北方稻蟹共作系统氨挥发损失的研究

doi:10.3969/j.issn.1004-1524.2018.04.14

浙江农业学报 ›› 2018, Vol. 30 ›› Issue (4): 622-631.DOI: 10.3969/j.issn.1004-1524.2018.04.14

北方稻蟹共作系统氨挥发损失的研究

王昂^{1, 2, 3}, 马旭洲^{1, 3, *}, 于永清⁴, 徐静⁵, 吕为群^{1, 2, *}

1.上海海洋大学水产科学国家级实验教学示范中心,上海 201306;
2.上海海洋大学水产种质资源开发利用重点实验室,上海 201306;
3.上海海洋大学农业部淡水水产种质资源重点实验室/上海市水产养殖工程技术研究中心/水产动物遗传育种协同创新中心,上海 201306;
4.盘山县河蟹技术研究所,辽宁盘锦 124000;
5.盘山县气象局,辽宁盘锦 124000

收稿日期:2018-01-05 出版日期:2018-04-20 发布日期:2018-04-19
通讯作者: 吕为群,E-mail:wqlv@shou.edu.cn;马旭洲,E-mail:xzma@shou.edu.cn
作者简介:王昂(1986—),男,江苏淮安人,博士研究生,主要从事稻田种养生态系统研究。E-mail:karso135@163.com
基金资助:
上海市现代农业产业技术体系(沪农科产字〔2018〕第4号); 水产动物遗传育种中心上海市协同创新中心 (ZF1206); 国家自然科学基金(31572599)

Ammonia volatilization from rice-crab culture systems in northern China

WANG Ang^{1, 2, 3}, MA Xuzhou^{1, 3, *}, YU Yongqing⁴, XU Jing⁵, LYU Weiqun^{1, 2, *}

1. National Demonstration Center for Experimental Fisheries Science Education, Shanghai Ocean University, Shanghai 201306, China;
2. Key Laboratory of Exploration and Utilization of Aquatic Genetic Resources, Ministry of Education, Shanghai Ocean University, Shanghai 201306, China;
3. Key Laboratory of Freshwater Aquatic Genetic Resources, Ministry of Agriculture/Shanghai Engineering Research Center of Aquaculture/Shanghai Collaborative Innovation for Aquatic Animal Genetics and Breeding, Shanghai Ocean University, Shanghai 201306, China;
4. Panshan Research Institution of Crab Technology, Panjin 124000, China;
5. Panshan County Meteorological Bureau, Panjin 124000, China

Received:2018-01-05 Online:2018-04-20 Published:2018-04-19

摘要/Abstract

摘要： 为探索稻蟹共作系统氨(NH₃)的挥发损失,在辽宁盘锦开展田间实验。实验采用二因素裂区设计,以养蟹为主因素,施肥为副因素,设置4个处理,即单作稻不施肥(R0M)、稻蟹共作不施肥(R0C)、单作稻施肥(R1M)和稻蟹共作施肥(R1C)。结果显示,在水稻全生育期,R0M、R0C、R1M和R1C的NH₃挥发量分别为8.56、7.37、45.64和41.34 kg·hm^-2。施肥是影响稻田NH₃挥发的主要因素,R1M和R1C的NH₃挥发量分别较R0M和R0C提高4.33倍和4.65倍。在施肥稻田,NH₃挥发主要集中在淹水后10 d内,该阶段的挥发量占全生育期的67.6%~76.7%。不施肥稻田的NH₃挥发速率整体较平稳。施肥也显著提高水稻氮(N)素积累量,R1M较R0M提高53.3%,R1C较R0C提高69.7%。养蟹可以降低稻田的NH₃总挥发量,从河蟹放入稻田后计,R1C的NH₃挥发量较R1M降低28.4%,差异显著;然而整个水稻生长季,R1M和R1C处理NH₃的总挥发量无显著差异。R1M和R1C处理NH₃总挥发量分别占当季施N量的28.5%和26.0%。养蟹提高了水稻N素积累量,在水稻成熟期R1C的水稻N素积累量较R1M增加25.0%。在不施肥稻田中,养蟹对削弱NH₃挥发损失和提高水稻N素积累量的效果不显著。

关键词: 稻蟹共作系统, NH3挥发, 田面水, 水稻N素积累量, 相关性

Abstract: In order to explore ammonia volatilization (AV) in the rice-crab system, a field experiment was carried out in Panjin, Liaoning Province. A split-plot design with two factors was arranged in this experiment, no crab and crab as the main factors, with and without fertilizer as sub-factors. The treatments included rice monoculture without fertilizer (R0M), rice-crab culture without fertilizer (R0C), rice monoculture with fertilization (R1M), and rice-crab culture with fertilizer (R1C). AV fluxes were measured via ventilation method. The results showed that seasonal AV losses from R0M, R0C, R1M and R1C fields were 8.56, 7.37, 45.64 and 41.34 kg·hm^-2, respectively. N fertilization was the dominant factor which significantly affected AV losses from the treatments. AV losses from R1M and R1C treatments were 4.33 and 4.65 times than those of R0M and R0C, respectively. In fertilized rice fields, 67.6%-76.7% of the AV losses occurred during 10 days after flooding. The rates of AV losses from no fertilized paddy field were small and stable. Compared with R0M and R0C, amounts of N accumulation in rice plants were significantly increased by 53.3% and 69.7% for R1M and R1C plots. Raising crab could significantly decrease AV losses from rice fields. AV loss from R1C was 28.4% lower than that from R1M treatment after the crab rearing in paddies, but there was little difference between them during the whole rice growth period. AV losses from R1M and R1C accounted for 28.5% and 26.0% of the seasonal N inputs, respectively. Rearing crab in rice fields could increase the amounts of N accumulation in rice plants. At maturity, N accumulation in rice plants in R1C treatment was 25.0% above that in R1M treatment, while the difference of AV and N accumulation were not significant between them under no fertilization.

Key words: rice-crab culture system, ammonia volatilization, flooding water, N accumulation in rice plant, correlation

中图分类号:

S181.6

王昂, 马旭洲, 于永清, 徐静, 吕为群. 北方稻蟹共作系统氨挥发损失的研究[J]. 浙江农业学报, 2018, 30(4): 622-631.

WANG Ang, MA Xuzhou, YU Yongqing, XU Jing, LYU Weiqun. Ammonia volatilization from rice-crab culture systems in northern China[J]. , 2018, 30(4): 622-631.

参考文献

[1] PINDER R W, ADAMS P J,PANDIS S N. Ammonia emission controls as a cost-effective strategy for reducing atmospheric particulate matter in the eastern united states[J]. Environmental Science & Technology , 2007, 41 (2): 380-385.
[2] VITOUSEK P M, ABER J D, HOWARTH R W, et al. Technical report: Human alteration of the global nitrogen cycle: Sources and consequences[J]. Ecological Applications , 1997, 7 (3): 737-750.
[3] LIU S, WANG J J, ZHOU T, et al. Ammonia and greenhouse gas emissions from a subtropical wheat field under different nitrogen fertilization strategies[J]. Journal of Environmental Sciences , 2017, 57 (7): 196-210.
[4] HUANG X, SONG Y, LI M, et al. A high-resolution ammonia emission inventory in China[J]. Global Biogeochemical Cycles , 2012, 26 (1): doi:10.1029/2011GB004161.
[5] 彭世彰,杨士红,徐俊增. 节水灌溉稻田氨挥发损失及影响因素[J]. 农业工程学报, 2009, 25 (8): 35-39.
PENG S Z, YANG S H, XU J Z. Ammonia volatilization and its influence factors of paddy field under water-saving irrigation[J]. Transactions of the CSAE , 2009, 25(8): 35-39. (in Chinese with English abstract)
[6] SHANG Q, GAO C, YANG X, et al. Ammonia volatilization in Chinese double rice-cropping systems: a 3-year field measurement in long-term fertilizer experiments[J]. Biology and Fertility of Soils , 2014, 50: 715-725.
[7] SCHLESINGER W H,HARTLEY A E. A global budget for atmospheric NH 3 [J]. Biogeochemistry , 1992, 15 (3): 191-211.
[8] 宋勇生,范晓晖,林德喜,等. 太湖地区稻田氨挥发及影响因素的研究[J]. 土壤学报, 2004, 41 (2): 265-269.
SONG Y S, FAN X H, LIN D X, et al. Ammonia volatilation from paddy fields in the Taihu lake region and its influencing factors[J]. Acta Pedologica Sinica , 2004, 41(2): 265-269. (in Chinese with English abstract)
[9] 彭显龙,王海含,刘小纶,等. 稻田施尿素后短期内氮素分布和氨挥发损失研究[J]. 东北农业大学学报, 2015, 46 (12): 24-32.
PENG X L, WANG H H, LIU X L, et al. Study on distribution of N and ammonia volatilization of urea within short time after fertilization in paddy soil[J]. Journal of Northeast Agricultural University , 2015, 46(12): 24-32. (in Chinese with English abstract)
[10] LI H, LIANG X Q, LIAN Y F, et al. Reduction of ammonia volatilization from urea by a floating duckweed in flooded rice fields[J]. Soil Science Society of America Journal , 2009, 73 (6): 1890-1895.
[11] LI Y, HUANG L, ZHANG H, et al. Assessment of ammonia volatilization losses and nitrogen utilization during the rice growing season in alkaline salt-affected soils[J]. Sustainability , 2017, 9 (1): 132-146.
[12] CAO Y,YIN B. Effects of integrated high-efficiency practice versus conventional practice on rice yield and N fate[J]. Agriculture Ecosystems & Environment , 2015, 202: 1-7.
[13] SANZ-COBENA A, MISSELBROOK T H, ARCE A, et al. An inhibitor of urease activity effectively reduces ammonia emissions from soil treated with urea under Mediterranean conditions[J]. Agriculture , Ecosystems & Environment , 2008, 126 (3-4): 243-249.
[14] SHANG Q, YANG X, GAO C, et al. Net annual global warming potential and greenhouse gas intensity in Chinese double rice-cropping systems: A 3-year field measurement in long-term fertilizer experiments[J]. Global Change Biology , 2011, 17 (6): 2196-2210.
[15] LIU T Q, FAN D J, ZHANG X X, et al. Deep placement of nitrogen fertilizers reduces ammonia volatilization and increases nitrogen utilization efficiency in no-tillage paddy fields in central China[J]. Field Crops Research , 2015, 184: 80-90.
[16] ZHOU S, HOU H,HOSOMI M. Nitrogen removal, N 2 O Emission, and NH 3 volatilization under different water levels in a vertical flow treatment system[J]. Water , Air , and Soil Pollution , 2008, 191: 171-182.
[17] BOYD C E,TUCKER C S. Sustainability of channel catfish farming[J]. World Aquaculture , 1995, 26 (3): 45-53.
[18] BOULDIN D R, JOHNSON R L, BURDA C, et al. Losses of inorganic nitrogen from aquatic systems[J]. Journal of Environmental Quality , 1974, 3 (2): 107-114.
[19] LI K. Rice-fish culture in China: A review[J]. Aquaculture , 1988, 71: 173-186.
[20] LI C F, CAO C G, WANG J P, et al. Nitrogen losses from integrated rice-duck and rice-fish ecosystems in southern China[J]. Plant and Soil , 2008, 307 (1/2): 207-217.
[21] LI X D, DONG S L, LEI Y Z, et al. The effect of stocking density of Chinese mitten crab Eriocheir sinensis on rice and crab seed yields in rice-crab culture systems[J]. Aquaculture , 2007, 273 (4): 487-493.
[22] 安辉,刘鸣达,王厚鑫,等. 不同稻蟹生产模式对稻蟹产量和稻米品质的影响[J]. 核农学报, 2012, 26 (3): 581-586.
AN H, LIU M D, WANG H X, et al. Effects of different rice-crab production models on rice-crab yield and quality[J]. Journal of Nuclear Agricultural Sciences , 2012, 26(3): 581-586. (in Chinese with English abstract)
[23] 隆斌庆,陈灿,黄璜,等. 稻田生态种养的发展现状与前景分析[J]. 作物研究, 2017, 31(6): 607-612.
LONG B Q, CHEN C, HUANG H, et al. Status and prospect of ecological planting and farming models in paddy fields[J]. Crop Research , 2017, 31(6): 607-612. (in Chinese)
[24] XU J Z, PENG S Z, YANG S H, et al. Ammonia volatilization losses from a rice paddy with different irrigation and nitrogen managements[J]. Agricultural Water Management , 2012, 104 (2): 184-192.
[25] 马玉华,刘兵,张枝盛,等. 免耕稻田氮肥运筹对土壤NH 3 挥发及氮肥利用率的影响[J]. 生态学报, 2013, 33 (18): 5556-5564.
MA Y H, LIU B, ZHANG Z S, et al. Effects of nitrogen management on NH 3 volatilization and nitrogen use efficiency under no-tillage paddy fields[J]. Acta Ecologica Sinica , 2013, 33(18): 5556-5564. (in Chinese with English abstract)
[26] 国家环境保护总局. 水和废水监测分析方法[M]. 4版.北京: 中国环境科学出版社, 2002: 279-281.
[27] 鲍士旦. 土壤农化分析[M]. 3版.北京: 中国农业出版社, 2000: 264-268.
[28] MAKINO A. Photosynthesis, grain yield, and nitrogen utilization in rice and wheat[J]. Plant Physiology , 2011, 155 (1): 125-129.
[29] ZHU X C, WANG X F, LI Z J, et al. Effects of dense planting with less basal N fertilization on rice yield, N use efficiency and greenhouse gas emissions[J]. International Journal of Agriculture & Biology , 2015, 17(6): 1091-1100.
[30] 潘圣刚,黄胜奇,曹凑贵,等. 氮肥运筹对稻田田面水氮素动态变化及氮素吸收利用效率影响[J]. 农业环境科学学报, 2010, 29 (5): 1000-1005.
PAN S G, HUANG S Q, CAO C G, et al. Effects of nitrogen management on dynamics of nitrogen in surface water from rice field and nitrogen use efficiency[J]. Journal of Agro-Environment Science , 2010, 29(5): 1000-1005. (in Chinese with English abstract)
[31] 李洪顺. 氮素运筹对超级杂交水稻氮吸收利用与产量的影响[D].长沙:中南大学, 2010: 35-36.
LI H S. Effect of nitrogen management on absorption and utilization of nitrogen and yield of super hybird rice[D]. Changsha: Central South University, 2010: 35-36. (in Chinese with English abstract)
[32] ZENG Q, GU X, CHEN X, et al. The impact of Chinese mitten crab culture on water quality, sediment and the pelagic and macrobenthic community in the reclamation area of Guchenghu Lake[J]. Fisheries Science , 2013, 79 (4): 689-697.
[33] 孙永健,孙园园,蒋明金,等. 施肥水平对不同氮效率水稻氮素利用特征及产量的影响[J]. 中国农业科学, 2016, 49 (24): 4745-4756.
SUN Y J, SUN Y Y, JIANG M J, et al. Effects of fertilizer levels on nitrogen utilization characteristics and yield in rice cultivars with different nitrogen use efficiencies[J]. Scientia Acricultura Sinica ,2016,49(24): 4745-4756. (in Chinese with English abstract)
[34] 陈飞星,张增杰. 稻田养蟹模式的生态经济分析[J]. 应用生态学报, 2002, 13 (3): 323-326.
CHEN F X, ZHANG Z J. Ecological economic analysis of rice-crab model[J]. Chinese Journal of Applied Ecology , 2002, 13(3): 323-326. (in Chinese with English abstract)
[35] 李洪亮,孙玉友,曲金玲,等. 施氮量对东北粳稻根系形态生理特征的影响[J]. 中国水稻科学, 2012, 26 (6): 723-730.
LI H L, SUN Y Y, QU J L, et al. Influence of nitrogen levels on morphological and physiological characteristics of root system in japonica rice in northeast China[J]. Chinese Journal of Rice Science , 2012, 26(6): 723-730. (in Chinese with English abstract)
[36] BAUTISTA E U, KOIKE M,SUMINISTRADO D C. Mechanical deep placement of nitrogen in wetland rice[J]. Journal of Agricultural Engineering Research , 2001, 78 (4): 333-346.
[37] SOMMER S G, SCHJOERRING J K,DENMEAD O T. Ammonia emission from mineral fertilizers and fertilized crops[J]. Advances in Agronomy , 2004, 82 (3): 557-622.
[38] LI C, CAO C, WANG J, et al. Nitrogen losses from integrated rice-duck and rice-fish ecosystems in southern China[J]. Plant and Soil , 2008, 307 (1-2): 207-217.
[39] LI P, LU J, HOU W, et al. Reducing nitrogen losses through ammonia volatilization and surface runoff to improve apparent nitrogen recovery of double cropping of late rice using controlled release urea[J]. Environmental Science & Pollution Research , 2017, 24 (12): 1-12.
[40] 钱龙,赵依民,王晓毅. 氨对河蟹幼体的急性毒性试验[J]. 淡水渔业, 1987 (2): 28-29.
QIAN L, ZHAO Y M, WANG X Y. Acute toxicity test of ammonia to larvae crab[J]. Freshwater Fisheries , 1987 (2): 28-29. (in Chinese)
[41] LIAO L, SHAO X, JI R, et al. Ammonia volatilization from direct seeded later-rice fields as affected by irrigation and nitrogen managements[J]. International Journal of Agriculture and Biology , 2015, 17(3): 582-588.
[42] HAYASHI K, NISHIMURA S,YAGI K. Ammonia volatilization from a paddy field following applications of urea: rice plants are both an absorber and an emitter for atmospheric ammonia[J]. Science of the Total Environment , 2008, 390(2/3): 485-494.
[43] ZHANG Q, LV D, MA X, et al. The effects of different transplanting ways on the phytoplankton community in rice-crab culture system[J]. Journal of Food Agriculture & Environment , 2014, 12 (1): 199-204.
[44] 陈振华,陈利军,武志杰,等. 辽河下游平原不同水分条件下稻田氨挥发[J]. 应用生态学报, 2007, 18 (12): 2771-2776.
CHEN Z H, CHEN L J, WU Z J, et al. Ammonia volatilization from rice field under different water conditions in lower Liaohe River Plain[J]. Chinese Journal of Applied Ecology , 2007, 18(12): 2771-2776. (in Chinese with English abstract)
[45] 郝晓晖,肖宏宇,苏以荣,等. 长期不同施肥稻田土壤的氮素形态及矿化作用特征[J]. 浙江大学学报(农业与生命科学版), 2007, 33 (5): 544-550.
HAO X H, XIAO H Y, SU Y R, et al. Characteristics of nitrogen forms and mineralization in paddy soils of long-term fertilization experiment[J]. Journal of Zhejiang University ( Agriculture & Life Sciences ), 2007, 33(5): 544-550. (in Chinese with English abstract)
[46] 孙文通,张庆阳,马旭洲,等. 不同河蟹放养密度对养蟹稻田水环境及水稻产量影响的研究[J]. 上海海洋大学学报, 2014, 23 (3): 366-373.
SUN W T, ZHANG Q Y, MA X Z, et al. A study on effects of different crab stocking density on water environment and rice yield[J]. Journal of Shanghai Ocean University , 2014, 23(3): 366-373. (in Chinese with English abstract)
[47] 张启明,铁文霞,尹斌,等. 藻类在稻田生态系统中的作用及其对氨挥发损失的影响[J]. 土壤, 2006, 38 (6): 814-819.
ZHANG Q M, TIE W X, YIN B, et al. Algae function in paddy field ecosystem and its effect on reducing ammonia volatilization from paddy fields[J]. Soils , 2006, 38(6): 814-819. (in Chinese with English abstract)
[48] 汪清,王武,马旭洲,等. 稻蟹共作对土壤理化性质的影响[J]. 湖北农业科学, 2011, 50 (19): 3948-3952.
WANG Q, WANG W, MA X Z, et al. The effects of integrated rice-crab production on soil physical and chemical properties[J]. Hubei Agriculture Sciences , 2011, 50(19): 3948-3952. (in Chinese with English abstract)
[49] 徐敏,马旭洲,王武. 稻蟹共生系统水稻栽培模式对水稻和河蟹的影响[J]. 中国农业科学, 2014, 47 (9): 1828-1835.
XU M, MA X Z, WANG W. Effects of different cultivation patterns on rice yield and crab in rice-crab culture system[J]. Scientia Agricultura Sinica , 2014, 47(9): 1828-1835. (in Chinese with English abstract)
[50] LIANG K, ZHONG X, HUANG N, et al. Nitrogen losses and greenhouse gas emissions under different N and water management in a subtropical double-season rice cropping system[J]. Science of the Total Environment , 2017, 609: 46-57.
[51] ZHANG M, YAO Y, ZHAO M, et al. Integration of urea deep placement and organic addition for improving yield and soil properties and decreasing N loss in paddy field[J]. Agriculture Ecosystems & Environment , 2017, 247: 236-245.

北方稻蟹共作系统氨挥发损失的研究

Ammonia volatilization from rice-crab culture systems in northern China

RichHTML

PDF (PC)

可视化

摘要/Abstract

引用本文

使用本文

参考文献

相关文章 15

编辑推荐

Metrics

本文评价

[1]	董艳敏, 严奉宪. 中国农业高质量发展的时空特征与协调度[J]. 浙江农业学报, 2021, 33(1): 170-182.
[2]	沈迪, 陈龙正, 路晓华, 陶建平, 冯顾城, 刘洁霞, 冯凯, 尹莲, 丁旭, 贾丽丽, 徐志胜, 刘惠吉, 熊爱生. 苏南地区29个秋冬茬芹菜品种资源评价[J]. 浙江农业学报, 2020, 32(4): 653-660.
[3]	张雄一, 徐新良, 张正, 庄大春, 曾钦, 毕仁贵, 严灿. 2000—2017年中国农业机械总动力水平空间演变特征[J]. 浙江农业学报, 2020, 32(4): 714-722.
[4]	白俊艳, 卢军浩, 付学言, 武晓红, 杨又兵, 雷莹, 庞有志, 卢小宁, 巩慧荣, 胡陆星, 刘红涛, 樊红灯, 曹恒, 时坤鹏, 陈梦柯, 马永康. 蛋用鹌鹑IGF-1R基因的多态性与体尺性状相关性分析[J]. 浙江农业学报, 2020, 32(3): 398-405.
[5]	辛世杰, 王晓慧, 戴国俊, 安婷婷, 张涛, 张跟喜, 谢恺舟, 王金玉, 王宏胜. 京海黄鸡柔嫩艾美尔球虫感染对脾脏和盲肠IL-6、IL-8、CCLi2基因表达量的影响及其相关性[J]. 浙江农业学报, 2019, 31(1): 39-46.
[6]	程远, 万红建, 刘超超, 姚祝平, 叶青静, 李志邈, 王荣青, 周国治, 杨悦俭, 陈德梁, 阮美颖. 十六个樱桃番茄品种果实风味品质相关指标比较分析[J]. 浙江农业学报, 2018, 30(11): 1859-1869.
[7]	徐睿, 张雅楠, 林子翔, 廖万甜, 胡镥巍, 祝彪, 朱祝军. 观赏辣椒种质资源农艺性状遗传多样性关联分析[J]. 浙江农业学报, 2018, 30(11): 1886-1892.
[8]	王道泽, 洪文英, 吴燕君, 陈瑞, 胡选祥. 水稻主栽品种和气象因素对稻瘟病田间流行的影响[J]. 浙江农业学报, 2017, 29(5): 791-798.
[9]	冯云钰, 罗龙皂, 田光明. 菜-稻耦合梯级消纳氮磷模式研究[J]. 浙江农业学报, 2017, 29(3): 469-476.
[10]	李琦, 刘双. 影响苏尼特放牧羊体质量变化的相关因素分析[J]. 浙江农业学报, 2017, 29(10): 1630-1636.
[11]	陈青1，陈再鸣2，*，钱琼秋2，余维良3，郑明海3，王松4，水狄云4. 培养料理化性状与秀珍菇菌丝营养和生殖生长的相关性[J]. 浙江农业学报, 2016, 28(5): 763-.
[12]	袁菊红, 胡绵好. 处理下彩叶草体内元素含量分布及相关性分析[J]. 浙江农业学报, 2016, 28(12): 2098-2108.
[13]	徐云焕, 梁森苗, 郑锡良, 任海英, 戚行江. 叶面营养对杨梅果实产量和品质的影响及各指标的相关性[J]. 浙江农业学报, 2016, 28(10): 1711-1717.
[14]	许童羽, 洪雪, 陈春玲, 周云成, 曹英丽, 于丰华, 李娜. 基于冠层NDVI数据的北方粳稻产量模型研究[J]. 浙江农业学报, 2016, 28(10): 1790-1795.
[15]	王志明1，王婕姝1，王毅2，韩向敏1，*，王华1. 甘肃高山细毛羊体重与体尺指标的相关性研究[J]. 浙江农业学报, 2016, 28(1): 28-.