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Predicting impacts of climate change on survival and growth of freshwater pearl mussels in Vogtland (Germany)
Jointly funded by BMBF and BMU/BFN(Funding Code: 01LC1313A-Dand 3514685E13-I13)
Fakultät Umweltwissenschaften Fachrichtung Hydrowissenschaften Institut für Hydrobiologie
© T
. S
chille
r
© J
. S
chn
eid
er
© F
. G
run
ick
e
© T
. S
chille
r
Annekatrin Wagner,
J. Schneider, T. Schiller, F. Grunicke, D. Jähnichen, D. Linke, T. Berendonk
For further information see www.flussmuschel.de
Status quo of Pearl mussels in Vogtland rivers
• The entire river system was settled with pearl mussels
• up to 1000 FPM/m2
• Stong decline ofpopulations
• lack of natural recruitment despite 30% of adults are gravid
• only three relict populations
• since 2002 successful captive breeding (Hruška-method),
First release to the wilderness 2009
What are best habitats for future reintroduction?
1920 1960 2000
Foto: T, Schiller TUD
Otto Baer 1995
T, Schiller TUD
Questions
1. Effects of change in temperature and precipitation on survival and
growth of juvenile mussels (Margaritifera margaritifera)
2. Probability for the occurence of critical condition in low mountain
region in Germany
3. General implications for the conservation management:
What are best habitats for future reintroduction?
1950 2000 2050 2100
TemperatureTemperatur
Niederschlag,
Laboratory experimentsTemperature control
Hypothesis for effects of
temperature on survival
and growth of FPMStatistical analysis
Empirical approaches
• Prediction of climate-driven changes
in mussel habitats
• Identify most suitable brooks for
reintroduction captive-bred FPM
Field studies in Vogtland brooks(2009-2019)
Bioindication
Discharge
Water temperature (data-Logger)
Turbidity…..
Meteorological Data
Station Bad Sohl (1950-2019)
Combined approach and methods
Air temperature
Precipitation
……Hydrological data Pegel Adorf
(1970-2019)
iDA Sachsen.de
Study area in Vogtland
Map „Fischregionen 2011“ (LfULG)
Rauner Bach (RB)
Eisenbach (EB)
Triebelbach(TB)
Tetterweinbach(TW)
Haarbach (HB)
GermanyMittelgebirgsregion: 550 m NN
Comparison of investigation years
Foto: T, Schiller TUD
2016
relatively cool summer
Rainfall: moderate in Jun/Jul and low in Aug
2017
no extremes, always sufficient rain
2018
Extreme flooding at the end of May,
during summer lack of precipitation and high air
temperatures
2019
Low rainfall throughout the summervery warm summer
0
30
60
90
120
Spring Summer
Rain
fall (
mm
/mon
th)
5
10
15
20
Mean
air
tem
pera
ture
( C
)
2016 2017 2018 2019
Long-term Mean Mittel: 1961 - 1990
Normal20162017
Flood2018
Low water in brooksSommer 2018 +2019Foto: T, Schiller TUD
• flow-through sediment cages
• in 5 streams
• each 15 PM of age 10-15
• control at 1. Juni and 31. August
• 2016 - 2019
In-situ Bioindikation mit semi-adulte FPM
© T
. S
chille
r
Foto: A. Wagner TUD Foto: A. Wagner TUD
Foto: T, Schiller TUD
© T
. S
chille
r
Lethale effects onsemiadult FPM
50%
60%
70%
80%
90%
100%
16 18 20 22 24 26
Überleben
Maxima Wassertemperatur ( C)
2016
2018
2017
2019
90%
95%
100%
0 20 40
Übe
rle
be
n
Abfluss Min Jun-Aug (l/s)
2017
2018
2019 Discharge<10 l/s und WT>25 C
increase in mortality
extreme flooding
no mortality
Max water temperature ( C)
Surv
ival
Surv
ival
Min discharge (l/s)
© T
. S
chille
r
gro= 48,3*exp(-0,5*((WT-14,75)/1,1)^2)
R=0,76
P<0,001
Temperature optimum ofsemiadulte PM
0
10
20
30
40
50
60
70
80
13 14 15 16 17
Wa
chstu
m (
µm
/d)
Wassertemperatur MW ( C)
semiadulte FPM_2016-2019
EB
HB
RB
TB
TW
0
10
20
30
40
50
60
70
13 14 15 16 17
Wachstu
m (µ
m/d
)
Wassertemperatur MW ( C)
2016
2018
2017
2019
Maximum growth
60 µm/d = 5,5 mm/Jahr
Temperature optimum 14,8 – 15,4 C
Gro
wth
(µ
m/d
)G
row
th (
µm
/d)
Water temperature ( C)
Foto: T, Schiller TUD
Factors cotrollinggrowth semi-adulter PM
2009-2014 data to bioindication from Michael Lange
• flow-through sediment cages
• in Rauner Bach
• Each 15 semiadulte FPM
• Control at 1. Juni and 31. August
• 2009 -2019
0
20
40
60
0 30 60 90 120 150
NS (mm/Monat)
0
20
40
60
15 16 17 18 19
Lufttemperatur MW ( C)
Foto: T, Schiller TUD
Wa
ch
stu
m (
µm
/d)
Factors cotrollinggrowth of
semi-adulter PMJun-Aug 2009-2019
High growth at
precipitation > 60 < 100 mm/month
> 8 rainy days/month
Average air temperature <17 C
R = 0,54P = 0,09
R = 0,78P = 0,007
Gro
wth
(µ
m/d
)
Air temperature ( C)
Rain (mm/month)
Risk of partial drying of the streams
2003, 2012, 2015,
2018, 2019
Foto: T, Schiller TUD
Foto: T, Schiller TUD
0
20
40
60
80
100
0 1 2 3 4 5 6 7 8 9 10 11 12
Rain
(m
m/m
on
th)
month
drying out (n=5)
suffient water (n=11)
Mittelwerte und SE der monatlichen
Niederschlagssumme (2002 -2019)
0
20
40
60
80
100
0 1 2 3 4 5 6 7 8 9 10 11 12
Rain
(m
m/m
on
th)
month
drying out (n=5)
suffient water (n=11)
0
20
40
60
80
100
0 1 2 3 4 5 6 7 8 9 10 11 12
Rain
(m
m/m
on
th)
month
drying out (n=5)
suffient water (n=11)
0
20
40
60
80
100
0 1 2 3 4 5 6 7 8 9 10 11 12
Rain
(m
m/m
on
th)
month
drying out (n=5)
suffient water (n=11)
Risk of partial drying of the streams
2003, 2012, 2015,
2018, 2019
Mean Values of monthly rain and SE
(2002 -2019)
Luft
tem
pera
tur
(°C
)
15
16
17
18
19
20
Data meteorology: Station Sohl (sklima.de)Groundwater level_Adorf (iDa Sachsen)
Nie
ders
chla
g J
ul-A
ug (
mm
/Monat)
0
20
40
60
80
100
120
140
160
180
Gru
ndw
assers
tand, m
in (c
m)
-135
-130
-125
-120
-115
-110
-105
P<0,001
P<0,001P=0,023
Luft
feuch
te (
min
) %
30
35
40
45
50
55
60
65
P<0,001
years with
drying up
Luft
tem
pera
tur
( C
)
Luft
feuchte
Min
(%
)
Pre
cip
ita
tio
n(m
m/m
on
th)
Gru
ndw
assers
tand M
in (
cm
)
Data: Jul-Aug 2002-2019
One-Way ANOVA
Years with drying-up n=5years without drying-up n=11
Min
air
hum
idity
(%)
Air
tem
pera
ture
( C
)
Min
gro
undw
ate
rle
vel(c
m)
years without
drying upyears with
drying up
years without
drying up
Foto: T, Schiller TUD
Trend to decreasing groundwater levels
1. Mai.
31. Mai.
1. Jul.
31. Jul.
31. Aug.
30. Sep.
31. Okt.
1970 1980 1990 2000 2010 2020
Sta
rt G
Wsta
nd
>120cm
0
30
60
90
120
150
1970 1980 1990 2000 2010 2020
Dau
er
GW
sta
nd
>120cm
(d
)
1. Jun
1. Sep
1. Okt
1. Nov
1. Aug
Periods with extremely low groundwater levels start earlier in the year and last longer
Data meteorology : Station Sohl (sklima.de)groundwater levels_Adorf (iDa Sachsen)
Sta
rt g
roundw
ate
rle
vel
>12
0cm
Dura
tion (
days)
of
the
pe
rio
d
with
gro
undw
ate
rle
vel>
12
0cm
0
200
400
600
800
1000
1200
1400
-4 -2 0 2 4 6 8 10 12
Life cycle
Foto: T, Schiller TUD
May NovSepJul
Length
(µm
)
Months after dropping of brown trout
Metamorphosis at the
gill of brown troutFPM lives in the hyporheic zone
Foto: F. Grunicke TUDFoto: F. Grunicke TUD Foto: A. Kuhr TUD
© T
. S
chille
r
In-situ bioindication with0+ PM
• In each brook 6-9 cylindrical tubes
mesh size of 0.42 mm
• filled with brook-specific gravel (2-6
mm)
• 50 post-parasitic mussels
• Exposed to 5 brooks and buried in
the sediment at a depth of 5 cm
• From Juni bis 31. August
• 2017 -2019
0
2
4
6
8
10
13 14 15 16 17
Wa
chstu
m (
µm
/d)
Wassertemperatur in -5cm ( C)
2019
2018
2017
growth = -35,373 + (2,483 * WT)
R2 = 0,73
P < 0,001
Temperature control ofgrowth of 0+PM
© T
. S
chill
er
Gro
wth
(µ
m/d
)
Water temperature in -5 cm ( C)
0%
20%
40%
60%
80%
100%
600 800 1000 1200 1400 1600 1800
Su
rviv
al
du
rin
g 1
. w
inte
r
Length at the end of 1. growing season (µm)
LP_2017
LP_2018
WE_Wi2017
DGR_2018
NonlinearRegression
© T
. S
chille
r
Influence of length in autumn on survival of
0+PM during first winter
Sigmoidal Regression:
Surv_wi = 0,97/(1+exp(-(L-1107)/97,2))
R2= 0,92
P<0,001
Survival during autumn+winter
Two Way Analysis of Variance
Startlänge p<0,001
Temperature winter p=0,91
0,5
1
1,5
13 14 15 16 17
Len
gth
at
the e
nd
of
1.
gro
win
g s
eason
(m
m)
0%
20%
40%
60%
80%
100%
13 14 15 16 17
Su
rviv
al
du
rin
g 1
. w
inte
r
Water temperature -5 cm (Jun-Aug) ( C)
© T
. S
chille
r
Estimated effect of water temperatures during
summer on survival of 0+PM during first winter
15 C during summer
corresponds to a survival of 50%
Wa
ter
Te
mp
era
ture
(°C
)
8
10
12
14
16
18
20
22
EB16
EB17
EB18
HB16
HB17
HB18
RB16
RB17
RB18
TB16
TB17
TB18
TW16
TW17
TW18
WB16
WB17
WB18
GB16
GB17
GB18
2016 2017 2018
Wa
ter
tem
pe
ratu
re(
C)
10
12
14
16
18
20
EB GBWBTWTBRBHB
Water temperatures during summer (Jun, Jul, Aug) 2016-2018
Logger(Tinytag)
Mean water temperature of river Lutter: 15.7 C
(Data: M. Lange)
too
co
ld
Lut
Bottleneck in mussel conservation strategy
krenal and epi-rhitral of rivers more suitable for the FPM in terms of morphology
and water quality compared to the meta- or hyporhitral, but often too cold
Adorf: 14,1 / 15,7
Mühlhausen: 13,6 / 15,3
Oelsnitz: 15,4 / 15,9
Rauner Mühle: 12,3 / 12,8
Mean Water temperatures(iDA) (Jun-Aug) 2002-2016: Cold years Air temp<16 Cwarm years Air temp>16 C
Reservoir
Small tributariesJB: 11,4 / 13,4Wer 12,1 / 13,9
Temperature in krenal and
rhithral
Otto Baer 1995
Weiße Elster 1800
© J
. S
chneid
er
TW: 15,1 / 17,1
Conclusions to hazard factors
Foto: T, Schiller TUD
Semiadulte Muscheln
Low rain or at less than 8 days/month Decrease of ground water levels Discharge <10 l/s Water temperatures >24 C
Age-0 FPM Average water temperatures during summer <15 C
Increasing probability of streams drying out.
For a successful freshwater mussel conservation approach, it is
crucial to consider consequences of climate warming.
Foto: T, Schiller TUD
Foto: T. Schiller TUD
© T
. S
chill
er
Many thanks to all partners, to our advisory boards and
to the supporters in the state ministries and offices.
For further information see www.flussmuschel.de
Thank you very much for your attention!