农业资源与环境学报
農業資源與環境學報
농업자원여배경학보
Journal of Agricultural Resources and Environment
2014年
3期
273-278
,共6页
肖明%杨文君%孙小凤%吕新
肖明%楊文君%孫小鳳%呂新
초명%양문군%손소봉%려신
土壤%As%农药%肥料%灌溉
土壤%As%農藥%肥料%灌溉
토양%As%농약%비료%관개
soil%arsenic%pesticide%fertilizer%irrigation
选择柴达木盆地诺木洪农场3种类型农田进行20 cm表层土壤砷(As)含量检测。第1种为新开垦原生地,第2种为20年耕种地,第3种为50年耕种地,检测As含量分别为16.29、14.90、14.04 mg·kg-1。3种土壤As含量均达到无公害食品标准(25 mg· kg-1)和绿色食品标准(20 mg·kg-1)。多年耕种并没有造成农田表层土壤As积累。农田灌溉用河水中未检出As。生产中使用的22种农药、肥料均检测到As,其中15种杀虫剂、杀真菌剂、除草剂、植物激素等,每年输入土壤As 4513.59 mg·hm-2;7种肥料每年输入土壤As 258015.24 mg·hm-2。施肥是土壤中As输入的重要来源,最主要的输入源是磷酸二铵,占到50%;其次为复合肥、鸡粪和有机肥。每年随作物输出As总量为4380 mg·hm-2。模拟田间灌溉,进行土壤柱淋漓试验,农田20 cm表层土壤每年随灌溉淋漓输出As为245230.65 mg·hm-2,这与随着肥料、农药输入量几乎相等。表层土壤As处在一个输入、输出相对稳定的动态平衡状态。从土壤中输出的As,随灌溉水输入到水系统中,继而造成水系统As的积累,最终将影响到地区农业的可持续发展。
選擇柴達木盆地諾木洪農場3種類型農田進行20 cm錶層土壤砷(As)含量檢測。第1種為新開墾原生地,第2種為20年耕種地,第3種為50年耕種地,檢測As含量分彆為16.29、14.90、14.04 mg·kg-1。3種土壤As含量均達到無公害食品標準(25 mg· kg-1)和綠色食品標準(20 mg·kg-1)。多年耕種併沒有造成農田錶層土壤As積纍。農田灌溉用河水中未檢齣As。生產中使用的22種農藥、肥料均檢測到As,其中15種殺蟲劑、殺真菌劑、除草劑、植物激素等,每年輸入土壤As 4513.59 mg·hm-2;7種肥料每年輸入土壤As 258015.24 mg·hm-2。施肥是土壤中As輸入的重要來源,最主要的輸入源是燐痠二銨,佔到50%;其次為複閤肥、鷄糞和有機肥。每年隨作物輸齣As總量為4380 mg·hm-2。模擬田間灌溉,進行土壤柱淋巑試驗,農田20 cm錶層土壤每年隨灌溉淋巑輸齣As為245230.65 mg·hm-2,這與隨著肥料、農藥輸入量幾乎相等。錶層土壤As處在一箇輸入、輸齣相對穩定的動態平衡狀態。從土壤中輸齣的As,隨灌溉水輸入到水繫統中,繼而造成水繫統As的積纍,最終將影響到地區農業的可持續髮展。
선택시체목분지낙목홍농장3충류형농전진행20 cm표층토양신(As)함량검측。제1충위신개은원생지,제2충위20년경충지,제3충위50년경충지,검측As함량분별위16.29、14.90、14.04 mg·kg-1。3충토양As함량균체도무공해식품표준(25 mg· kg-1)화록색식품표준(20 mg·kg-1)。다년경충병몰유조성농전표층토양As적루。농전관개용하수중미검출As。생산중사용적22충농약、비료균검측도As,기중15충살충제、살진균제、제초제、식물격소등,매년수입토양As 4513.59 mg·hm-2;7충비료매년수입토양As 258015.24 mg·hm-2。시비시토양중As수입적중요래원,최주요적수입원시린산이안,점도50%;기차위복합비、계분화유궤비。매년수작물수출As총량위4380 mg·hm-2。모의전간관개,진행토양주림리시험,농전20 cm표층토양매년수관개림리수출As위245230.65 mg·hm-2,저여수착비료、농약수입량궤호상등。표층토양As처재일개수입、수출상대은정적동태평형상태。종토양중수출적As,수관개수수입도수계통중,계이조성수계통As적적루,최종장영향도지구농업적가지속발전。
The topsoil arsenic of three wolfberry farmland in the Nuomuhong Farm located in the Qaidam Basin, western China,was detected in this study. The first farmland was an original land, which had never been farmed, the second one was a farmland which had been farmed for 20 years and the third one was a farmland which had been farmed for 50 years. The arsenic contents of those three farmlands were 16.29, 14.90 mg·kg-1 and 14.04 mg·kg-1, respectively. All of them were up to meet the Pollution-Free Food(25 mg·kg-2)and the Green Food(20 mg·kg-1) standards. Farming for many years did not cause the accumulation of farmland topsoil arsenic. Irrigation water was found to be free of arsenic. Fifteen kinds of pesticides, fungicides, herbicides and plant hormones contributed 4 513.59 mg·hm-2 of arsenic to the soil per year. Seven kinds of fertilizer contributed 258 015.24 mg·hm-2 of arsenic to the soil per year. Fertilization was thus a major source of arsenic pollution in the soil, the most serious source of pollution was DAP(50%), followed by compound fertilizer, chicken manure and organic fertilizer. Total 4 380 mg·hm-2 arsenic was output with crops per year. In the experiments of field irrigation simulation and dripping wet the soil, there were 245 230.65 mg·hm-2 arsenic output from 20 cm topsoil by irrigation dripping per year, but the same amount of arsenic were input topsoil with fertilizers and pesticides per year. Farmland topsoil arsenic was an input-output homeostasis state. The arsenic that output from the soil en-tered and accumulated in water system with irrigation water, ultimately affected the sustainable development of agriculture in the region.