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      有機(jī)無(wú)機(jī)復(fù)混肥對(duì)水稻土烤煙養(yǎng)分積累、分配與利用的影響

      2019-09-10 07:22:44朱英華田維強(qiáng)芶劍渝
      中國(guó)煙草科學(xué) 2019年2期
      關(guān)鍵詞:烤煙

      朱英華 田維強(qiáng) 芶劍渝

      摘? 要:為了實(shí)現(xiàn)烤煙施肥的輕簡(jiǎn)化,采用框栽試驗(yàn),測(cè)定和分析了不同施肥處理(空白,不施肥;CK,煙草專(zhuān)用復(fù)合肥;H1,有機(jī)無(wú)機(jī)肥料配比1:1;H2,有機(jī)無(wú)機(jī)肥料配比2:1)對(duì)烤煙干物質(zhì)及養(yǎng)分積累,養(yǎng)分分配率和表觀及經(jīng)濟(jì)利用率的影響。結(jié)果表明,與空白相比,施肥處理極顯著提高了烤煙干物質(zhì)及養(yǎng)分積累量。與CK相比,H1處理煙株鉀的積累量和表觀及經(jīng)濟(jì)利用率極顯著提高,其表觀和經(jīng)濟(jì)利用率分別增加了24.85和19.16個(gè)百分點(diǎn);H2處理煙株根、莖、葉的干物質(zhì)及氮、磷、鉀積累量顯著或極顯著增加,其氮、磷、鉀的表觀利用率極顯著提高,分別提高了21.15、6.10和24.59個(gè)百分點(diǎn),經(jīng)濟(jì)利用率顯著或極顯著增加,分別增加了10.97、3.79和18.44個(gè)百分點(diǎn);H1和H2處理均降低了煙葉氮分配率,提高了鉀的分配率。綜合來(lái)看,以H2處理的表現(xiàn)較好。

      關(guān)鍵詞:烤煙;有機(jī)無(wú)機(jī)復(fù)混肥;養(yǎng)分利用率;養(yǎng)分積累;養(yǎng)分分配率

      中圖分類(lèi)號(hào):S572.06????????? 文章編號(hào):1007-5119(2019)02-0030-08????? DOI:10.13496/j.issn.1007-5119.2019.02.005

      Abstract: In order to simplify the fertilization of flue-cured tobacco in mountainous regions, a pot experiment was carried out to determine and analyze the effects of different fertilization treatments (blank, no fertilization; CK, fusible tobacco special compound fertilizer; H1 treatment, organic fertilizer: inorganic fertilizer=1∶1, H2 treatment, organic fertilizer∶inorganic fertilizer=2∶1) on dry matter and nutrient accumulation, nutrient distribution ratio, and nutrient utilization ratio of flue-cured tobacco root, stem and leaf. The results showed that compared with the blank, accumulation of dry matter and N, P, K of root, stem, leaf and whole plant was significantly (p≤0.01) increased in the other treatments. Compared with the CK, the K accumulation amount, apparent utilization ratio and economic utilization ratio of H1 treatment were increased significantly (p≤0.01), and that the apparent utilization ratio and economic utilization ratio of H1 treatment were increased 24.85 and 19.16 percentage points, respectively. The accumulation of dry matter and N, P, K of root, stem and leaf of H2 treatment were significantly (p≤0.05 or p≤0.01) increased and the apparent utilization ratios of N, P, K were significantly (p≤0.01) increased, which was 21.15, 6.10 and 24.59 percent higher than the CK, respectively. Simultaneously, the economic utilization ratios of N, P, K of H2 treatment were significantly (p≤0.05 or p≤0.01) increased by 10.97, 3.79 and 18.44 percentage points compared to the CK, respectively. Compared with the CK, the N distribution ratio of leaves was reduced while that of K was increased in organic-inorganic compound fertilizer (H1 and H2). ?In summary, H2 treatment showed the best performance.

      常規(guī)農(nóng)業(yè)長(zhǎng)期施用化肥引起了土壤養(yǎng)分失衡、酸化、鹽漬化等一系列環(huán)境污染問(wèn)題,影響了土壤微生物區(qū)系和作物對(duì)養(yǎng)分的吸收與利用[1];而有機(jī)農(nóng)業(yè)則會(huì)導(dǎo)致糧食作物、蔬菜和果樹(shù)減產(chǎn)[2-3]。由此可見(jiàn),單施有機(jī)肥或化肥均不利于作物產(chǎn)量和品質(zhì)的提高[4],有機(jī)-無(wú)機(jī)復(fù)合農(nóng)業(yè)是未來(lái)世界農(nóng)業(yè)發(fā)展的方向[5],有機(jī)無(wú)機(jī)肥料配施和有機(jī)肥料部分替代無(wú)機(jī)肥料也成為研究的熱點(diǎn)。但在常規(guī)農(nóng)業(yè)的基礎(chǔ)上增施有機(jī)肥,無(wú)形中增加了施肥用工量和種植成本,不利于農(nóng)業(yè)輕簡(jiǎn)化栽培的發(fā)展;而有機(jī)無(wú)機(jī)復(fù)混肥是將有機(jī)物料和無(wú)機(jī)肥料按一定比例混合,采用一定制造工藝加工復(fù)合而成,既含有有機(jī)質(zhì),又含有化學(xué)肥料養(yǎng)分[6],有機(jī)無(wú)機(jī)肥料一次性施入土壤,節(jié)省了施肥用工成本。許多研究表明,有機(jī)無(wú)機(jī)復(fù)混肥能提高番茄[7]、葉類(lèi)蔬菜[8]、水稻[9-10]、小麥[11-12]、玉米[13]、辣椒[14]等作物產(chǎn)量,改善土壤結(jié)構(gòu)和微生物性狀及酶活性[9,12,15],提高作物養(yǎng)分吸收量和利用率[6,10,11,13]。前人對(duì)有機(jī)肥在烤煙生產(chǎn)中的應(yīng)用做了大量研究[16-23],但采用框栽試驗(yàn)研究有機(jī)無(wú)機(jī)復(fù)混肥對(duì)烤煙養(yǎng)分積累、分配及利用的影響鮮見(jiàn)報(bào)道。本研究旨在通過(guò)有機(jī)無(wú)機(jī)復(fù)混肥對(duì)水稻土烤煙干物質(zhì)和養(yǎng)分積累量、分配率及利用率影響的研究,為貴州烤煙生產(chǎn)有機(jī)肥料部分替代無(wú)機(jī)肥料和輕簡(jiǎn)化施肥提供理論依據(jù)和技術(shù)支撐。

      1? 材料與方法

      1.1? 試驗(yàn)材料

      試驗(yàn)于2017年4—10月在貴州省遵義市煙草公司湄潭科技園進(jìn)行,采用正方形可拆卸塑料框(邊長(zhǎng)42 cm,高60 cm)內(nèi)襯黑色塑料袋,供試品種為烤煙K326。試驗(yàn)土壤為水稻土,土壤堿解氮174.23 mg/kg、速效磷為18.85 mg/kg、速效鉀125.25 mg/kg、有機(jī)質(zhì)1.75%、pH 5.67。將水稻土0~20 cm的耕作層土壤晾(曬)干,粉碎后用3 mm孔徑篩子過(guò)篩并充分混合均勻。每框裝土量125 kg(土與煙框上口齊平)。裝好土后,用直徑10 cm塑料管,做成高20 cm套筒,將其垂直插入裝滿土的煙框中心點(diǎn)位置,將套筒內(nèi)土取出,再將各處理基肥(每框按施肥量稱準(zhǔn)確)施入套筒底部土壤,并與套筒底部土壤充分混均,再將取出的土裝回,將煙苗栽入煙框中心點(diǎn)位置,各框煙苗栽入深度相同,根系距施肥位置至少5 cm。

      1.2? 試驗(yàn)設(shè)計(jì)

      試驗(yàn)采用隨機(jī)區(qū)組設(shè)計(jì),設(shè)空白、CK(對(duì)照)、H1和H2共4個(gè)處理,3次重復(fù)??瞻诪椴皇┓剩珻K為煙草專(zhuān)用復(fù)合肥基肥(氮、磷和鉀的含量分別為10%、3.9%和20.7%)+追肥(氮、磷、鉀的含量分別為15%、0%和24.9%),H1和H2處理均為有機(jī)無(wú)機(jī)復(fù)混肥,有機(jī)無(wú)機(jī)復(fù)混肥為有機(jī)肥與無(wú)機(jī)肥按照相應(yīng)比例混合后擠壓造粒,H1處理為1∶1有機(jī)無(wú)機(jī)復(fù)混肥基肥(無(wú)機(jī)氮、磷和鉀的含量分別為2.5%、2.5%和6.0%,有機(jī)氮、磷和鉀的含量分別為3.4%、0%和3.5%,C/N為4.5)+追肥(氮、磷、鉀含量分別為12%、0%和27.3%),H2處理為2︰1有機(jī)無(wú)機(jī)復(fù)混肥基肥(無(wú)機(jī)氮、磷和鉀的含量分別為1.7%、1.7%和4.0%,有機(jī)氮、磷和鉀的含量分別為2.6%、0%和2.8%,C/N為7.7)+追肥(氮、磷、鉀含量分別為12%、0%和27.3%)。不同處理之間的純氮施用量一致,在此基礎(chǔ)上,通過(guò)調(diào)整追肥的不同養(yǎng)分比例,盡量縮小不同處理之間磷、鉀施用量差異。CK基肥純氮施用量均為4.17 g/框,磷用量為1.63 g/框,鉀用量為8.63 g/框; H1處理的基肥純氮施用量均為4.17 g/框,磷用量為1.77 g/框,鉀用量為6.71 g/框;H2處理的基肥純氮施用量均為4.17 g/框,磷用量為1.65 g/框,鉀用量為6.60 g/框。追肥為氮鉀二元復(fù)合肥,CK純氮施用量為1.88 g/框,鉀用量為3.11 g/框;H1和H2處理純氮施用量均為1.88 g/框,鉀用量為4.28 g/框,其他栽培措施按照當(dāng)?shù)貎?yōu)質(zhì)煙葉生產(chǎn)方案執(zhí)行。

      1.3? 測(cè)定項(xiàng)目與方法

      烤煙現(xiàn)蕾打頂后,煙葉成熟分次采收,根、莖在煙葉采收結(jié)束后一次性收獲,收獲后均采用105 ℃殺青,65 ℃烘干、稱重;同一煙株分次采收的煙葉充分混勻,根、莖、葉磨細(xì)后均采用硫酸-過(guò)氧化氫消煮,全自動(dòng)定氮儀測(cè)定氮含量、分光光度法測(cè)定磷含量、火焰原子吸收分光光度法測(cè)定鉀含量[24],根據(jù)根、莖、葉的干物質(zhì)積累量及氮磷鉀含量計(jì)算整株干物質(zhì)及氮磷鉀積累量。

      1.4? 養(yǎng)分利用率計(jì)算方法

      表觀利用率=[(施肥處理煙株吸收該養(yǎng)分總量-空白煙株吸收該養(yǎng)分量)/每株肥料施入該養(yǎng)分量]×100%

      經(jīng)濟(jì)利用率=[(施肥處理煙葉吸收該養(yǎng)分總量-空白煙葉吸收該養(yǎng)分量)/每株肥料施入該養(yǎng)分量]×100%

      2? 結(jié)? 果

      2.1? 不同肥料處理對(duì)烤煙干物質(zhì)積累的影響

      由圖1可知,與空白相比,施肥處理煙株的根、莖、葉及全株的干物質(zhì)積累量均極顯著增加。與CK相比,H1處理煙株根、莖干物質(zhì)積累量顯著增加,增幅分別為24.67%和24.67%,葉片及全株干物質(zhì)積累量無(wú)顯著變化;H2處理煙葉干物質(zhì)積累量顯著增加,增幅為37.51%,根、莖和全株的干物質(zhì)積累量均極顯著提高,增幅分別為37.50%、35.11%和36.19%。H1和H2處理間煙株各器官及全株的干物質(zhì)積累量無(wú)顯著差異。在本試驗(yàn)條件下,H2處理更有利于烤煙不同器官及全株的干物質(zhì)積累。

      2.2? 不同肥料處理對(duì)烤煙不同器官N素含量和積累量的影響

      由圖2a可知,與空白相比,施肥處理煙株根、葉及全株的氮含量極顯著提高。與CK相比,H1處理煙株的根、莖氮含量顯著增加,增幅分別為7.52%和8.63%;H2處理的烤煙莖的氮含量極顯著提高,增幅為12.24%,其根、葉及全株的氮含量無(wú)顯著變化。H1和H2處理之間不同器官氮含量差異均未達(dá)到顯著水平。由此可見(jiàn),有機(jī)無(wú)機(jī)復(fù)混肥的施用提高了煙株根、莖的氮含量。

      由圖2b可見(jiàn),與空白相比,施肥處理煙株的根、莖、葉及全株的氮積累量均極顯著增加。與CK相比,H1處理煙株根、莖氮積累量極顯著提高,分別提高了34.66%和35.03%,全株的氮積累量顯著增加,增加了24.38%;H2處理煙株葉片氮積累量顯著提高,提高了32.54%,根、莖和全株的氮積累量極顯著增加,增幅分別為40.92%、54.51%和38.01%。

      2.3? 不同肥料處理對(duì)烤煙不同器官P素含量和積累量的影響

      由圖3a可知,與空白相比,施肥處理煙株的莖、葉及全株的磷含量均極顯著增加。與CK相比,H1處理煙株根的磷含量顯著降低,降低了11.90%,莖的磷含量極顯著增加,增加了28.17%,葉片及全株的磷含量無(wú)顯著變化;H2處理煙株的莖磷含量極顯著提高,提高了14.79%,根、葉片及全株磷含量均沒(méi)有顯著變化。H2處理煙株根磷含量顯著高于H1,但其莖磷含量顯著低于H1,2個(gè)處理之間的葉片及全株的磷含量差異不顯著。由此可見(jiàn),施用有機(jī)無(wú)機(jī)復(fù)混肥極顯著促進(jìn)了煙株莖磷含量提高,但對(duì)葉片及全株磷含量影響不大。

      2.4? 不同肥料處理對(duì)烤煙不同器官K素含量和積累量的影響

      由圖4a可見(jiàn),與空白相比,施肥處理煙株根、莖、葉及全株的鉀含量均極顯著提高。與CK相比,H1和H2處理煙株根、莖、葉及全株鉀含量均極顯著提高,H1處理分別增加了30.27%、21.24%、44.84%、33.16%,H2處理分別提高了40.92%、9.09%、30.53%、22.70%。H2處理煙株根系鉀含量極顯著高于H1處理,而H1處理煙株的莖、葉片及全株鉀含量極顯著高于H2處理。

      2.5? 不同肥料處理對(duì)烤煙各器官氮、磷、鉀養(yǎng)分分配的影響

      圖5可知,與空白相比,H1處理煙株根、莖的氮分配率顯著提高,而葉片的氮分配率極顯著降低,H2處理煙株莖氮分配率極顯著提高,葉的氮分配率顯著降低;H1和H2煙株莖的磷分配率極顯著提高,根、葉無(wú)顯著變化;H1處理根系鉀分配率顯著降低,而葉片鉀分配率顯著增加。與CK相比,H1處理煙株根、莖氮分配率分別增加了1.73和1.44個(gè)百分點(diǎn),鉀分配率分別降低了3.05和1.42個(gè)百分點(diǎn),煙葉的氮分配率降低了3.18個(gè)百分點(diǎn),鉀增加了4.47個(gè)百分點(diǎn);H2處理煙株根、莖氮分配率分別增加了0.45和2.02個(gè)百分點(diǎn),鉀分配率降低了1.65和2.0個(gè)百分點(diǎn),葉片的氮分配率降低了2.46個(gè)百分點(diǎn),鉀分配率增加了3.66個(gè)百分點(diǎn)。由此可見(jiàn),施用有機(jī)無(wú)機(jī)復(fù)混肥提高了煙株根、莖的氮和葉片鉀分配率,降低了煙葉氮和根、莖的鉀分配率。

      2.6? 不同肥料處理對(duì)烤煙氮、磷、鉀養(yǎng)分利用的影響

      圖6a可知,與CK相比,H1處理煙株的氮、鉀表觀利用率極顯著提高,分別提高了15.48和24.85個(gè)百分點(diǎn),其磷的表觀利用率無(wú)顯著變化;H2煙株氮、磷、鉀的表觀利用率極顯著提高,分別提高了21.15、6.10和24.59個(gè)百分點(diǎn);H1和H2處理之間煙株氮、磷、鉀的表觀利用率差異均不顯著。由此可見(jiàn),施用有機(jī)無(wú)機(jī)復(fù)混肥極顯著提高了煙株氮和鉀的表觀利用率。

      由圖6b可見(jiàn),與CK相比,H1和H2處理煙株鉀經(jīng)濟(jì)利用率極顯著提高,分別提高了19.16和18.44個(gè)百分點(diǎn);H2處理煙株磷經(jīng)濟(jì)利用率極顯著提高,提高了3.79百分點(diǎn),氮經(jīng)濟(jì)利用率顯著增加,增加了10.97個(gè)百分點(diǎn)。由此可見(jiàn),施用有機(jī)無(wú)機(jī)復(fù)混肥極顯著提高煙株鉀素的經(jīng)濟(jì)利用率;在本試驗(yàn)條件下,H2顯著或極顯著促進(jìn)了煙株氮、磷、鉀經(jīng)濟(jì)利用率和表觀利用率的提高。

      3? 討? 論

      與不施肥相比,施肥顯著提高了糧食及蔬菜等作物的干物質(zhì)和養(yǎng)分積累量[9-14]。本試驗(yàn)條件下,施肥極顯著促進(jìn)了烤煙根、莖、葉及全株的干物質(zhì)積累。與單施化肥相比,有機(jī)無(wú)機(jī)配施能顯著提高作物產(chǎn)量[9-10,13-14,16];在化肥減量20%條件下,精制有機(jī)肥對(duì)煙葉產(chǎn)量無(wú)顯著影響,生物有機(jī)肥使煙葉產(chǎn)量提高了30.02%[25];也有研究認(rèn)為,有機(jī)無(wú)機(jī)配施促進(jìn)烤煙干物質(zhì)積累,尤其是促進(jìn)烤煙生長(zhǎng)后期干物質(zhì)的積累[26]。本試驗(yàn)條件下,H1處理對(duì)煙株葉片及全株干物質(zhì)積累量影響不大,H2處理顯著或極顯著提高了煙株葉、根、莖和全株的干物質(zhì)積累量。不同有機(jī)無(wú)機(jī)比例的復(fù)混肥表現(xiàn)出的煙株不同器官干物質(zhì)積累量差異,可能是不同有機(jī)無(wú)機(jī)復(fù)混肥中C/N不同,影響了土壤中微生物次生代謝物質(zhì)種類(lèi)、數(shù)量、活性和養(yǎng)分吸收及利用效率[12-15,18]。

      與單施化肥相比,有機(jī)無(wú)機(jī)肥料配施促進(jìn)了烤煙生長(zhǎng)后期鉀的吸收[26]和煙葉鉀含量提高,降低煙葉氮含量,尤其是降低了上部煙葉氮和煙堿含量[18]。本試驗(yàn)條件下,2個(gè)有機(jī)無(wú)機(jī)復(fù)混肥處理煙株根、莖、葉及全株的鉀含量極顯著增加,但煙葉氮含量略降低,這與唐莉娜等[18]研究結(jié)果基本一致。有機(jī)無(wú)機(jī)肥料配施促進(jìn)了煙株氮、磷、鉀積累量的提高[25-26]。本試驗(yàn)條件下,有機(jī)無(wú)機(jī)復(fù)混肥顯著或極顯著提高了烤煙根、莖、葉和全株的鉀積累量,這可能是有機(jī)物物料分解過(guò)程中產(chǎn)生的有機(jī)酸溶解了土壤中難溶性鉀,提高鉀的有效性,促進(jìn)了鉀吸收量[18,26]。2∶1有機(jī)無(wú)機(jī)復(fù)混肥(H2)顯著或極顯著促進(jìn)煙株根、莖、葉和全株的氮、磷積累量,這與前人的研究結(jié)果基本相同[9-14]。

      與單施化肥相比,有機(jī)無(wú)機(jī)配施可明顯提高煙葉中磷、鉀和根系中氮素的分配比例,降低莖稈中氮、磷、鉀分配比例[27],但孟蕾等[29]研究認(rèn)為,施用發(fā)酵餅肥對(duì)烤煙各器官的氮分配率沒(méi)有影響。本試驗(yàn)條件下,有機(jī)無(wú)機(jī)復(fù)混肥降低了煙葉氮素和根、莖鉀素分配率,提高了煙葉鉀素和根、莖氮素的分配率。這可能是有機(jī)無(wú)機(jī)肥料配比、肥料養(yǎng)分含量或煙株收獲時(shí)間等因素差異造成的。有機(jī)肥增加了土壤保肥性[18],提高了土壤養(yǎng)分供給能力[9,10,30],顯著提高了氮、磷、鉀的表觀利用效率和經(jīng)濟(jì)利用率[6,9-14,27,30];在化肥減量20%條件下,精制有機(jī)肥煙株氮、磷、鉀的表觀利用率分別增加了18.44%、40.60%、18.37%,生物有機(jī)肥則分別增加了69.49%、60.94%、39.36%[25]。本試驗(yàn)條件下,與CK相比,有機(jī)無(wú)機(jī)復(fù)混肥均極顯著促進(jìn)了鉀表觀利用率和經(jīng)濟(jì)利用率的提高,這可能是有機(jī)物料減少了土壤中鉀離子的淋失,提高了鉀的利用效率[18]。H2處理極顯著提高了烤煙磷的表觀利用率和經(jīng)濟(jì)利用率,但H1與CK之間差異不顯著,這可能是高比例有機(jī)物料的加入促進(jìn)了土壤磷的有效化[31],從而提高了磷的表觀和經(jīng)濟(jì)利用率;H2處理顯著或極顯著提高了烤煙氮的經(jīng)濟(jì)利用率和表觀利用率,可能是高比例的有機(jī)物料促進(jìn)了土壤氮素的有效性和降低了氮的淋溶。

      4? 結(jié)? 論

      在框栽試驗(yàn)條件下,有機(jī)無(wú)機(jī)復(fù)混肥極顯著提高了煙株鉀的表觀及經(jīng)濟(jì)利用率和莖、葉及全株鉀含量及積累量,尤其是2:1有機(jī)無(wú)機(jī)復(fù)混肥(H2),其顯著或極顯著增加了根、莖、葉及全株的干物質(zhì)和氮、磷、鉀的積累量,顯著或極顯著提高了煙株氮、磷的經(jīng)濟(jì)利用率及表觀利用率。有機(jī)無(wú)機(jī)復(fù)混肥還降低了煙株根、莖鉀和煙葉氮的分配率,提高了煙葉鉀和根、莖氮的分配率。由此可見(jiàn),有機(jī)無(wú)機(jī)復(fù)混肥有利于提高烤煙N、P、K養(yǎng)分的積累和利用率,但有機(jī)無(wú)機(jī)復(fù)混肥中養(yǎng)分配比對(duì)植煙土壤養(yǎng)分的有效性和烤后煙葉產(chǎn)質(zhì)量的影響需進(jìn)一步研究。

      參考文獻(xiàn)

      [1]PAUNGFOO-LONHIENNE C, VISSER J, LONHIENNE T. G. A, et al. Past, present and future of organic nutrients[J]. Plant and Soil, 2012, 359(1-2): 1-18.

      [2]周建斌. 作物營(yíng)養(yǎng)從有機(jī)肥到化肥的變化與反思[J]. 植物營(yíng)養(yǎng)與肥料學(xué)報(bào),2017,23(6):1686-1693.ZHOU J B. Reconsideration of the changes of plant nutrition from organic fertilizers to chemical fertilizers[J]. Journal of Plant Nutrition and Fertilizer, 2017, 23(6): 1686-1693.

      [3]STOCKDALE E A, LAMPKIN N H, HOVI M, et al. Agronomic and environmental implications of organic farming systems [J]. Advances in Agronomy, 2000(70): 261-327.

      [4]FANDICA I R, KADYAMPAKENI D, BOTTOMANI C, et al. Comparative response of varied irrigated maize to organic and inorganic fertilize application [J]. Physics and Chemistry of the Earth, 2007(32): 1107-1116.

      [5]IKA D, THOMAS L, RUTH B. K et al. Conventionalisation of organic farming practices: from structural criteria towards an assessment based on organic principles[J]. Agronomy for Sustainable Development, 2010, 30(1): 67-81.

      [6]杜偉. 有機(jī)無(wú)機(jī)復(fù)混肥優(yōu)化肥料養(yǎng)分利用的效應(yīng)與機(jī)理[D]. 北京:中國(guó)農(nóng)業(yè)科學(xué)院,2010.DU W. The optimizing effects and mechanisms of organic-inorganic compound fertilizer on inorganic fertilizer utilization[D]. Beijing: Chinese Academy of Agriculture Sciences, 2010.

      [7]韓曉玲,張乃文,賈敬芬. 生物有機(jī)無(wú)機(jī)復(fù)混肥對(duì)番茄產(chǎn)量、品質(zhì)及土壤的影響[J]. 土壤肥料,2005(3):51-53.HAN X L, ZHANG N W, JIA J F. Effects of biological organic-inorganic compound fertilizer on yield, quality of tomato and soil[J]. Soil and Fertilizers Sciences, 2005(3): 51-53.

      [8]翟廷廣,周權(quán)鎖,葛瀅,等. 蠶沙有機(jī)無(wú)機(jī)復(fù)混肥對(duì)葉菜類(lèi)蔬菜產(chǎn)量和品質(zhì)的影響[J]. 江蘇農(nóng)業(yè)學(xué)報(bào),2010,26(1):80-84.ZHAI T G, ZHOU Q S, GE Y, et al. Effects of organic-inorganic complex fertilizers from silk worm excrement on the yield and quality of leaf vegetable[J]. Jiangsu Agricultural Science, 2010, 26(1): 80-84.

      [9]張小莉,孟琳,王秋君,等. 不同有機(jī)無(wú)機(jī)復(fù)混肥對(duì)水稻產(chǎn)量和氮素利用率的影響[J]. 應(yīng)用生態(tài)學(xué)報(bào),2009,20(3):624-630.ZHANG X L, MENG L, WANG Q J, et al. Effects of organic-inorganic mixed fertilizers on rice yield and nitrogen use efficiency[J]. Chinese Journal of Applied Ecology, 2009, 20(3): 624-630.

      [10]田亨達(dá),張麗,張堅(jiān)超,等. 施用有機(jī)物機(jī)復(fù)混肥對(duì)太湖平原烏泥土稻麥生長(zhǎng)的影響[J]. 南京農(nóng)業(yè)大學(xué)學(xué)報(bào),2012,35(1):69-74.TIAN H D, ZHANG L, ZHANG J C, et al. Effect of organic-inorganic compound fertilizers on the growth of rice and wheat in South Jiangsu[J]. Journal of Nanjing Agricultural University, 2012, 35(1): 69-74.

      [11]田亨達(dá),張麗,張堅(jiān)超,等. 蘇南地區(qū)稻麥輪作系統(tǒng)對(duì)不同有機(jī)物機(jī)復(fù)混肥的響應(yīng)[J]. 應(yīng)用生態(tài)學(xué)報(bào),2011,22(11):2868-2874.TIAN H D, ZHANG L, ZHANG J C, et al. Responses of rice-wheat rotation system in south Jiangsu to organic-inorganic compound fertilizers[J]. Chinese Journal of Applied Ecology, 2011, 22(11): 2868-2874.

      [12]王秋君,張小莉,羅佳,等. 不同有機(jī)物機(jī)復(fù)混肥對(duì)小麥產(chǎn)量、氮效率和土壤微生物多樣性的影響[J]. 植物營(yíng)養(yǎng)與肥料學(xué)報(bào),2009,15(5):1003-1009.WANG Q J, ZHANG X L, LUO J, et al. Effects of different organic-inorganic mixed fertilizations on yield of wheat nitrogen use efficiency and soil microbial diversity[J]. Plant Nutrition and Fertilizer Science, 2009, 15(5):1003-1009.

      [13]郎曉峰,徐陽(yáng)春,沈其榮. 不同有機(jī)物機(jī)復(fù)混肥對(duì)土壤供氮和玉米生長(zhǎng)的影響[J]. 生態(tài)與農(nóng)村環(huán)境學(xué)報(bào),2008,24(3):33-38.LANG X F, XU Y C, SHEN Q R, et al. Effect of formation of organic-inorganic mixed fertilizers on soil N supply and growth of maize[J]. Journal of Ecology and Rural Environment, 2008, 24(3): 33-38.

      [14]蔣小芳,羅佳,黃啟為,等. 不同原料堆肥的有機(jī)物機(jī)復(fù)混肥對(duì)辣椒產(chǎn)量和土壤生物性狀的影響[J]. 植物營(yíng)養(yǎng)與肥料學(xué)報(bào),2008,14(4):766-773.JIANG X F, LUO J, HUANG Q W, et al. Effect of different organic-inorganic mixed fertilizer application on pepper yield and soil microbial properties[J]. Plant Nutrition and Fertilizer Science, 2008, 14(4): 766-773.

      [15]邵麗,谷潔,張社奇,等. 生物復(fù)混肥對(duì)土壤微生物功能多樣性及土壤酶活性的影響[J]. 農(nóng)業(yè)環(huán)境科學(xué)學(xué)報(bào),2012,31(6):1153-1159.SHAO L, GU J, ZHANG S Q, et al. Effects of bio-compound fertilizer on corn soil microbial community and enzyme activities[J]. Journal of Agro-environment Science, 2012, 31(6): 1153-1159.

      [16]彭智良,黃元炯,劉國(guó)順,等. 不同有機(jī)肥對(duì)煙田土壤微生物以及煙葉品質(zhì)和產(chǎn)量的影響[J]. 中國(guó)煙草學(xué)報(bào),2009,15(2):41-45.PENG Z L, HUANG Y J, LIU G S, et al. Effects of different organic fertilizer on soil microbe and hence quality and yield of tobacco leaves[J]. Acta Tabacaria Sinica, 2009, 15(2): 41-45.

      [17]劉洪華,趙銘欽,王付峰,等. 有機(jī)無(wú)機(jī)肥配施對(duì)烤煙揮發(fā)性香氣物質(zhì)的影響[J]. 中國(guó)煙草學(xué)報(bào),2010,16(5):65-71.LIU H H, ZHAO M Q, WANG F F, et al. Effects of combined of organic fertilizer and chemical fertilizer on volatile aroma components in flue-cured tobacco[J]. ActaTabacaria Sinica, 2010, 16(5): 65-71.

      [18]唐莉娜,張秋芳,陳順輝. 不同有機(jī)肥與化肥配施對(duì)植煙土壤微生物群落PLFAs和烤煙品質(zhì)的影響[J]. 中國(guó)煙草學(xué)報(bào),2010,16(1):36-40.TANG L N, ZHANG Q F, CHEN S H. Effects of applying organic manures combined with chemical fertilizers on diversity of PLFAs biomarkers of microbial community in tobacco-growing soil and its consequences on flue-cured tobacco leaf quality[J]. Acta Tabacaria Sinica, 2010, 16(1): 36-40.

      [19]楊云高,王樹(shù)林,劉國(guó),等. 生物有機(jī)肥對(duì)烤煙產(chǎn)質(zhì)量及土壤改良的影響[J]. 中國(guó)煙草科學(xué),2012,33(4):70-74.YANG Y G, WANG S L, LIU G, et al. Effects of bio-organic fertilizer on yield and quality of flue-cured tobacco and soil improvement[J]. Chinese Tobacco Science, 2012, 33(4): 70-74.

      [20]施河麗,譚軍,王興斌,等. 煙草秸稈生物有機(jī)肥對(duì)植煙土壤交換性鹽基的影響[J]. 中國(guó)煙草科學(xué),2015,36(4):80-84.SHI H L, TAN J, WANG X B, et al. Effects of tobacco straw bio-organic fertilizer on exchangeable base of tobacco soil[J]. Chinese Tobacco Science, 2015, 36(4): 80-84.

      [21]楊德廉,李祥英,馬夙靜,等. 有機(jī)肥施用對(duì)煙田土壤細(xì)菌多態(tài)性的影響[J]. 中國(guó)煙草科學(xué),2018,39(3):31-39.YANG D L, LI X Y, MA S J, et al. Effects of organic fertilizer application on soil bacterial polymorphism in tobacco fields[J]. Chinese Tobacco Science, 2018, 39(3): 31-39.

      [22]施河麗,孫立廣,譚軍,等. 生物有機(jī)肥對(duì)煙草青枯病的防效及對(duì)土壤細(xì)菌群落的影響[J]. 中國(guó)煙草科學(xué),2018,39(2):54-62.SHI H L, SUN L G, TAN J, et al. Control efficiency of bio-organic fertilizers on tobacco bacterial wilt and their effects on soil bacterial community[J]. Chinese Tobacco Science, 2018, 39(2): 54-62.

      [23]孫立廣,張洪春,趙秀云,等. 煙草青枯病拮抗菌在有機(jī)肥中的定殖效率及田間防治效果[J]. 中國(guó)煙草科學(xué),2016,37(4):48-53.SUN L G, ZHANG H C, ZHAO X Y, et al. Colonization rate of several antagonistic bacteria against tobacco bacterial wilt in organic fertilizers and control efficacy in field[J]. Chinese Tobacco Science, 2016, 37(4): 48-53.

      [24]方金豹. 植物中氮、磷、鉀的測(cè)定:NY/T2017—2011[S].北京:中國(guó)農(nóng)業(yè)出版社,2011:3-10.FANG J B. Determination of nitrogen, phosphorus and potassium in plants: NY/T2017—2011[S]. Beijing: China Agriculture Press, 2011: 3-10.

      [25]宋建群,徐智,湯利,等. 不同有機(jī)肥對(duì)烤煙養(yǎng)分吸收及化肥利用率的影響[J]. 云南農(nóng)業(yè)大學(xué)學(xué)報(bào),2015,30(3):471-476.SONG J Q, XU Z, TANG L, et al. Effects of different organic fertilizers on nutrient absorption and fertilizer use efficiency of flue-cured tobacco[J]. Journal of Yunnan Agricultural University, 2015, 30(3): 471-476.

      [26]劉泓. 有機(jī)肥與化肥配施對(duì)烤煙K吸收和干物質(zhì)積累的影響[J]. 福建農(nóng)業(yè)大學(xué)學(xué)報(bào),1998,27(3):257-260.LIU H. Effects of organic manures combined with chemical fertilizers on potassium uptake and dry mafter accumulation of flue-cured tobacco[J]. Journal of Fujian Agricultural University, 1998, 27(3): 257-260.

      [27]彭華偉,劉國(guó)順,吳學(xué)巧,等. 生物有機(jī)肥對(duì)烤煙氮磷鉀積累、吸收和含量的影響[J]. 中國(guó)煙草科學(xué),2008,29(1):25-29.PENG H W, LIU G S, WU X Q, et al. Effects of bio-organic fertilizer on accumulation, uptake and contents of N, P, K in flue-cured tobacco[J]. Chinese Tobacco Science, 2008, 29(1): 25-29.

      [28]唐莉娜,熊德中. 有機(jī)無(wú)機(jī)肥配施對(duì)烤煙氮磷鉀營(yíng)養(yǎng)分配及產(chǎn)量和質(zhì)量的影響[J]. 福建農(nóng)業(yè)學(xué)報(bào),1999,14(2):50-55.TANG L N, XIONG D Z. Effect of combining application of organic –chemical fertilizers on the NPK distribution and yield and the quality of tobacco leaves [J]. Fujian Journal of Agricultural Sciences, 1999, 14(2): 50-55.

      [29]孟蕾,曾慶武,張吉立,等. 定向發(fā)酵餅肥對(duì)烤煙各器 官氮含量及氮分配的影響研究[J]. 中國(guó)農(nóng)學(xué)通報(bào),2012,28(10):249-253.MENG L, ZENG Q W, ZHANG J L, et al. Studies on effects of nitrogen content and nitrogen allocation in flue-cured tobacco organs under fermented soybean cake [J]. Chinese Agricultural Science Bulletin, 2012, 28(10): 249-253.

      [30]王昌全,李廷強(qiáng),夏建國(guó),等. 有機(jī)物機(jī)復(fù)混肥對(duì)農(nóng)產(chǎn)品產(chǎn)質(zhì)量的影響[J]. 四川農(nóng)業(yè)大學(xué)學(xué)報(bào),2001,19(3):241-244.WAGN C Q, LI T Q, XIA J G, et al. Effect of organic-inorganic compound fertilizer on quality of agricultural products[J]. Journal of Sichuan Agricultural University, 2001, 19(3): 241-244.

      [31]樊紅柱,陳慶瑞,郭松,等. 長(zhǎng)期不同施肥紫色水稻土磷的盈虧及有效性[J]. 植物營(yíng)養(yǎng)與肥料學(xué)報(bào),2018,24(1):154-162.FANG H Z, CHEN Q R, GUO S, et al. Phosphorus balance availability in a purple paddy soil under long-term different fertilization[J]. Journal of plant nutrition and fertilizers, 2018, 24(1): 154-162.

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