Lake Wyara Soil Indicators of Queensland Wetlands · Soil Indicators of Queensland Wetlands...
Transcript of Lake Wyara Soil Indicators of Queensland Wetlands · Soil Indicators of Queensland Wetlands...
Soil
Ind
icat
ors
of Q
uee
nsla
nd W
etla
nds Lake Wyara
Study AreaLake Wyara is located in Currawinya National Park, approximately 120 kmsouth west of Eulo, South-West Queensland.
The area is an aggregation of large and small ephemeral lakes, claypans and drainage depressions1. Lake Numalla is part of the Currawinya Lakes, which are on the Ramsar List of Wetlands of International Importance.
At the time of sampling the lake was dry. Lake Wyara is an example of a semi-arid saline lake in the Mulga Lands Bioregion
Climate2
0
100
200
300
400
500
600
700
800
900
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov DecMonth
Rai
nfal
l-Eva
pora
tion
(mm
)
0
5
10
15
20
25
30
35
40
Tem
pera
ture
(Deg
.C)
Rain Evap
Temp (min) Temp (max)
The study area is situated within a semi-arid climatic region with no distinct wet and dry season. Evaporation exceeds rainfall in every month. The average annual rainfall for the area is 271 mm.
Landform and Inundation
Shallow salt lake on gently undulating sand plainsSaline permanently inundated lake from overland flow
Soils3 Hydrosols and Kandosols
Vegetation4 Halosarcia spp. open succulent shrubland on alluvium (RE 6.3.10)6.3.10)
Geology5 Quaternary alluvium
Disturbance No effective disturbance except grazing by hoofed animals
Soil
In
dic
ator
s of
Q
ue
ensl
and
W
etla
nd
s Location GDA94 • MGA Coordinates : 230071 E, �817384 N, Zone 55 • Lat/Long : -28.74273 S, 144.23�05 E
Landscape Diagram
Site 4
Saturated zone
Site 1
Outer zone
Site 2Site 3
Transition zone
Salt crystals on soil surface 700m
Footslope of first lunette
Complex of lunettes moving out of lakeSparse shrubland and bead weedDry salt lake
Sand ridge
Soil ProfilesSite 158Site 157Site 156Site 155
0.02 mA1
0.05 m
0.1 m0.13 m
0.2 m
A21
B?
B?
0.3 m
0.� m
B?
B?
B?
B?
0.01 mA11
0.1 m
A12
0.55 m
0.9 m
B21
B22
0.08 mA
0.15 m2A11
0.4 m
0.5 m
2A12
2C
0.8 m
2C
0.1 m
A1
0.5 m
0.� m
A2e
0.8 m
0.9 m
2A1
2A3
2B2
Soil
In
dic
ator
s of
Q
ue
ensl
and
W
etla
nd
s Soil Indicators Present (within 0.3 m of surface)
Indicator� Site 155 Site 156Organic materials and organic carbon (OC)*
No organic materials OC: 1.98%
No organic materials OC: 0.23%
Matrix colour Greenish grey Pinkish grey to greenish grey
Chroma (thickness of layer)**
Present (0.25 m� Present (0.3 m�
Mottles and Segregations Common <5 mm distinct yellow mottles Many 5-15 mm prominent red mottles Few 5-15 mm prominent yellow mottles Few 5-15 mm distinct brown mottles
Not present
Depth to groundwater 0.� m Not present
Ferruginous root channel and pore linings
Not present Present
pH*7 Strongly alkaline Strongly alkaline
Texture Light clay Clay loam to light clay
Acid sulfate material Present Not present
Electrical Conductivity (EC)7
Brine (Seawater� Highly saline
Indicator� Site 157 Site 158Organic materials and organic carbon (OC)*
No organic materials OC: 0.14%
No organic materials OC: 0.09%
Matrix colour Greyish brown to grey Light grey
Chroma (thickness of layer)**
Present (0.3 m� Present (0.2 m�
Mottles and Segregations Very few <5 mm faint brown mottles Very few <2 mm saline crystals
Not present
Depth to groundwater Not present Not present
Ferruginous root channel and pore linings
Not present Not present
pH*7 Strongly alkaline Strongly alkaline
Texture Loamy sand to light clay Sand
Acid sulfate material Not present Not present
Electrical Conductivity (EC)7
Moderately saline Non saline
*Organic carbon % (Dumas method) and pH taken from surface (0-0.1 m) **Chroma value is less than or equal to 2
Summary of Field ObservationsOrganic carbon content increases moving into the saturated zone, whilst there is no visible
accumulation of plant materials this can be attributed to the presence of microscopic algaePresence of faint, distinct and prominent mottling indicative of water fluctuation throughout the
soil profile in the saturated and transition zoneGley colours (Figure 1) and sulfidic materials confirmed by laboratory testing indicate a permanently
reduced environment in the saturated zoneThe average pH in the saturated zone is mildly alkaline however there is a layer (between 0.15 and
0.25 m) where the pH is strongly acidic, this could be from the oxidation of sulfidic materials
•
•
•
•
Figure 1. Gley soil colours
When a soil is exposed to an anaerobic environment ferric iron (Fe III) in the soil is quickly reduced to the colourless and
mobile ferrous Iron (Fe II)
This gives the soil a characteristic grey/green/blue colour called “gley”
Soil Indicators of Queensland WetlandsSo
il M
orph
olog
y
Site
155
Clas
sifi
cati
on
Aust
ralia
n So
il Cl
assi
fica
tion
Su
lfidi
c, H
yper
salic
Hyd
roso
lLa
ndfo
rm E
lem
ent
Play
aM
orph
olog
ical
Typ
e Fl
at
Hor
izon
Dep
th (
m)
Boun
dary
Text
ure
Colo
urM
ottl
esCo
arse
Fr
agm
ents
Stru
ctur
eSe
greg
atio
nsCo
nsis
tenc
e
A10
to .
02 s
harp
to
light
cla
yye
llow
ish
brow
n (1
0YR5
4�
none
none
mas
sive
none
-
A21
.02
to .
05-
light
cla
ybr
own
(10Y
R53�
co
mm
on (
10-2
0%)
fine
(<5
mm
� di
stin
ct y
ello
w
mot
tles
none
mas
sive
none
-
B?.0
5 to
.1-
light
cla
yda
rk g
reen
ish
grey
(10
GY4
1�
none
none
mas
sive
none
-
B?.1
to
.13
-lig
ht c
lay
light
gre
enis
h gr
ey (
10G
Y71�
man
y (2
0-50
%� m
ediu
m
(5-1
5 m
m�
prom
inen
t re
d m
ottl
es,
few
(2-
10%�
m
ediu
m (
5-15
mm
� pr
omin
ent
yello
w m
ottl
es
few
(2-
10%�
an
gula
r qu
artz
sm
all p
ebbl
es
(2-�
mm
�
mas
sive
none
-
B?.1
3 to
.2
-lig
ht c
lay
gree
nish
gre
y (1
0GY�
1�fe
w (
2-10
%� m
ediu
m
(5-1
5 m
m�
dist
inct
bro
wn
mot
tles
none
mas
sive
none
-
B?.2
to
.3-
light
cla
ygr
eeni
sh g
rey
(10G
Y51�
none
few
(2-
10%�
an
gula
r qu
artz
sm
all p
ebbl
es
(2-�
mm
�
mas
sive
none
-
B?.3
to
.�-
light
cla
ylig
ht g
reen
ish
grey
(10
GY7
1�
very
few
(<2
%) fi
ne
(<5
mm
� fa
int
brow
n m
ottl
es
very
few
(<2
%�
angu
lar
quar
tz
smal
l peb
bles
(2
-� m
m�
mas
sive
none
-
B?.�
to
.7-
light
cla
ylig
ht g
reen
ish
grey
(10
GY8
1�
none
none
mas
sive
none
-
Soil Indicators of Queensland Wetlands
Site
156
Clas
sifi
cati
on
Aust
ralia
n So
il Cl
assi
fica
tion
H
aplic
, H
yper
salic
Hyd
roso
lLa
ndfo
rm E
lem
ent
Foot
slop
eM
orph
olog
ical
Typ
e M
idsl
ope
Hor
izon
Dep
th (
m)
Boun
dary
Text
ure
Colo
urM
ottl
esCo
arse
Fra
gmen
tsSt
ruct
ure
Segr
egat
ions
Cons
iste
nce
A10
to .
01 s
harp
to
clay
loam
, sa
ndy
pink
ish
grey
(7
.5YR
�2�
none
none
stro
ng 1
0-20
mm
pl
aty
none
-
A12
.01
to .1
cle
ar t
ocl
ay lo
amgr
ey (
10YR
�1�
none
few
(2-
10%�
sub
angu
lar
quar
tz s
mal
l peb
bles
(2
-� m
m�
mod
erat
e 5-
10 m
m p
laty
com
mon
(10
-20%
) fin
e (<
2 m
m�
ferr
ugin
ous
root
lini
ngs
-
B21
.1 t
o .5
5 g
radu
al t
olig
ht c
lay
light
gre
enis
h gr
ey (
10Y7
1�
none
none
mas
sive
none
-
B22
.55
to .9
light
cla
ygr
eeni
sh g
rey
(10Y
�1�
none
none
mas
sive
none
-
Site
157
Clas
sifi
cati
on
Aust
ralia
n So
il Cl
assi
fica
tion
H
aplic
, H
yper
salic
Hyd
roso
lLa
ndfo
rm E
lem
ent
Lune
tte
Mor
phol
ogic
al T
ype
Sim
ple
slop
eH
oriz
onD
epth
(m
)Bo
unda
ryTe
xtur
eCo
lour
Mot
tles
Coar
se
Frag
men
tsSt
ruct
ure
Segr
egat
ions
Cons
iste
nce
A10
to .
08 a
brup
t to
loam
y sa
ndgr
eyis
h br
own
(2.5
Y52�
no
neno
nem
assi
veno
ne-
2A11
.08
to .1
5 c
lear
to
light
cla
ygr
eyis
h br
own
(2.5
Y52�
ve
ry f
ew (
<2%�
fin
e (<
5 m
m)
fain
t br
own
mot
tles
none
mod
erat
e 5-
10 m
m
suba
ngul
ar b
lock
y
very
few
(<2
%) fi
ne
(<2
mm
� sa
line
crys
tals
-
2A12
.15
to .
4 c
lear
to
light
cla
ylig
ht b
row
nish
gre
y (2
.5Y�
2�no
neno
new
eak
5-10
mm
su
bang
ular
blo
cky
very
few
(<2
%) fi
ne
(<2
mm
� sa
line
crys
tals
-
2C.4
to
.5 c
lear
to
sand
y lig
ht
clay
light
bro
wni
sh g
rey
(2.5
Y�3�
no
neno
nem
assi
veno
ne-
2C.5
to
.8-
clay
loam
light
bro
wni
sh g
rey
(2.5
Y�2�
no
neno
nem
assi
veco
mm
on (
10-2
0%)
fine
(<2
mm
� sa
line
crys
tals
-
Soil Indicators of Queensland Wetlands
Site
158
Clas
sifi
cati
on
Aust
ralia
n So
il Cl
assi
fica
tion
Bl
each
ed,
Mes
otro
phic
, Ye
llow
Kan
doso
lLa
ndfo
rm E
lem
ent
Play
aM
orph
olog
ical
Typ
eFl
at
Hor
izon
Dep
th (
m)
Boun
dary
Text
ure
Colo
urM
ottl
esCo
arse
Fr
agm
ents
Stru
ctur
eSe
greg
atio
nsCo
nsis
tenc
e
A10
to .1
cle
ar t
osa
ndlig
ht b
row
nish
gre
y (2
.5Y�
3�
none
none
sing
le g
rain
none
-
A2e
.1 t
o .5
cle
ar t
osa
ndlig
ht g
rey
(2.5
Y72�
no
neno
nem
assi
veno
ne-
2A1
.5 t
o .�
gra
dual
to
loam
y sa
ndda
rk g
reyi
sh b
row
n (2
.5Y4
3�
none
none
mas
sive
none
-
2A3
.� t
o .8
gra
dual
to
light
san
dy
clay
loam
grey
ish
brow
n (1
0YR5
2�
none
none
mas
sive
none
-
2B2
.8 t
o .9
-cl
ay lo
am,
sand
y-
none
none
mas
sive
none
-
Soil
Chem
istr
y
Site
Dep
th (
m)
pH*
EC dS/m
Cl mg/
kgN
O3-
Nm
g/kg
TC**
%TN
**%
Ca meq
/100
gM
gm
eq/1
00g
Na
meq
/100
gK m
eq/1
00g
ESP
%CE
Cm
eq/1
00g
155
0.00
-0.1
08.
5�2
.511
4000
81.
980.
195.
715.
4115
.�2.
�5�2
.425
0.20
-0.3
0�.
�34
.951
000
110.
520.
0�3.
452.
�217
.32.
8557
.730
0.40
-0.5
08.
131
.945
300
140.
27<0
.03
�.37
3.01
15.2
2.52
58.5
2�
15�
0.00
-0.1
08.
921
3030
09
0.23
<0.0
32.
�51.
974.
381.
0840
11
0.20
-0.3
08.
517
.925
800
50.
19<0
.03
2.�2
2.3�
122.
11�3
.219
0.40
-0.5
08.
�13
.218
300
30.
25<0
.03
2.88
1.89
8.5
1.39
5�.7
15
157
0.00
-0.0
88.
82.
4427
202
0.14
<0.0
31.
850.
380.
530.
4513
.24
0.08
-0.1
58.
73.
5540
00<1
0.21
<0.0
33.
540.
782.
470.
9827
.49
0.20
-0.3
08.
��.
5483
705
0.28
<0.0
3�.
121.
�7.
231.
8742
.517
0.40
-0.5
08.
59.
1412
200
20.
54<0
.03
7.71
1.82
10.4
2.1�
43.3
24
158
0.00
-0.1
09
0.12
853
0.09
<0.0
30.
718
<0.3
10<0
.091
0.11
3<3
0.20
-0.3
08.
�0.
02<2
01
<0.0
5<0
.03
0.87
3<0
.310
<0.0
910.
123
<3
0.40
-0.5
09.
10.
1712
5<1
<0.0
5<0
.03
0.54
7<0
.310
0.11
0.12
3.7
<3
*Aqu
eous
1:5
**To
tal c
arbo
n an
d to
tal n
itro
gen
Soil
In
dic
ator
s of
Q
ue
ensl
and
W
etla
nd
s
0
0.1
0.2
0.3
0.4
0.5
0 0.5 1
E C (d/S /m )
Dept
h (m
)
0
0.1
0.2
0.3
0.4
0.5
0 10 20 30 40 50 60
E C (d/S /m )
Dept
h (m
)
0
0.1
0.2
0.3
0.4
0.5
0 5 10 15 20 25
E C (d/S /m )
Dept
h (m
)
0
0.1
0.2
0.3
0.4
0.5
0 5 10 15
E C (d/S /m )
Dept
h (m
)
References1. DEWHA (2008). Australian Wetlands Database. [online]. Available at http://www.environment.gov.au/water/publications/environmental/wetlands/database/ [accessed 21/08/08].
2. Queensland Department of Natural Resources and Water (2008). SILO [online]. Available at http://www.longpaddock.qld.gov.au/silo/ [accessed 5/11/2007].
3. Isbell RF (2002). The Australian Soil Classification. CSIRO Publishing, Collingwood, Victoria, revised edition.
4. EPA (2008) Regional Ecosystems. [online]. Available at http://www.epa.qld.gov.au/nature_conservation/biodiversity/regional_ecosystems/ [accessed 28/06/08].
5. Bureau of Mineral Resources (1971). Eulo: Australia 1:250,000 Geological Series, Bureau of Mineral Resources, Canberra.
6. Bryant KB, Wilson PR, Biggs AJW, Brough DM and Burgess JW (2008). Soil Indicators of Queensland Wetlands: State-wide assessment and methodology. Queensland Department of Natural Resources and Water. Brisbane.
7. Hazelton P and Murphy B (2007). Interpreting Soil Test Results: What do all the numbers mean?. [2nd ed]. CSIRO publishing. Collingwood Victoria.
8. Department of Natural Resources (1997). Salinity Management Handbook. Queensland Department of Natural Resources, Brisbane.
Electrical CondictivityElectrical conductivity (EC� is a measure to describe the salinity, or the presence of soluble salts, of water, a soil water extract or suspension8. Moving along the transect from the saturated zone to the outer zone there is a distinct difference in profiles sampled.
Site 155
Salts are accumulating at the surface
due to an evaporative
concentration
This level of salt
concentration is considered hypersaline
Site 158
Very little salt is observed in the outer zone
Site 157
Salt is being leached through the soil
profile with accumulation
at depth
Site 156
Salts are accumulating at the surface
due to an evaporative
concentrationbut the
effect is less pronounced
9 3 1 1 6 6 2 1 8 0 6 4 3