commonwealth as Critically Endangered


Reintroduction Tissue culture

Yes Yes

Synaphea quarztitica

WA (not show

Limited information available from Dept. Parks and Wildlife (WA)

Endangered: State level, Critically

Can be sexual

Non-woody plant -

Introduction Tissue culture

No

56

http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/symonanthus-translocation




Breeding System



n in ALA)

Endangered or Endangered: Federal level

&/or asexual

perennial

Tetratheca juncea

NSW 1. Wyong Shire Council, Donaldson Coal, Centennial Coal 2. Assessment reports submitted by EFS to Wyong Shire Council and the developer involved. Documents can be supplied if required 3. Great lakes Council

Vulnerable NSW & Commonwealth Yes Vulnerable

Can be sexual &/or asexual As above As above

Non-woody plant - perennial As above As above

Other - experimental translocation from a development site Ecological replacement Other

Adult transplant As above Bulk topsoil

No Yes No

No

Verticordia albida






No

Verticordia lindleyi ssp lindley

WA http://www.bgpa.wa.gov.au/science/biodiversity-and-extensions/verticordia-translocation

WA State as Priority 3.


Reintroduction Yes Yes

Wilsonia backhousei

NSW SA

Sullivan M et al. Present to Ecological Soc in NZ

Yes Sexual Woody plant -


Yes Yes

57


Breeding System



TAS VIC WA

long-lived ≥ 10 years

Xanthorrhoea glauca

ACT NSW QLD VIC

Abigroup (Lend Lease); North Burnett Regional Council; Qld Parks and Wildlife Service, Department of Environment and Heritage Protection; Vegetation Matters

Type ! restricted (Qld NCA)


Other - Conservation translocation

Adult transplant

No n/a

Zieria prostrata NSW http://www.environment.nsw.gov.au/resources/nature/recoveryplanFinalZieriaProstrata.pdf

Endangered Sexual Woody plant - long-lived ≥ 10 years


Yes No

,

58

Table 2. Details of published, “grey” or unpublished reports, websites or locations of reports that contain information on flora translocations, listed by groups

Taxon Report/citation details Cooks River Castlereagh Ironbark Forest community

Unpublished ecological reports to the client, various government departments (inc. OEH) from ecological consultant. Consultants have given talks to various bodies (workshops, seminars, conferences).

Cumberland Plain Woodland community


Orchids - various Unpublished ecological reports to the client, various government departments (inc. OEH) from ecological consultant. Consultants have given talks to various bodies (workshops, seminars, conferences).

Sydney Sandstone Ridgetop Woodland

http://www.dixonsand.com.au/environment_frame.htm (Annual Environmental Monitoring Reports)

Various non-threatened Western Sydney species


General/other publications Cochrane, Anne; Monks, Leonie 2006 : Seedbanks and the conservation of threatened species In Eds: Sweedman, L; Merritt, AUSTRALIAN SEEDS: A GUIDE TO THEIR COLLECTION, IDENTIFICATION AND BIOLOGY Pages: 61-66 Dixon, B. (2005). Managing Phytophthora cinnamomi on a rare ironstone multi-translocation site in Western Australia. Australasian Plant Conservation vol. 13:4, 18-19. Dixon B (2010) Controlling weeds on translocation sites, strategies, solutions and probable short term costs to the environment. Abstracts< Australian Network for Plant Conservation, 8th National Conference, Perth. Jusaitis M (2012). Serendipity during long-term monitoring of translocation trials. Australasian Plant Conservation 20(3): 8-10. Jusaitis M (1993). Conservation studies on four endangered plants from Kangaroo Island, South Australia. Final report. Black Hill Flora Centre, Botanic Gardens of Adelaide. Jusaitis M and B Sorensen (1994). Conservation studies on endangered plant species from South Australia's Agricultural regions. Black Hill Flora Centre, Botanic Gardens of Adelaide. Jusaitis M (1997). Experimental translocations: Implications for the recovery of endangered plants. In DH Touchell, KW Dixon, AS George and AT Wills (eds), Conservation into the 21st Century. Proceedings of the 4th International Botanic Gardens Conservation Congress, Perth, Western Australia. Kings Park and Botanic Garden, Western Australia, pp 181-196.

59

http://www.dixonsand.com.au/environment_frame.htm

http://apps.webofknowledge.com.simsrad.net.ocs.mq.edu.au/full_record.do?product=UA&search_mode=GeneralSearch&qid=6&SID=Y2pdLgtxoTObPMSiCDb&page=1&doc=4

http://apps.webofknowledge.com.simsrad.net.ocs.mq.edu.au/full_record.do?product=UA&search_mode=GeneralSearch&qid=6&SID=Y2pdLgtxoTObPMSiCDb&page=1&doc=4

Jusaitis M and J Val (1997). Herbivore grazing: an important consideration in plant translocations. Re-introduction News No. 13: 11-12. Jusaitis M and J Val (1997). Success of plant translocations can be improved by optimising choice of propagule. Re-introduction News No. 13: 10-11. Jusaitis M (2005). Translocation trials confirm specific factors affecting the establishment of three endangered plant species. Ecological Management & Restoration 6: 61-67.

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