RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN >> 2015, Vol. 24 >> Issue (11): 1898-1905.doi: 10.11870/cjlyzyyhj201511013

Previous Articles     Next Articles

EFFECTS OF SEMI-LUNAR TIDAL CYCLING ON SOIL PHYSICAL AND CHEMICAL PROPERTIES IN COASTAL WETLANDS

BU Nai-shun1, WANG Kun1, HOU Yu-le1, LI Gang1, QI Shu-juan1, FANG Chang-ming2, QU Jun-feng1   

  1. 1. School of Environmental Science and Spatial Informatics, China University of Mining and Technology, Xuzhou, 221116, China;
    2. School of Life Science, Fudan University, Shanghai 200438, China
  • Received:2015-04-07 Revised:2015-07-10 Online:2015-11-20

Abstract: As important hydrological features of coastal wetlands, periodic tides usually present two types of hydrological cycles on different time scales, semi-diurnal and semi-lunar tidal cycles (consisting of neap and spring tide periods (NTP and STP)). Therefore, tidal effects on soil physical and chemical properties of the vegetated zone may vary greatly between tidal cycles, because of different inundation frequencies and durations. Previous studies suggested that soil properties showed no significant change across the semi-diurnal cycle, probably because these work were mainly conducted in STP when soils were inundated or water-saturated most of the time. However, there has been no study on whether or how the semi-lunar tidal cycle affects soil properties in coastal wetlands. A field study was conducted in Chongming Dongtan wetland in the Yangtze River estuary to investigate temporal variations of soil physical and chemical properties along with the transition from NTP to STP in a semi-lunar tidal cycle and to explore possible underlying mechanisms of these variations. During the cycling of semi-lunar tides, periodic neap and spring tides significantly affected soil physical and chemical properties of coastal wetlands. A major change caused by the transition between NTP and STP was in soil water conditions. Soil moisture was significantly greater in STP than in NTP, because soil was over-saturated or submerged nearly all the time during STP due to frequent tidal inundation, especially in the low tide zone. Further analysis indicated that increased moisture in top soils in STP was greater than those in subsurface and deep soils. This suppressed the diffusion of O2 from atmosphere into soil, and existing soil O2 was rapidly consumed during STP. Therefore, soil Eh decreased dramatically with the transition from neap to spring tides. Regression analysis also showed that soil Eh was negatively correlated with moisture (R2 = 0.60, P < 0.0001). Furthermore, variations of soil Eh with that transition increased gradually from the low to the high tide zone, probably because the frequency of inundation by tidewater is greater and the duration is longer in the former zone. No significant change in soil pH values was observed between NTP and STP. Soil pH is an important factor in regulating the soil inorganic carbon (SIC) pool. SIC may account for more than 60% of soil total carbon in wetlands of the Yangtze River estuary. Periodic tidal inundation can maintain the alkaline environment (pH > 8.0) of soils, ensuring the stability of the SIC pool in the estuary. Soil conductivity and sulfate content were significantly greater in STP than in NTP because of the influence of tides, suggesting that tides transport substantial nutrients to coastal wetlands. Because of greater inundation frequency and longer duration, this exchange of salts was more efficient in the low tide zone than in the high tide zone. Consequently, compared with NTP, increase in soil conductivity and sulfate content in STP decreased gradually from the low to the high tide zone. Thus nutrient input via this mechanism may be vital in supporting high plant productivity in coastal wetlands. Positive effects of nutrient input on plant productivity were likely stronger in the low tide zone than in the high tide zone. This speculation may be confirmed by the results that plant traits of Spartina alterniflora such as aboveground plant biomass, plant height, and basal stem diameter were more advantageous in the low tide zone than in the high tide zone. In addition, soil bulk density, pH values, dissolved organic carbon (DOC) and dissolved nitrogen (DN) did not change significantly with the transition from NTP to STP, except at site S1 where only topsoil bulk density, DOC and DN were significantly lower in NTP than in STP. These findings indicate that semi-lunar tidal cycling can significantly impact soil physical and chemical properties in coastal wetlands, especially soil water, salinity and nutrient characteristics as well as redox environment, which may play important roles in regulating plant growth and relative ecological processes of coastal wetlands.

Key words: semi-lunar tidal cycle, coastal wetlands, soil physical and chemical properties, Chongming Dongtan, Spartina alterniflora

CLC Number: 

  • S728.5
[1] BARBIER E B,HACKER S D,KENNEDY C,et al.The value of estuarine and coastal ecosystem services[J].Ecological Monographs,2011,81:169-193.
[2] TOWNEND I,FLETCHER C,KNAPPEN M,et al.A review of salt marsh dynamics[J].Water and Environment Journal,2011,25:477-488.
[3] KVALE EP.The origin of neap-spring tidal cycles[J].Marine Geology,2006,235:5-18.
[4] 高君颖,王维奇,鄂 焱,等.潮汐对闽江河口湿地土壤理化特征的影响分析[J].湿地科学与管理,2011,7:48-52.
[5] TONG C,WANG W Q,ZENG C S,et al.Methane emission from a tidal marsh in the Min River estuary,southeast China[J].Journal of Environmental Science and Health Part a-Toxic/Hazardous Substances & Environmental Engineering,2010,45:506-516.
[6] 仝 川,姚 顺,王维奇,等.中国东南沿海短叶茳芏潮汐沼泽湿地甲烷动态[J].中国科学:地球科学,2012,42:723-735.
[7] 徐宏发,赵云龙.上海市崇明东滩鸟类自然保护区科学考察集[M].北京:中国林业出版社,2005.
[8] YANG S L,DING P X,CHEN S L.Changes in progradation rate of the tidal flats at the mouth of the Changjiang (Yangtze) River,China[J].Geomorphology, 2001,38:167-180.
[9] WANG Q,AN S Q,MA Z J,et al.Invasive Spartina alterniflora:biology,ecology and management[J].Acta Phytotaxonomica Sinica,2006,44:559-588.
[10] LI B,LIAO C H,ZHANG X D,et al.Spartina alterniflora invasions in the Yangtze River estuary,China:an overview of current status and ecosystem effects[J].Ecological Engineering,2009,35:511-520.
[11] 鲁如坤.土壤农业化学分析方法[M].北京:中国农业科技出版社,2000.
[12] SEYBOLD C A,MERSIE W,HUANG J Y,et al.Soil redox,pH,temperature,and water-table patterns of a freshwater tidal wetland[J].Wetlands,2002,22:149-158.
[13] DE MARS H,WASSEN M J.Redox potentials in relation to water levels in different mire types in the Netherlands and Poland[J].Plant Ecology,1999,140:41-51.
[14] TANG L,GAO Y,WANG C H,et al.How tidal regime and treatment timing influence the clipping frequency for controlling invasive Spartina alterniflora:implications for reducing management costs[J].Biological Invasions,2010,12:593-601.
[15] MENDOZA U N,DA CRUZ C C,MENEZES MP,et al.Flooding effects on phosphorus dynamics in an Amazonian mangrove forest,Northern Brazil[J].Plant and Soil,2012,353:107-121.
[16] MORRIS J T,HASKIN B.A 5-year record of aerial primary production and stand characteristics of Spartina alterniflora[J].Ecology,1990,71:2209-2217.
[17] TRILLA G G,DE MARCO S,MARCOVECCHIO J,et al.Net primary productivity of Spartina densiflora Brong in an SW Atlantic Coastal Salt Marsh[J].Estuaries and Coasts,2010,33:953-962.
[18] PENNINGS S C,GRANT M B,BERTNESS M D.Plant zonation in low-latitude salt marshes:disentangling the roles of flooding,salinity and competition[J].Journal of Ecology,2005,93:159-167.
[19] DAUSSE A,GARBUTT A,NORMAN L,et al.Biogeochemical functioning of grazed estuarine tidal marshes along a salinity gradient[J].Estuarine Coastal and Shelf Science,2012,100:83-92.
[20] HINES M E,BANTA G T,GIBLIN AE,et al.Acetate concentrations and oxidation in salt-marsh sediments[J].Limnology and Oceanography, 1994,39:140-148.
[21] MOZDZER T J,KIRWAN M,MCGLATHERY K J,et al.Nitrogen uptake by the shoots of smooth cordgrass Spartina alterniflora[J].Marine Ecology-Progress Series, 2011,433:43-52.
[22] EHRENFELD J G,RAVIT B,ELGERSMA K.Feedback in the plant-soil system[J].Annual Review of Environment and Resources,2005,30:75-115.
[23] PATRA S,刘丛强,李思亮,等.长江口溶解无机碳循环的地球化学研究[J].地球与环境,2010,38:409-413.
[24] CHENG X,LUO Y,CHEN J,et al.Short-term C4 plant Spartina alterniflora invasions change the soil carbon in C3 plant-dominated tidal wetlands on a growing estuarine Island[J].Soil Biology and Biochemistry,2006,38:3380-3386.
[25] 祖元刚,李 冉,王文杰,等.我国东北土壤有机碳、无机碳含量与土壤理化性质的相关性[J].生态学报,2011,31:5207-5216.
[26] PILSKALN C H,PADUAN J B,CHAVEZ F P,et al.Carbon export and regeneration in the coastal upwelling system of Monterey Bay,central California[J].Journal of Marine Research,1996,54:1149-1178.
[27] BOUCHARD V,LEFEUVRE J C.Primary production and macro-detritus dynamics in a European salt marsh:carbon and nitrogen budgets[J].Aquatic Botany,2000,67:23-42.
[28] YAN Y,ZHAO B,CHEN J Q,et al.Closing the carbon budget of estuarine wetlands with tower-based measurements and MODIS time series[J].Global Change Biology,2008,14:1690-1702.
[29] TZORTZIOU M,NEALE P J,MEGONIGAL J P,et al.Spatial gradients in dissolved carbon due to tidal marsh outwelling into a Chesapeake Bay estuary[J].Marine Ecology-Progress Series,2011,426:41-56.
[30] WOLFF W J,VANEEDEN M J,LAMMENS E.Primary production and import of particulate organic matter on asalt marsh in the Netherlands[J].Netherlands Journal of Sea Research,1979,13:242-255.
[31] CHMURA G L,HUNG G A.Controls on salt marsh accretion:a test in salt marshes of Eastern Canada[J].Estuaries, 2004,27:70-81.
[32] NEUBAUER S C.Contributions of mineral and organic components to tidal freshwater marsh accretion[J].Estuarine Coastal and Shelf Science,2008,78:78-88.
[33] LOOMIS M J,CRAFT C B.Carbon sequestration and nutrient (nitrogen,phosphorus) accumulation in river-dominated tidal marshes,Georgia,USA[J].Soil Science Society of America Journal,2010,74:1028-1036.
[34] PENG R H,FANG C M,LI B,et al.Spartina alterniflora invasion increases soil inorganic nitrogen pools through interactions with tidal subsidies in the Yangtze Estuary,China[J].Oecologia,2011,165:797-807.
[35] HOWES B L,DACEY J W H,GOEHRINGER D D.Factors controlling the growth form of Spartina alterniflora:feedbacks between aboveground production,sediment oxidation,nitrogen and salinity[J].Journal of Ecology,1986,74:881-898.
[36] 汪承焕.环境变异对崇明东滩优势盐沼植物生长、分布与种间竞争的影响[D].上海:复旦大学,2009.
[1] BU Nai-shun, HU Yue, YANG Xiao, ZHANG Xue, WANG Jian, LI Bo, FANG Chang-ming, SONG You-tao. EFFECTS OF SPARTINA ALTERNIFLORA INVASION ON SOIL PHYSICAL AND CHEMICAL PROPERTIES IN WETLANDS OF THE YANGTZE RIVER ESTUARY [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2017, 26(01): 100-109.
[2] LING Cheng-Xing, ZHANG Fu-Qing, Lin- Hui-. RESEARCH ON EXTRACTING COASTAL WETLANDS WATER INFORMATION USING COMPOSITION CIWI WATER INDEX [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2010, 19(2): 152-.
[3] KUANG Run-Yuan, ZHOU Yun-Han, LI Hang, TIAN Bei. SPATIAL FUZZY COMPREHENSIVE ASSESSMENT OF BIRD HABITAT SUITABILITY IN CHONGMING DONGTAN [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2009, 18(3): 229-233.
[4] ZHENG Zongsheng, ZHOU Yunxuan, LIU Zhiguo, TIAN Bo. DEM RECONSTRUCTION BASED ON HYDRODYNAMIC MODEL AND WATERLINE METHOD [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2008, 17(5): 756-756.
[5] LI Sheng,ZHANG Shougong,YAO Xiaohua,REN Huadong. FFECT OF DIFFERENT LAND USE MODES ON SOIL ENVIRONMENT IN KARST ROCKY DESERTIFICATION ZONE, MIDDLE GUIZHOU PROVINCE OF CHINA [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2008, 17(3): 384-384.
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
[1] LI Na,XU You-peng,CHEN Shuang. INFLUENCE OF URBANIZATION ON PRECIPITATION IN SUZHOU CITY[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2006, 15(3): 335 -339 .
[2] ZHANG Zheng, FU Rongbing, YANG Haizhen, GU Guowei. COMPARISON OF ORGANIC MATTER REMOVAL IN SUBSURFACE |HORIZONTAL FLOW WETLANDS BASED ON WATER BUDGET [J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2007, 16(3): 363 .
[3] SUN Weixia, ZHAO Yongcun, HUANG Biao, LIAO Jingjing, WANG Zhigang, WANG Hongjie. SPATIAL VARIABILITY OF SELENIUM IN SOIL ENVIRONMENT AND  ITS CORRELATION WITH HUMAN HEALTH IN THE YANGTZE RIVER DELTA OF CHINA[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2008, 17(1): 113 .
[4] XU Su-fang, ZHOU Yin-kang. EVALUATION ON THE SUSTAINABILITY IN LAND USE OF DEVELOPMENT ZONE——A CASE STUDY IN WUHU ECONOMIC AND TECHNOLOGICAL DEVELOPMENT ZONE[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2006, 15(4): 453 -457 .
[5] HAO Hanzhou,JIN Menggui,CAO Lijing,XIE Xianjun. APPLICATION OF FUZZY MATHEMATICS IN WATER QUALITY ASSESSMENT[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2006, 15(Sup1): 83 -87 .
[6] LIU Yao-bin,LI Ren-dong. ANALYSIS ON REGIONAL DISPARITY OF ECONOMIC DEVELOPMENT IN HUBEI PROVINCE FROM 1994 TO 2000[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2004, 13(1): 12 -17 .
[7] CHEN Yong-bo. EFFECT OF THE THREE-GORGE PROJECT(TGP) ON THE SUSTAINABLE DEVELOPMENT IN THE YANGTZE BASIN[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2004, 13(2): 109 -113 .
[8] SHI Lian-qiang, LI Jiu-fa, YING Ming, ZUO Shu-hua, XU Hai-gen. EVOLUTIONAL PROCESS IN MEIMAOSHA OF THE YANGTZE RIVER ESTUARY AND ITS RESPONSE TO RESERVOIR PROJECT[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2006, 15(4): 458 -464 .
[9] WENG Junshan, DUAN Ning,ZHANG Ying. PHYSICAL AND CHEMICAL CHARACTERISTICS OF ATMOSPHERIC PARTICLES IN SHUANGQIAO FARM, JIAXING CITY[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2008, 17(1): 129 .
[10] WANG Shu-guo-,|DUAN Xue-jun-,YAO Shi-mou. EVOLUTIONARY CHARACTERISTICS AND DRIVING MECHANISM OF POPULATION DISTRIBUTION IN YANGTZE RIVER DELTA AREA[J]. RESOURCES AND ENVIRONMENT IN THE YANGTZE BASIN, 2007, 16(4): 405 .