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Khả năng cố định khí nhà kính của rừng ngập mặn:
Nghiên cứu tại rừng ngập mặn Cần Giờ
Ability of mangroves to fix atmospheric greenhouse gaz: Case
study in Can Gio mangrove, Viet Nam
Trương Văn Vinh
Khoa Lâm Nghiệp, Trường Đại học Nông Lâm – TP. HCM
1
TP. HCM, ngày 09/11/2020
Email: tvvinh@hcmuaf.edu.vn; ĐT: 0989352208
2
(Alongi 2014)
3
Can Gio
mangrove forest
~57 % area
1964 - 1969
665,666 gallons of Agent Orange
343,385 gallons of Agent White
49,200 gallons of Agent Blue
since 1978
~21,000 ha
since 1978
~21,000 ha
~ 32,125 ha
77 mangrove species
35 true mangroves
42 associates
Nowadays
4
5
Mudflat
Fringe forest
Transition forest
Inner forest
118.8
91.7
24.3
150.2157.6118.6
61.9
241.8
157.9
Ecosystem carbon
stock
150.2
(Mg C ha-1)
181.9
(Mg C ha-1)
311.5
(Mg C ha-1)
479.2
(Mg C ha-1)
Buried dead trunk of Rhizophora
40 cm
Soil surface
- MacKenzie et al., (2016) tỷ lệ bồi
lắng trung bình: ~0.99 ± 0.09 cm yr-1
7
Total mangrove
forest cover
32 126 ha
Mudflat
1 413 ha
Mix forest
8 617 ha
Rhizophora
forest
23 508 ha
The overall carbon stock
of Can Gio ~13.6 Tg C
8
9
LiCOR-8100 A
10
LiCOR-840A
LiCOR-820
(1) (2) (3)
11
168 mmol
CO2m-2d-1
78 mmol
CO2m-2d-1
Triều cao
266 mmol
CO2m-2d-1
Triều thấp
- 168.5 (Lovelock et al., 2014)
- 88.6 (Lang’at et al., 2014)
- 80.5 (Leopold et al., 2014)
- 65.5 (Grellier et al., 2014)
12
13
Vertical CO2 concentrations profiles in the canopy
Heightaboveground(m)
14
Eddy-Covariance System on river
15
Eddy-Covariance System in Rhizophora forest
16
17
January February March April
May
DecemberNovemberOctober
AugustJulyJune
September
Observation data in 5 years (2016 – 2020)
18
T0C
H (%)
Net Ecosystem Exchange (μmolm-2s-1)
19
Net Ecosystem Exchange CO2
20
Net Ecosystem Exchange CO2
2/6/2017
16/6/2017
21
Daily sum of Net Ecosystem Exchange
CO2 (gram Carbon/m2/day)
22(Leopold 2016)
Where is the Net Ecosystem Production (NEP) of Can Gio Mangrove Forest,
Tropical, planted mangrove (Rhizophora)???
23
Xin chân thành
cảm ơn!
CHƯƠNG TRÌNH TRỒNG RỪNG
NGẬP MẶN TẠI TX. VĨNH CHÂU,
SÓC TRĂNG (2020 -2028)

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Ability of mangroves to fix atmospheric greenhouse gaz: Case study in Can Gio mangrove, Viet Nam

Editor's Notes

  1. Our main objectives were to quantify the seasonal variability of the litterfall of these two species and to determine their decay rates on the forest floor. We were also interested in nutrient releases during decomposition processes, as well as the evolution of the δ13C values and the content of some trace metals.
  2. Because of GHG increase in the atmosphere, the earth’s climate has warmed by approximately 0.6°C over the past 100 years with two main periods of warming
  3. geographical distribution of mangroves in Vietnam can divided into 4 zones and 12 subzones
  4. During the war (1964 – 1969), most of these forests were destroyed by the spraying of defoliants, particularly in Can Gio, where ~57 % of mangrove areas were destroyed Fortunately, these areas were subsequently reforested since 1978 Nowadays, Can Gio mangrove forest area covers approximately 32,125 ha of mangrove forests including 23,508 ha of interior forest and 8,617 ha of mixed forest
  5. the soil carbon stocks were significantly different between the different stands soil carbon stocks increased with the elevation gradient, with higher values in the inner forest
  6. - The reforestation program started in 1978 (Hong and San, 1993) - MacKenzie et al., (2016) determined an average vertical accretion rate of around 0.99 cm yr-1
  7. CO2 concentrations were higher in the daytime at low tide than in the daytime at high tide. This result may be related to the higher CO2 emmission from soil at low tide than CO2 emmission from water column at high tide. The highest CO2 concentrations were determine at night in May, which related to the period of highest CO2 emissions from soils and trunks due to the high temperature and beginning of the rainy season.