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EMISSION OF METHANE FROM SEDIMENTS OF SELECTED POLISH DAM RESERVOIRS

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Dam reservoirs contribute significantly to global gross methane emission which has been estimated at 104 ±7.2 Tg CH 4 per year. However, this value might be far from real since the contribution of small dam reservoirs has not been taken into consideration. This study was aimed at estimating the amount of methane emitted from selected lowland dam reservoirs in Poland in relation to hydrochemical conditions: depth, organic matter content, red-ox, pH. The research was conducted on 4 dam reservoirs located in a SW to NE cross-section of Poland: Turawa, Sulejowski, Włocławski, Siemianówka. The reservoirs show a wide range of average amount of collected gas and CH 4 content. Calculated methane ebullition amounted to 4 mg m -2 d -1 in Sulejowski, 401 mg m -2 d -1 in Siemianówka, 42 mg m -2 d -1 Turawa and 413 mg m -2 d -1 in Wło-cławski reservoirs. The most spatially diversified results were reported for Włocławski and the most stable for Siemianówka and Sulejowski. The remarkably high values of methane emission noted for Siemianówka and Włocławski reservoirs exhibit the range typical to tropical reservoirs, which suggest potential for CH 4 exploitation for energy production purposes.
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Teka Kom. Ochr. Kszt. Środ. Przyr. – OL PAN, 2009, 6, 368–373
EMISSION OF METHANE FROM SEDIMENTS
OF SELECTED POLISH DAM RESERVOIRS
Adriana Trojanowska, Marta Kurasiewicz, Łukasz Pleśniak,
Mariusz Orion Jędrysek
Laboratory of Isotope Geology and Geoecology, Institute of Geological Sciences, University of Wroclaw,
Cybulskiego str. 30, 50-205 Wroclaw, adriana.trojanowska@ing.uni.wroc.pl
Summary. Dam reservoirs contribute significantly to global gross methane emission which has
been estimated at 104 ±7.2 Tg CH
4
per year. However, this value might be far from real since the
contribution of small dam reservoirs has not been taken into consideration. This study was aimed
at estimating the amount of methane emitted from selected lowland dam reservoirs in Poland in
relation to hydrochemical conditions: depth, organic matter content, red-ox, pH. The research was
conducted on 4 dam reservoirs located in a SW to NE cross-section of Poland: Turawa,
Sulejowski, Włocławski, Siemianówka. The reservoirs show a wide range of average amount of
collected gas and CH
4
content. Calculated methane ebullition amounted to 4 mg m
-2
d
-1
in
Sulejowski, 401 mg m
-2
d
-1
in Siemianówka, 42 mg m
-2
d
-1
Turawa and 413 mg m
-2
d
-1
in Wło-
cławski reservoirs. The most spatially diversified results were reported for Włocławski and the
most stable for Siemianówka and Sulejowski. The remarkably high values of methane emission
noted for Siemianówka and Włocławski reservoirs exhibit the range typical to tropical reservoirs,
which suggest potential for CH
4
exploitation for energy production purposes.
Key words: methane, sediments, dam reservoirs
INTRODUCTION
Methane is considered to be one of the most active greenhouse gases, whose
concentration increase in the atmosphere is currently about twenty times faster than
that of other greenhouse gases of global importance [IPCC 2001]. It was estimated
that approximately 45% of methane in the atmosphere comes from areas periodi-
cally or permanently flooded with water, such as rice fields, marshes, lakes.
Dam reservoirs are also considered to be significant sources of methane
emissions, responsible for about 18% of global greenhouse effect of anthropo-
genic origin. Globally, methane emissions from dam reservoirs are estimated at
EMISSION OF METHANE FROM SEDIMENTS...
369
104 ±7.2 Tg CH
4
per year. It was estimated that the average methane emission
form dam reservoirs of the temperate zone is 55.1 ±84.7 mg m
-2
day
-1
, and from
the tropical zone – about 136 ±245 mg m
-2
day
-1
[Sournis et al. 2005, Lima et al.
2008]. However, these numbers, as calculated on the basis of the case of large dam
reservoirs (mainly Brasilian, Indian, Canadian), may be inaccurate since they ex-
clude a great number of small water bodies [ICOLD 2003, Sournis et al. 2005].
Therefore, the aim of this study was to estimate the amount of CH
4
emitted
from sediments of selected Polish dam reservoirs and to indicate its potential
relationship with depth, organic matter content and other environmental factors.
METHODS
The research was conducted on 4 dam reservoirs: Turawa, Sulejowski,
Wloclawski and Siemianowka, characterised by a wide range of hydrological and
Table 1. Selected morphometric and hydrochemical parameters charactering the conditions in studied
dam reservoirs [Ambrożewski 1996, Gurwin et al. 2005, Górniak and Jekatierynczuk-Rudczyk 2006,
Suchowolec 2006, Gierszewski et al. 2006]
Parameters
Turawa
Reservoir
Sulejowski
Reservoir
Włocławski
Reservoir
Siemianówka
Reservoir
River Mala Panew Pilica Vistula Narew
Length of reservoir, km 7 17 58 11
Mean depth, m 4 3,5 5,5 2,5
Volume, km
3
106 75 408 62
Mean water retention time, days 110 42 5 540**
Mean organic matter
content in sediments, %*
6,5 ±9,9 6,5 ±4,7 11,5 ±7,7 10,7 ±3,4
Mean carbonates content
in sediments, %*
< 1 12 ±8,5 22 ±8,6 < 1
Mean content of CH
4
in pore gas, %*
9 ±14 4 ±7 27 ±23 49 ±15
Mean ebulition of methane,
mg m
-2
day
-1
*
42 ±98 4 ±10 413 ±587 401 ±618
Additional information on
environmental problems
heavy metals,
eutrophication
eutrophiction hydrocarbons Humic
substances
*data collected for this research, ** estimated from water exchange time
and hydrochemical conditions (Tab. 1). Gas and sediment samples were col-
lected from the reservoirs in several points randomly distributed over the bed of
each reservoir. Pore gas was collected using traps set at the bottom of the reser-
voirs for several hours. Bottom sediments were collected at the same stations
using an Ekman-Birge sampler. The quantity of collected gas and temperature
(digital thermometer, ±0.1°C), pH (WTW SenTix SP, ±0.01), redox (ORP Sen-
Tix WTW, platinum, ±0.01 mV) of sediments were measured during sampling.
Adriana Trojanowska et al.
370
Analyses of the concentration of CH4 in pore gas samples were made using an
ELWRO 504 gas chromatograph. Analyses of water content and organic matter
content were made using the gravimetric method [Håkanson and Jansson 1983]. The
content of carbonates in the sediments was analysed using a calcite bomb.
RESULTS
The studied reservoirs showed wide variations in the amount of pore gas
emitted from the sediments. The lowest amount of gas was collected from the
Sulejowski Reservoir (38 ml m
-2
d
-1
in average), where at several stations no gas
has been detected at all. The highest gas amounts were collected in the Wło-
cławski Reservoir: 3114 ml m
-2
d
-1
, on average. In other studied reservoirs mean
gas emission was calculated at 990 ml m
-2
d
-1
in Siemianowka and 1445 ml m
-2
d
-1
in Turawa. The largest spatial variation in the amount of gas emitted from the
sediment and in methane percentage content was recorded in the Włocławski
Reservoir, while the smallest in the Sulejowski (Fig. 1, Tab. 1). Percentage con-
Fig. 1. Methane percentage content in pore gas (A) and methane ebullition from sediments (B)
of dam reservoirs: Turawa (I), Sulejowski (II), Włocławski (III), Siemianówka (IV)
EMISSION OF METHANE FROM SEDIMENTS...
371
tent of methane in pore gas was the lowest in the Sulejów Reservoir, where it
reached only 4.5% on average and did not exceed 20% at either station. The
highest content of methane was recorded in gas samples collected from the
Siemianówka Reservoir (49% on average). In other reservoirs lower values were
noted – 27% in Włocławski Reservoir and 9% in Turawa.
Taking into account the average percentage content of methane, calculated
values of methane ebullition amounted to 4 mg m
-2
d
-1
in the Sulejowski reser-
voir, 401 mg m
-2
d
-1
in Siemianówka, 42 mg m
-2
d
-1
in Turawa and 413 mg m
-2
d
-1
in Włocławski (Tab. 1, Fig. 1).
DISCUSSION
Jones et al. [1982] indicated factors that regulate the rate of CH
4
emission
from sediments under natural conditions: the availability of substrates, tempera-
ture, redox potential, pH, water column. The highest ebullition rate was recorded
in the Włocławski and Siemianówka Reservoirs, which are rich in organic mat-
ter, however only in the Włocławski Reservoir this relationship was confirmed
with a weak correlation coefficient (r = 0.42, p = 0.11). Although, some trends
of increased ebullition were noted in areas of organic matter accumulation. Ex-
tremely low methane ebullition in the Sulejowski Reservoir may be due to toxic
effects of cyanobacterial blooms or abundant sulphates and nitrates which, ac-
cording to Conrad et al. [1999], may inhibit methanogenesis and increase deni-
trification simultaneously [Trojanowska and Kurasiewicz 2009]. However, at the
same time, methane emission showed a significant relationship with pH (r = 0.70,
p = 0.016).
Heavy metals, abundant in sediments of the Turawa Reservoir [Gurwin et
al. 2005], are probably responsible for inhibition of methanogenesis, according
to Mishra et al. [1999]. The ebullition of CH
4
from the reservoirs Sulejowski and
Turawa displays lower values characteristic for temperate water bodies (Tab. 1).
The surprisingly high values of methane emitted from sediments of the Wlo-
clawski and Siemianowka reservoirs are comparable with results recorded in
large tropical reservoirs [Sournis et al. 2005, Santos et al. 2006]. The results
presented in this paper are derived solely from the summer sampling, the most
intense period of processing of organic matter in sediments, which could cause
overestimation of CH
4
emission.
All studied reservoirs are shallow and rather rich in organic matter (Tab. 1).
An increase of percentage contribution of CH
4
with depth was noted for the
Turawa and Siemianówka reservoirs (r = 0.42, p = 0.11, and r = 0.74, p = 0.004,
respectively). It was previously confirmed by Joyce and Jewell [2003], who
proved that the highest potential of methane ebullition is exhibited by shallow
waters, and the highest rate of the process in noted up to 5 m depth, while at
greater depths is significantly decreased. Furthermore, Lima [2005], on the basis
Adriana Trojanowska et al.
372
of the isotopic composition of carbon in methane, confirmed that with increasing
depth in large dam reservoirs the rate of CH
4
consumption significantly in-
creases, which in consequence reduces its emissions. Weaving and currents im-
pact on sediments greatly accelerates and intensifies ebullition of methane from
sediments in dam reservoirs [Keller and Stallard 1994, Joyce and Jewell 2003],
hence probably the increased liberation of methane from sediments in the rheo-
limnetic Włocławski Reservoir and in other reservoirs at stations located close to
the main stream course (Fig. 1).
CONCLUSION
High values of methane emission recorded in the Włocławski and
Siemianówka reservoirs suggest that the contribution of lowland shallow waters
may be relatively significant in the total greenhouse gas budget. The technology
of methane recovery from sediments and water of dam reservoirs allows using
pore gas for energy production purposes, global reserves of pore gas being esti-
mated at 100 ±6.9 Tg CH
4
per year [Kilkuchi and Maral 2007, Lima et al. 2008].
In this case temperate lowland shallow dam reservoirs should be also taken into
consideration.
REFERENCES
Ambrożewski Z., 1996. Problemy ekologiczne i powodziowe zbiornika wodnego Sulejów. Aura 7, 19–21.
Conrad R., 2005. Quantification of methanogenic pathways rushing stable carbon isotopic signa-
tures; a review and proposal. Org. Geochem. 36, 739–752.
Gierszewski P., Szmanda J.B., 2006. Distribution of the bottom deposits and accumulation dynamics in
the Wloclawek Reservoir (central Poland). WSEAS Trans. Environ. Develop. 2, 543–549.
Gurwin J., Kryza J., Poprawki L., Skowronek A., 2005. Badania geoekologiczne Jeziora Turaw-
skiego. III Konferencja „Zasoby wodne Triasu Opolskiego i Jezior Turawskich”, Strzelce
Opolskie 2005.
Górniak A., Jekaterinczuk-Rudczyk E., 2006. Węgiel organiczny w osadach dennych zbiornika
Siemianówka [w:] Górniak A. (red.), Ekosystem zbiornika Siemianówka w latach 1990–2004 i
jego rekultywacja. Zakład Hydrobiologii Uniwersytetu w Białymstoku, 111–112.
Hakanson L., Jansson M., 1983. Principles of lake sedimentology, Springer-Verlag, Berlin, Hei-
derberg, New York, Tokyo, pp. 316.
Intergovermental Panel on Climate Change (IPCC), 2001. Climate Change: Synthesis Report
2001. Cambridge University Press, pp. 396.
International Commission On Large Dams (ICOLD) 2003. World register of dams. http://
www.icold-cigb.org
Jones J.G., Simon B.M., Gardener S., 1982. Factors affecting methanogenesis and associated
anaerobic processes in the sediments of a stratified eutrophic lake. J. General Microb. 18, 1–11.
Joyce J., Jewell P.W., 2003. Physical controls on methane ebullition from reservoirs and lakes.
Environ. Eng. Geosci., IX (2), 167–178.
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Keller M., Stallard R.F., 1994. Methane emission by bubbling from Gatun Lake, Panama. J. Geo-
phys. Res., 99, 8307–8319.
Kikuchi R., do Maral P.B., 2007. Conceptual schematic for capture of biomethane released from
hydroelectric power facilities. Biores. Technol. 99, 5967–5971.
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voirs. Chemosphere 59, 1697–1702.
Lima I.B.T., Ramos F.M., Bambace L.A.W., Rosa R.R., 2008. Methane Emissions from Large
Dams as Renewable Energy Resources: A Developing Nation Perspective. Mitig Adapt Strat
Glob Change, 13, 193–206
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production in tropical rice soils. Ecotoxicol. Environ. Safety, 44, 129–136.
Santos M.A., Rosa, L.P., Sikar B., Sikar E., Santos E.O., 2006. Gross greenhouse gas fluxes from
hydro-power reservoir compared to thermo-power plants. Energy Policy 34, 481–488.
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Suchowolec T., 2006. Morfologia i zagadnienia techniczne zbiornika Siemianówka [w:] Górniak A.
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Hydrobiologii Uniwersytetu w Białymstoku, 22–26.
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Acknowledgements. The studies were supported by the Polish Ministry of Higher Education and Science,
grant No R1205602. We would like to acknowledge Janusz Krajniak and Radoslaw Drynda for their support in
field works.
EMISJA METANU Z OSADÓW WYBRANYCH ZBIORNIKÓW ZAPOROWYCH
W POLSCE
Streszczenie. Udział zbiorników zaporowych w globalnej emisji metanu ocenia się jako znaczący,
oszacowano go na 104 ±7,2 CH
4
Tg rocznie. Jednak szacunki te mogą odbiegać od rzeczywistości,
ponieważ nie uwzględniają emisji z małych zbiorników zaporowych. Celem badań było oszaco-
wanie wielkości emisji metanu z wybranych nizinnych zbiorników zaporowych w Polsce w odnie-
sieniu do warunków hydrochemicznych i morfometrycznych: głębokości, zawartości materii orga-
nicznej, redox, pH. Badania przeprowadzono w 4 zbiornikach zlokalizowanych w transekcie z
południowego zachodu na północny wschód Polski: Turawie, Sulejowskim, Włocławskim, Siemianów-
ce. Ilość gazu wydzielanego z osadów i % zawartość w nim CH
4
były znacznie zróżnicowane w bada-
nych zbiornikach. Wyliczona ebulicja metanu osiągnęła wartości: 4 mg m
-2
· d
-1
w Sulejow-
skim, 401 mg m
-2
·
d
-1
w Siemianówce, 42 mg m
-2
·
d
-1
w Turawie i 413 mg m
-2
·
d
-1
we Włocław-
skim. Najbardziej zróżnicowane przestrzennie wyniki zanotowano w zbiorniku Włocławskim,
natomiast najbardziej wyrównane w Siemianówce. Wyjątkowo wysokie wartości emisji metanu ze
zbiorników Siemianówka i Włocławskiego przekraczały wartości uważane za typowe dla zbiorników
tropikalnych, co wskazuje na możliwość pozyskiwania metanu z tego źródła do celów energetycznych.
Słowa kluczowe: metan, osady, zbiorniki zaporowe
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Factors affecting methanogenesis in the sediments of a eutrophic lake were studied during late summer, a period during which CH, gas production slowed down dramatically or stopped completely. The most active methanogenesis occurred in the surface sediments and the temperature optimum for the process in these deeper sediments was 30 OC. Addition of H, or formic acid to sediment slurries stimulated CH, production to a greater extent than did acetic or pyruvic acid. Analysis of the kinetics of the conversion of H, to CH, suggested that the sediments were severely limited in H,, the concentration being considerably less than 2.5 pmol l-', the K, for the process. Methanogenesis was not stimulated by the addition of trace quantities of Ni2+, Co2+, MOO:- or Fe2+ ions but was inhibited by 0-5 mmol SO:- 1-*. Under natural conditions the sediments were also limited in SO:- and sulphate reducers acted as net H, donors to the methanogens; addition of SO:- allowed the sulphate reducers to compete effectively for H,. The addition of 20 mmol Na,MoO, 1-I to sediments inhibited methanogenesis but this was not due entirely to its effect in the H, transfer from sulphate reducers; it also inhibited CO, uptake by sediments and the production of CH, from CH,COOH and CO, by cultures of methanogens. It is therefore inadvisable to use MOO:- at this concentration as a specific inhibitor of sulphate reducers in such freshwater sediments. Experiments with other inhibitors of methanogens suggested that they may interact with sulphate reducers, acetogens or anaerobic bacteria involved in fatty acid decomposition. Small, sealed sediment cores, which were used to reproduce natural conditions, particularly of available H, concentration, were injected with trace quantities of H14C05 and I4CH3COOH. The results suggested that more than 75% of the CH, was derived from CO, and the remainder from CH,COOH. The overall rates of methanogenesis in the small cores agreed well with results from the field.
Article
In most environments, CH4 is produced from acetate (i.e. the methyl group) and H2/CO2 as precursors. The relative contribution of these two methanogenic pathways to total CH4 production can be quantified when the stable carbon isotopic signatures of CO2, CH4 and acetate methyl are measured for the CH4 production site and the isotopic fractionation factors are known for the conversion of CO2 and of acetate methyl to CH4. Literature review shows that the fractionation factors are not constants but differ, sometimes substantially, from site to site and from condition to condition. Large differences are also evident from studies of microbial cultures. More data, in particular explicit determination of fractionation factors under various conditions and environments are required. Experimental determination of fractionation factors under environmental conditions may be done by stimulation or inhibition experiments that allow the measurement of stable carbon fractionation in distinct reactions. Isotopic fractionation during acetate turnover is a particular challenge, since acetate methyl may be produced and consumed by several competing pathways. Acetate may be produced from organic carbon or from CO2 and may be consumed by conversion to CH4, CO2 or biomass. Use of isotopic signatures in CH4 emitted from a production site (e.g. a wetland) requires even more complex models, since isotopic discrimination in addition occurs during transport and oxidation of the CH4 produced.
Article
This paper presents the findings of gross carbon dioxide and methane emissions measurements in several Brazilian hydro-reservoirs, compared to thermo power generation.The term ‘gross emissions’ means gas flux measurements from the reservoir surface without natural pre-impoundment emissions by natural bodies such as the river channel, seasonal flooding and terrestrial ecosystems. The net emissions result from deducting pre-existing emissions by the reservoir.A power dam emits biogenic gases such as CO2 and CH4. However, studies comparing gas emissions (gross emissions) from the reservoir surface with emissions by thermo-power generation technologies show that the hydro-based option presents better results in most cases analyzed.In this study, measurements were carried in the Miranda, Barra Bonita, Segredo, Três Marias, Xingó, and Samuel and Tucuruí reservoirs, located in two different climatological regimes. Additional data were used here from measurements taken at the Itaipu and Serra da Mesa reservoirs.Comparisons were also made between emissions from hydro-power plants and their thermo-based equivalents. Bearing in mind that the estimated values for hydro-power plants include emissions that are not totally anthropogenic, the hydro-power plants studied generally posted lower emissions than their equivalent thermo-based counterparts.Hydro-power complexes with greater power densities (capacity/area flooded—W/m2), such as Itaipu, Xingó, Segredo and Miranda, have the best performance, well above thermo-power plants using state-of-the-art technology: combined cycle fueled by natural gas, with 50% efficiency.On the other hand, some hydro-power complexes with low-power density perform only slightly better or even worse than their thermo-power counterparts.
Article
We studied methane emission by bubbling from Gatun Lake, Panama, at water depths of less than 1 m to about 10 m. Gas bubbles were collected in floating traps deployed during 12- to 60-hour observation periods. Comparison of floating traps and floating chambers showed that about 98% of methane emission occurred by bubbling and only 2% occurred by diffusion. Average methane concentration of bubbles at our sites varied from 67% to 77%. Methane emission by bubbling occurred episodically, with greatest rates primarily between the hours of 0800 and 1400 LT. Events appear to be triggered by wind. The flux of methane associated with bubbling was strongly anticorrelated with water depth. Seasonal changes in water depth caused seasonal variation of methane emission. Bubble methane fluxes through the lake surface into the atmosphere measured during 24-hour intervals were least (10-200 mg/m2/d) at deeper sites (greater than 7 m) and greatest (300-2000 mg/m2/d) at shallow sites (less than 2 m).
Article
In a laboratory incubation study, the effect of select heavy metals on methane (CH(4)) production in three rice soils was investigated under flooded conditions. Heavy metals behaved differently in their effect on methanogenesis in different soils and methane-producing bacteria. Cd, Cu, and Pb inhibited CH(4) production in all the soils. Zn stimulated CH(4) production in the alluvial soil, but inhibited it in laterite and acid sulfate soils. Cr effectively inhibited CH(4) production in the alluvial soil, but stimulated it in laterite and acid sulfate soils. The stimulatory effect of Zn and the inhibitory effect of Cr on methanogenesis in alluvial soil were attributed to their stimulation or inhibition of methanogenic bacterial population.
Article
Biogeochemical distinction of methane emissions to the atmosphere may essentially rely on the surface area and morphometry of Amazon hydroreservoirs. Tucurui (deep) and Samuel (shallow) reservoirs released in average 13.82+/-22.94 and 71.19+/-107.4 mg CH4 m(-2)d(-1), respectively. delta13C-CH4 values from the sediments to the atmosphere indicate that the deep reservoir has extended methanotrophic layer, oxidizing large quantities of light isotope methane coming from the sediments, while sediment-generated methane can easily evade the shallow reservoir.