土壤矿质氮和可矿化氮对当季作物的贡献

从土壤矿质氮－硝态氮和铵态氮，土壤可矿化氮3个指标研究了土壤剖面不同层次有效氮对作物吸氮的贡献，结果表明，不同指标反映土壤供氮能力状况不一。土壤硝态氮和土壤可矿化氮与作物吸氮有较好的相关关系，而土壤铵态氮与作物氮关系不密切，在深度120cm之上的土层的土壤可矿化氮对作物吸氮有较大的贡献，在考虑土壤供氮能力时，建议应该考虑120cm深层以上的土壤。     

桓台县高产农田土壤硝态氮淋失动态研究

试验研究高产农田生态系统条件下N肥施用量和秸秆还田对土体硝态氮（NO3^--N）的时空分布动态结果表明，NO3^- -N含量在空间上随土壤深度而降低，这一相关关系可用Y=aX^b函数表达。小麦-玉米2季秸秆还田同单季小麦秸秆还田对NO3^- -N的动态影响较小，但相同施N量下未进行玉米秸秆还田0-40cm土层土壤中NO3^- -N含量偏高，土体NO3^- -N有淋失较强的趋势。土体NO3^- -N含量年度内波动大小与施N量密切相关，0-40cm土层土壤内NO3^- -N含量起伏最大，60cm土层以下相对稳定。各土层内NO3^- -N含量与施N量相关密切，这一相关关系影响到2m土层深度。土体中NO3^- -N含量周年内出现2次峰值和1次低谷，峰值出现在玉米和小麦收获后，低谷发生在小麦苗期-开花期土体养分大量吸收时期。9月下旬2m土层土壤NO3^- -N含量可高达10mg/kg，而且有淋失出2m土体的趋势。     

秸秆覆盖方式和施氮量对河套灌区夏玉米氮利用及产量影响

为探究夏玉米氮素转运利用规律、产量及土壤NO3－-N含量分布对秸秆覆盖方式和施氮量的响应，在河套灌区开展2a不同秸秆覆盖方式（秸秆表覆B处理、秸秆深埋S处理）和不同施氮水平（不施氮N0、低氮N1、中氮N2、高氮N3）的田间试验，以传统耕作模式为对照（CK处理）。结果表明：在0～100 cm土层，各处理NO3－-N含量随施氮量增加而增大，成熟期B和CK处理随土层加深呈先减后增趋势，而S处理呈先增后减趋势；B处理提高0～20 cm土层NO3－-N含量，而S处理提高20～40 cm土层NO3－-N含量（P<0.05）；秸秆覆盖可减少0～100 cm土层NO3－-N累积损失量，且显著提高氮肥利用率及夏玉米氮素转运量对籽粒产量的贡献率，SN2处理效果较佳。相比CK处理，成熟期的SN2处理2 a平均NO3－-N累积损失量降低39.6%，氮肥利用率较提高28.5%，夏玉米氮素转运量对籽粒产量的贡献率提高32.1%，增产9.3%。综合分析，秸秆深埋配施中氮效果较佳，可实现河套灌区夏玉米提效增产的目标，并减少深层土壤NO3－-N累积损失量，为优化河套灌区夏玉米耕作施氮模式和缓解农业面源污染提供参考。     

石灰性土壤起始NO3——N对土壤供氮能力测定方法的影响

在陕西省的澄城、永寿、杨陵 3地区选取有机质、全N、硝态N含量差异较大的 17个石灰性土壤 ,分别在淋洗与未淋洗土壤起始NO3--N后 ,利用盆栽试验探讨土壤NO3--N淋洗前、后 ,不同方法测定的已矿化N和可矿化N与小麦吸N量之间的相关性。结果表明 ,未淋洗土壤起始NO3--N ,用KCl直接浸取、KCl煮沸法所浸取以及通气培养前CaCl2 所淋洗的起始NO3--N均与小麦吸N量密切相关 ,相关系数 (r)分别为 0.934 ,0.856和 0.862 ,均达1%显著水准。与此相反 ,通气培养、淹水培养、沸水煮沸、碱性高锰酸钾、酸性高锰酸钾及碱解扩散等方法所提取的可矿化N与小麦吸N量间无显著相关。淋洗土壤起始NO3--N后 ,用KCl直接浸取、KCl煮沸法浸取以及通气培养前CaCl2 所淋洗的起始NO3--N与小麦吸N量之间的相关系数明显降低 ,达不到 5%的显著水准。而通气培养、淹水培养、沸水煮沸、碱性高锰酸钾、酸性高锰酸钾及碱解扩散等方法所提取的可矿化N与小麦吸N量之间相关系数却明显提高 ,都达到 5%或 1%的显著水平。其中变化最明显的是淹水培养 1周矿化出的NH4+-N、通气正式培养 2周矿化出的NO3--N及碱解扩散出的NH4+-N ,其与小麦地上部吸N量之间的相关系数 (r)分别由淋洗前的0.443,0.119,0.259增加到淋洗后的 0.866 ,0.767,0.763。说明可矿化N反映土壤供N能力不佳是因为受起始NO3--N的干扰和影响，在土壤NO3--N含量较高的情况下，要正确评价可矿化N测定方法必须考虑NO3--N的作用。     

不同施氮情况下小麦玉米间作土壤硝态氮的动态变化

本文主要研究了0、210、420和630kg/hm2（NO、N1、N2和N3）4种不同施氮量对小麦玉米间作土壤硝态氮(NO-3-N)含量动态变化的影响。结果表明,0～200cm土层硝态氮的含量整体表现为N3>N2>N1>N0。各生育时期低氮水平下0～60cm土层,中、高氮水平下的0～80cm土层土壤硝态氮含量变化显著。0～60cm土层土壤硝态氮累积量随作物生育时期的变化呈“双峰”曲线,峰值分别出现在小麦挑旗期和玉米大喇叭口期,而60～200cm土层土壤硝态氮累积量的变化呈“单峰”曲线,峰值出现在玉米大喇叭口期。N0处理硝态氮累积量各生育时期变化差异较小。小麦与玉米共生期内0～200cm土层硝态氮含量表现为玉米带>小麦带,差异最大的时期为小麦灌浆期和玉米大喇叭口期。土壤硝态氮向深层的运移量随施氮量增加而增加,与N0相比,施氮后100～200cm土层硝态氮累积量小麦带增加了1053～6253kg/hm2,玉米带增加了1791～7039kg/hm2。优化氮肥施用比例,适当降低小麦播前施氮量可减小土壤硝态氮深层淋溶的风险。     

太湖地区氮肥用量对土壤供氮、水稻吸氮和地下水的影响

利用矿化培养与田间试验的方法,探讨了太湖地区长期施氮条件下,氮肥用量对土壤供氮、水稻吸氮与环境的影响。初步试验结果表明:多年施用氮肥能够提高土壤的供氮能力,并随施N量的增加而增加。增加氮肥用量能够提高稻株含氮量和吸氮量,但氮素向谷粒的转移率降低,试验区水稻氮肥用量以225～270kghm-2左右为佳。稻田田面水和渗漏液的N素养分动态变化显示,施N会造成田面水NH4 N和NO3-N含量的短暂升高,但不同施N量之间相差并不显著。稻田渗漏液中的氮以硝态氮为主,通常在淹水泡田后的7d内有一个NO3-N含量的峰值期,NO3-N含量在1.62～2.75mgL-1之间,约10d后降至0.5mgL-1以下;NH4 N含量变化有随施N量而增加的趋势,高峰期通常出现在分蘖末期,其余时间NH4 N含量在0.2mgL-1以下。     

黑土区水稻土有机氮组分及其对可矿化氮的贡献

采用Bremner法和长期淹水密闭培养法,研究了黑土区不同有机碳水平水稻土有机氮组分及其与可矿化氮的关系。结果表明,土壤酸解氮含量大于非酸解氮。土壤酸解各组分氮含量及其占全氮比例大小的顺序相同,即均为未知态氮氨基酸态氮氨态氮氨基糖态氮。土壤氮素矿化潜力(N0)为38~175.3 mg kg-1,矿化速率常数(k0)为0.022~0.041 d-1。土壤有机碳、全氮含量与氮矿化潜力(N0)之间均呈显著正相关(p0.01或p0.05);土壤C/N、p H与氮素矿化潜力(N0)之间均呈显著正相关(p0.01),而与矿化速率常数(k0)之间则均呈显著负相关(p0.05或p0.01),因此,土壤有机碳(氮)、C/N和p H是影响土壤有机氮素矿化的重要因素。相关分析表明,在各组分有机氮中,酸解氨态氮、酸解氨基酸态氮和非酸解氮均与氮矿化势(N0)关系密切(p0.01),但进一步通过多元回归分析和通径分析表明,酸解氨态氮是对可矿化氮具有直接重要贡献的组分,是土壤可矿化氮的主要来源。     

外加碳、氮对土壤氮矿化、固定与激发效应的影响

本文利用14C和15N对中国生黄绵土(坡地黄绵土)、菜园黄绵土和瑞典耕作草甸土的土壤氮矿化、固定与激发效应进行了研究。结果表明,外加碳、氮能促进土壤氮的矿化、固定与激发效应;促进作用的大小次序为外加NH4-15N大于外加NO3-15N,外加葡萄糖+NH4-15N大于外加葡萄糖+NO3-15N,外加麦秸+NH4-15N大于外加麦秸+NO3-15N,外加葡萄糖+NH4-15大于外加麦秸+NH4-15,外加葡萄糖+NO3-15N大于外加麦秸+NO3-15N;低肥力土壤高于高肥力土壤。在本文中提出了土壤净矿化氮的激发效应、土壤生物固定氮激发效应和土壤总矿化氮的总激发效应的概念,认为土壤氮的总激发效应更能反映土壤氮激发效应的实质。     

氮肥与有机肥配施对设施土壤净矿化氮动态变化的影响

研究设施栽培条件下氮肥与有机肥配施对土壤净矿化氮含量及其速率的动态变化的影响,以评估净矿化氮在设施土壤供氮能力方面的作用,为设施番茄生产的合理施肥提供重要的理论依据。以设施番茄栽培连续7年定位施肥田间试验为依托,选择不同施氮量（N0、N1、N2、N3）和不同氮量配施有机肥（MN0、MN1、MN2、MN3）8个处理土壤,采用室内连续好氧培养方法,研究了各施肥处理土壤净矿化氮含量及净氮矿化速率,分析了土壤净矿化氮含量与可溶性有机氮、微生物量氮含量之间的联系。研究结果表明:在0 ~ 20 cm土层,氮肥与有机肥配施处理土壤全氮和无机氮含量均显著高于单施氮肥处理（P < 0.05）,施氮量对土壤全氮含量无显著影响,但对土壤无机氮含量则有显著影响,随施氮量的增加呈显著增加趋势。在培养过程中,各处理土壤净矿化氮含量随着培养时间延长呈先逐渐增加而后下降趋势,各处理土壤净氮矿化速率在培养7 d时最大,7 ~ 70 d期间快速下降,70 d后呈缓慢下降趋势,氮肥与有机肥配施处理土壤净矿化氮量和净氮矿化速率均显著高于单施氮肥处理（P < 0.05）,氮肥与有机肥配施处理土壤净矿化氮含量和净氮矿化速率随施氮量增加呈下降趋势;与单施氮肥相比,氮肥与有机肥配施显著提高土壤可溶性有机氮与微生物量氮含量（P < 0.05）,但受施氮量影响不显著;土壤净矿化氮含量与可溶性有机氮、微生物量氮之间有密切联系,但与可溶性有机氮之间的密切程度更大。综合来看,MN1、MN2处理可显著提高土壤供氮能力（无机氮 + 净矿化氮）。在设施番茄栽培条件下,连续7年氮肥与有机肥配施可显著提高设施土壤供氮能力,也可较好地协调设施土壤氮素供应与固持的关系。     

旱地土壤的供氮潜力

对潮土、黄褐土、黄棕壤和红壤旱地的供氮潜力进行研究的结果表明,矿化势(No)变化于60340mgkg-1之间,矿化速率常数(K)0.00556-0,01280d-1,矿化势(No)、矿化速率常数(K)和矿化量(Nt)与土壤供氮量均呈显著相关,说明No、Nt和K是土壤供氮潜力的重要参数。这些参数与土壤全氮、有机质、有机氮、易分解有机质、C/N等土壤组成性质密切相关。测定表明,供试土壤粘土矿物多以2:1型为主,土壤固定态铵多在100mgkg-1以上,有部分可重新释放出来,是研究土壤供氮潜力时不容忽视的因素。     

Development of Soil N Testing for Wheat Production using Soil Residual Mineral N

The effects of soil residual nitrate (NO₃-N) and ammonium (NH₄-4) on wheat (Triticum aestivum L.) grain yield and N uptake were evaluated in a three-year experiment from 1991 to 1993, in the province of Quebec, Canada. Soil samples were collected at harvest from the depth of 0-30 and 30–60 cm from 20 wheat sites and analyzed in the laboratory for NO₃-N and NH₄-N. Wheat yield and N-uptake was also determined. Using statistical analysis system (SAS) and Matlab, data were analyzed and the best-fitted regression equations were plotted. Significant amounts of soil NO₃-N was found in the soil ranging from 31.6 to 61.6 kg/ha. The amount of soil NH₄-N varied from 9.2 to 23.3 kg/ha. The statistical effects of model parameters indicated that soil NO₃-N and soil NH₄-N significantly influenced wheat yield and N uptake. It may be possible to investigate wheat behavior at harvest using soil residual NO₃-N and NH₄-N.     

气候-土壤-作物之间氮形态契合在氮肥管理中的关键作用

采用合理的作物养分管理措施对粮食安全保障、土壤与农业可持续发展和生态环境保护至关重要。正确的养分管理策略应是针对某一特定气候-土壤-作物条件选择特定的肥料品种、用量、施用时间和施用位置。然而,当前的氮肥管理措施大多未考虑作物氮形态喜好特性、土壤氮素转化特点以及气候条件等因素的影响,以致在实际生产中效果欠佳。本文提出最大化满足作物氮形态喜好,氮肥形态、土壤氮素转化特点以及气候条件高度契合才能显著提高氮肥利用率,同时降低施氮量、减少活性氮向环境的扩散;气候-土壤-作物之间氮形态契合程度也是引进新的作物或者实施新的施肥措施的重要依据。本文为因地制宜地制定农业减氮增效措施指出了另一个方向。     

长期施肥对土壤有机氮影响研究Ⅰ氮肥及其配施下土壤有机氮组分变化

试验布置在典型的黄土高原的沟壑区，长武试验示范区，在长期的小麦连作的基础上，通过单施氮肥以及氮肥与其它肥料的配合使用，研究不同施肥对土壤有机氮组分的影响，试验结果表明，长期施肥对土壤铵氮和氨基糖氮影响较小，而对土壤氨基酸态氮和酸解和未知态氮影响较大，特别是化学氮肥和有机肥的配施效果较好。     

Soil N Losses by Denitrification Evaluated Using the 15N Tracer Method

Molecular nitrogen (N₂) and nitrous oxide (N₂O) generated by denitrification increase N losses in the soil–plant system. This study aimed to quantify N₂ and N₂O from potassium nitrate (K¹⁵NO₃) applied to soils with different textures and moisture contents in the absence and presence of a source of carbon (C) using the ¹⁵N tracer method. In the three soils used (sandy texture (ST), sandy clay loam texture (SCLT), and clayey texture (CT)), three moisture contents were evaluated (40%, 60%, and 80% of the water holding capacity (WHC)) with (D⁺) and without (D^?) dextrose added. The treatments received 100 mg N kg^?1 (KNO₃ with 23.24 atom% ¹⁵N). N₂ emissions occurred in all of the treatments, but N₂O emissions only occurred in the D⁺ treatment, showing increases with increasing moisture content. SCLT with 80% WHC in the D⁺ treatment exhibited the highest accumulated N emission (48.26 mg kg^?1). The ¹⁵N balance suggested trapping of the gases in the soil.     

供氮方式对黑土土壤无机氮浓度的影响

采用好气恒温培养法,通过一次和分次供氮的方式,研究不同尿素施用量对黑土土壤无机态氮浓度的短期效应。结果表明:CK处理(不供氮方式)在培养期间,NH4+-N的浓度始终保持较低水平,而NO3--N浓度则呈稳步上涨的变化态势;pH值稳定在6.0～6.3之间;硝化率则稳定在90%左右。一次供氮方式各处理NH4+-N的浓度,在施氮后第3d时达到最大,第20d后趋于稳定;NO3--N的浓度则呈稳步增长的态势;土壤的pH值与NH4+-N的浓度的变化规律相似,在培养后的第3d达到峰值,而后开始下降,在培养第10d时,各处理的pH值趋于稳定,且明显低于CK;而硝化率则随着培养时间的延长,呈逐渐增加的变化趋势,在第20d时已与CK无显著差异,趋于平缓。分次供氮各处理在第1次施氮1d后,NH4+-N浓度达到峰值,之后开始呈下降的变化趋势,另外3次施氮后NH4+-N浓度变化与此类似,且每次施肥后第3d和第10d土壤NH4+-N浓度之间差异不显著;NO3--N浓度在第1次施氮1d后,各处理差异不明显,第3d达到最大,但整体上是呈稳步增长的变化趋势;各处理的pH值的变化情况与一次供氮的情况相似;土壤硝化率硝化率呈先下降后上升的趋势,整体呈逐步上升的变化趋势。     

烤田对土壤中氮素和与氮有关的酶活性影响

在水稻分蘖期对5种不同尿素氮肥水平的小区进行烤田5天的试验。试验结果表明,在烤田过程中,脲酶活性变化不明显,呈微弱增加趋势。硝酸还原酶活性急剧降低,羟胺还原酶活性呈波动变化,几乎检测不到亚硝酸还原酶活性。土表的铵态氮也呈波动变化,随着烤田时间的增加铵态氮含量降低。土表的硝态氮浓度不断增加,烤田增大了复水后硝态氮向地下水淋溶的趋势。施氮量越多,土表的矿质氮含量也越多。土壤烤田的主要目的是通过降低土壤的含水量,提高土壤的氧化还原电位,改善土壤的通气状况。     

Soil microbial and extractable C and N after wildfire

 The effect of wildfire on soil microbes and extractable C (C_ext) and N (N_ext) changed with respect to the time from burning and soil depth. Initially, microbial biomass C (C_mic) and N (N_mic) were drastically reduced in the soil surface layer (0–5 cm) and reduced by 50% in the subsurface (5–10 cm), whereas C_ext increased by 62% in the surface layer and did not significantly change in the subsurface. These parameters were affected for the following 4 years, during which the average reductions in the soil surface and subsurface layers were, respectively, 60% and 50% for C_mic, 70% and 45% for N_mic, 60% and 40% for the ratio C_mic: organic C (C_org) and 70% and 30% for the ratio N_mic: total N (N_tot), while for C_ext the surface layer was the only zone consistently affected and C_ext decreased by up to 59%. Immediately after a fire, the C_ext : C_org ratio increased by 3.5-fold and 2-fold in the surface and subsurface layers, respectively; thereafter for 2 years, it decreased in the surface layer (by up to 45%) while the effect on the subsurface layer was not consistent. The effect of burning on N_ext lasted 1 year, in which N_ext increased by up to 7- and 3-fold in the surface and subsurface layers, respectively, while the average N_ext : N_tot ratio doubled in the surface layer and increased by 34% in the subsurface. During the time in which each parameter was affected by burning, the soil factor explained a high percentage of variance in the fluctuations of C_mic, N_mic, C_mic : C_org and N_mic : N_tot, while those of N_ext and N_ext : N_tot, but not those of C_ext and C_ext : C_org depended on both the soil and its depth. In the burned soils similar patterns of response were found between the following parameters listed in pairs: C_mic and N_mic; C_mic : C_org and N_mic : N_tot; C_ext and N_ext; and C_ext : C_org and N_ext : N_tot. However, after the fire relationships found previously between the parameters studied and many other soils properties were either no longer evident, or were inverted. Although the addition of cellulose to the burned soil favoured fungal mycelium development and increased C_mic and C_ext contents, the negative effect of burning on the microbial biomass and the C_ext was not counteracted even under incubation conditions suitable for both microbial growth and C mineralization. Received: 28 May 1997     

土壤全氮含量和施氮水平对棉花产量及氮肥利用效率的影响

为探讨不同土壤全氮含量水平下棉花的氮肥施用效应,采用盆栽试验,研究不同土壤全氮含量(0.58、0.64、0.74、0.83、1.29 g·kg~(-1))和施氮水平(每盆施加量分别为0、1.75、3.50 g)对棉花籽棉产量、氮素吸收、氮肥利用率的影响。结果表明,棉花单株籽棉产量和干物重随施氮量增加而显著增加,土壤全氮含量与施氮水平对棉株根、茎、铃壳部位的干物质积累具有显著的互作效应。同一土壤条件下,棉花单株氮素积累量随施氮水平增加而显著增加。氮肥表观回收率随土壤全氮含量上升呈先降后升的变化趋势,且在土壤全氮含量0.74 g·kg~(-1)时较低,但土壤全氮含量在0.58~0.83 g·kg~(-1)内,不同施氮处理间氮肥表观回收率差异不显著。氮肥农学利用率随土壤全氮含量增加呈下降趋势。土壤全氮含量0.74 g·kg~(-1)时的氮肥生理利用率高于土壤全氮含量0.58、0.64和0.83 g·kg~(-1)。土壤全氮含量1.29g·kg~(-1)条件下,低氮水平氮肥利用效率(表观回收率、农学利用率、生理利用率)显著优于高氮水平;土壤全氮含量0.58~0.74 g·kg~(-1)时,高氮可实现增产增效;土壤全氮含量0.83~1.29 g·kg~(-1)时,低氮能维持较高的产量和氮肥利用率。本研究结果为不同土壤全氮条件下棉花氮肥投入提供了参考。     

Soil N dynamics and N yield of barley grown on Breton loam using N from biological fixation or fertilizer

Summary Soil N dynamics and barley yields (Hordeum vulgare L.) were compared in pot experiments using surface samples from a Gray Luvisol under three cropping systems at Breton, Alberta: (1) an agroecological 8-year rotation including cereals, forage, and fababeans (Vicia faba L.) as green manure, from wich two plots were selected, one following fababeans, and the second following 3 years of forage; (2) a continuous grain system, with fertilizer N at 90 kg ha^-1 year^-1; and (3) a classical Breton 5-year rotation [following oats (Avena sativa L.)] involving forage and cereals, without returning crop residues to the land, selecting one plot with PKS treatment and a second as control. The fertilizer N equivalent for the cropping system; A_N value and A value (analogous to A_N), but in fertilizer ¹⁵N units, soil biomass, and C and N mineralization were monitored. In the first agroecological plot (after fababeans), grain and total plant biomass production were 116% greater than from the continuous grain treatment. Barley plants in the two agroecological plots derived 48.5% and 37.8%, respectively, of their N requirement from non-labelled soil N sources not present in the continuous grain plot. At crop maturity, the recovery of ¹⁵N microbial biomass was 1.5 times higher in soil from the first agroecological plot than from the continuous grain plot. The fertilizer N equivalent was 2670 mg pot^-1 (485 kg ha^-1) for the first and 1850 mg pot^-1 for the second agroecological treatment. Fertilizer N equivalent values exceed net amounts of N mineralized by a factor of 4. Recovery by the barley crop of ¹⁵N added at 55 mg pot^-1 was more efficient in the agroecological treatments (45%–51%) than in the continuous grain or classical Breton treatments (35%–37%). It was concluded (1) that past soil history may be associated more with the ability of barley plants to compete for available N, and hence the use of N, than with net soil N mineralization; and (2) an increased supply of N to crops following the incorporation of fababean residues, manure application, and the soil N-conserving effect of growing legumes were all partly responsible for the observed differences in soil fertility.     

氮肥对水稻不同生长期土壤不同深度氮素渗漏的影响

为了探明太湖地区氮肥施用对水稻不同生长期稻田土壤氮素渗漏的影响,利用渗漏管进行了原位监测。结果表明：①土壤各层(20 ~ 40、40 ~ 60、60 ~ 80和80 ~ 120 cm)渗漏液中铵态氮(NH4+-N)的平均浓度在水稻分蘖期较高,而硝态氮(-N)和全氮(TN-N)的平均浓度则在苗期相对较高。渗漏液中NH4+-N和TN-N浓度随土壤深度增加基本呈降低趋势。②以土壤80 ~ 120 cm深处渗漏量为进入地下水的氮素渗漏量,发现TN-N渗漏量占施肥量的比例为1.69% ~ 2.04%。分蘖期的NH4+-N渗漏量相对较多,而苗期-N和TN-N相对较多,总TN-N渗漏量中NH4+-N和-N基本无差异。③氮肥用量增加降了氮肥利用效率,加剧了土壤各层氮素渗漏风险。当施氮量由N 200增至270 kg/hm2时,氮肥表观利用率下降7.14%,下渗至地下水中的TN-N增加12.3%。