HERBACEOUS VEGETATION RESPONSE PATTERNS:
SPECIES VS FUNCTIONAL DIVERSITY
Van Staden, Nanette¹, Siebert, F.¹, Siebert, S.J.¹,
Swemmer, A.M.² & Komape, D.¹
¹Unit for Environmental Sciences and Management,
North-West University
²SAEON, Ndlovu Node, Phalaborwa
INTRODUCTION
• Plant species diversity
— a proxy for conservation efforts & management practices (Fraser et al., 2014)
— limitations i.t.o. disturbance effects on ecosystem functioning &
stability (Lacroix & Abbadie, 1998; Mouillot et al., 2013; Mori et al., 2013)
• Species functional diversity
— useful tool to determine ecosystem function (Dı́az & Cabido, 2001; Mayfield et al.,
2005; Zhang et al., 2012; Kotschy, 2013)
• Plant traits
— explore prevailing relationships between species & their
environment (Wesuls et al., 2012)
— reliable indicators of adaptation (Dı́az & Cabido, 2001; Moretti & Legg, 2009; Pérez-
Harguindeguy et al., 2013)
— better predictors of ecosystem processes (Díaz et al., 1999; Pérez-Harguindeguy et al.,
2013)
INTRODUCTION
• The combination of species & functional diversity
— should provide a better understanding semi-arid savanna ecosystem
functionality
— will ultimately lead to improved management & conservation
practices (Dı́az & Cabido, 2001; Zhang et al., 2012; Moretti et al., 2013)
— the key to understand resilience in disturbed environments (Lavorel et al.,
1998)
— may assist decision-making to safeguard ecosystem services (Dı́az &
Cabido, 2001; McIntyre & Lavorel, 2007; Zhang et al., 2012; Moretti et al., 2013)
• Which measure of diversity best explains herbaceous response patterns
to land-use changes in a semi-arid savanna ecosystem?
Study area
The semi-arid Phalaborwa Timbavati Mopaneveld
— well conserved within the Kruger National Park & other nature
reserves
— classified as ‘Least threatened’ (Mucina & Rutherford, 2006)
Phalaborwa region exposed to
— urbanisation, agricultural & mining practices
— responsible for transformation of natural Mopaneveld outside
protected areas (Mucina & Rutherford, 2006; Rutherford et al., 2012; Davis et al., 2013)
— how well can Mopaneveld vegetation absorb such disturbances?
Lulekani: Communal area
Pompeye: Strip mines
Pompeye: Protected Mopaneveld
Land use types:
Strip mines >30 years & strip
mines <10 years (Pompeye
quarts strip mine).
Protected area (Pompeye).
Communal rangelands &
communal old fields
(Lulekani).
PERMANOVA = significance (p<0,05)
Species richness
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Marg
alef
rich
ness
(1
m²)
0
2
4
6
8
10
12
14
16
18
20
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
to
tal sp
eci
es
rich
ness
(1
m²) Protected area
*
*
— Higher on communal rangelands & –old fields (Shackleton, 2000; Otto et al., 2006;
Cramer et al., 2008; Rutherford & Powrie, 2011; Rutherford & Powrie, 2013)
—Strip mines>30 years surrounded by protected areas recovered well
—Lower on strip mines<10years
Diversity
*
*
0
0.5
1
1.5
2
2.5
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Sh
an
no
n D
ivers
ity
(1m
²)
Protected area
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Sim
pso
n d
ivers
ity
(1m
²)
— Strip mines<10 years significantly lower, deteriorated & loss of
ecosystem function= diversity-stability & insurance hypothesis (Chapin et
al., 2000; McCann, 2000; Hautier et al., 2015)
— More diverse ecosystems = more stable (Allan et al., 2011)
Evenness
* *
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Pie
lou
's E
ven
ness
(1
m²)
Protected area
— Communal old fields & strip mines < 10 years deviated
significantly from protected areas
— Certain herbaceous species dominated
— Responds rapidly & sensitive to anthropogenic disturbances (Chapin
et al., 2000; Wittebolle et al., 2009; Crowder et al., 2010)
Trait richness
*
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Marg
alef
trai
t ri
chn
ess
(1
m²)
*
15
16
17
18
19
20
21
22
23
24
25
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
to
tal tr
ait r
ich
ness
(1
m²)
Protected area
— No loss of traits despite loss of species
— Available resources used & species take advantage of
environmental conditions = buffering effect (Mason et al., 2005)
— Margalef trait richness indicated that communal old fields
& strip mines younger than 10 years deviated significantly
Trait diversity
0
0.5
1
1.5
2
2.5
3
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Sh
an
no
n tra
it d
ivers
ity
(1m
²)
Protected area
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Sim
pso
n tra
it d
ivers
ity
(1m
²)
— Maintained & no clear patterns observed (Flynn et al., 2013; Mandle &
Ticktin, 2015)
— No significant deviation from protected area
Trait evenness
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Communal
rangelands
Communal
old fields
Strip mines
>30yrs
Strip mines
<10 yrs
Mean
Pie
lou
tra
it e
ven
ness
Protected area
— No significant deviation
— Traits evenly distributed
— All parts of niche occupied and utilised (Mason et al., 2005)
— High evenness of traits contribute to same ecosystem function
— Functional redundant species (Wittebolle et al., 2009) & trait-based
redundancy (Mori et al.,2013)
Species
• Communal rangelands, old fields & strip mines>30years compared favorably
• Strip mines<10years deviated significantly from protected areas
Evenness
• Old fields & strip mines<10 years dominated by certain species (deviated from protected areas)
Traits
• No significant deviation
• Communal- and strip mine practices compares favorably to protected areas
Diversity
measures
Species richness decline & random loss of species with respect to
traits
Functional diversity insensitive to land use & remain constant =
high redundancy levels ecosystem functioning at high levels (Flynn et al., 2013)
Forbs vs. grasses
0
2
4
6
8
10
12
14
16
18
Protected area Communal
rangelands
Communal old
fields
Strip mines>30yrs Strip mines<10yrs
To
tal h
erb
aceo
us
ind
icat
or
speci
es
Grass Forbs
Grass:Forb
1:2
Grass:Forb
1:4
Grass:Forb
1:8
Grass:Forb
1:5
Grass:Forb
2:1
Dominant plant functional groups & their traits
Grass:forb ratio
1
2
3
4
5
Protected area
1
2
3
4
5
Communal rangelands
1
2
3
4
5
Communal old fields
1
23
4
5
Strip mines > 30 years
1
2
3
4
5
Strip mines < 10 years
Dominant plant functional groups & their traits
Grass:forb ratio
•Weedy perennials
•Erect growth form
•Non-clonal
•Unassisted dispersal
•Sun tolerant
•G:F ratio =1:2
PFG 3
•Non-weedy perennials
•Erect growth form
•Non-clonal
•Unassisted dispersal
•Sun tolerant
•G:F ratio =1:2
PFG 4
•Non-weedy annuals
•Erect growth form
•Non-clonal
•Unassisted dispersal
•Sun tolerant
•G:F ratio =1:4
PFG 5
CONCLUSION
• Include both species & functional diversity measures
• Functional diversity measures better explain ecosystem resilience to
disturbances such as land use change
• Forbs fulfil important ecological role, contributing to redundancy &
resilience at species as well as group level
ACKNOWLEDGEMENTS
• South African Observation Network (SAEON; Ndlovu
Node)
• Palabora Mining Company (PMC) & field rangers
• Unit for Environmental Sciences and Management, North-
West University & North-West University for additional
financial support
• Dedicated fieldworkers
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