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1.
施用污泥对土壤重金属形态分布和生物有效性的影响   总被引:11,自引:0,他引:11  
采用盆栽技术和BCR连续浸提法研究了污泥的添加对土壤Cd、Pb、Cu和Zn形态分布的影响及重金属在黑麦草-施污泥土壤中迁移转化规律.结果表明:污泥的添加使土壤中生物有效态的Cd和Zn含量显著增加,生物有效态Pb含量显著降低,残渣态Pb的比例较CK增加了33.3%~74.5%,而可交换态和可还原态Cu含量在污泥与土壤添加比为1∶1时,仅占总量的0.7%和0.2%.污泥的添加能促进黑麦草对Cd、Cu和Zn的吸收,抑制对Pb的吸收.多元线性回归分析结果表明,黑麦草体内Cd、Zn和Cu含量分别与土壤中可还原态Cd、Zn和可氧化态Cu含量存在正相关,草体中Pb的含量则受土壤中可交换态和可氧化态Pb含量共同影响.种植黑麦草后根际土中可氧化态Cd和Cu分别向可交换态Cd和残渣态Cu转化,可交换态和可还原态Zn向可氧化态Zn转化,Pb的生物有效性基本未受影响.  相似文献   

2.
根瘤菌对土壤铜、锌和镉形态分配的影响   总被引:13,自引:0,他引:13  
以湖南郴州红壤和河北巩义褐土为供试土壤。制备Cu、Zn、Cd污染土壤。接种大豆根瘤菌(Rhi-zobium fredii)HN01,用连续提取法浸提土壤中不同形态的重金属.结果表明。褐土接种根瘤菌后固相结合态Zn总量降低10%。专性吸附态、氧化锰结合态和有机结合态Zn减少达9%~26%.红壤中结合态Zn的总量变化不显著,但专性吸附态和氧化锰结合态Zn含量显著减少。交换态Zn含量显著增加.褐土中接种根瘤菌抑制了Cu向土壤溶液的释放,固相结合态Cu总量增加18%,可交换态、专性吸附态、氧化锰结合态和有机结合态的Cu增加20%~54%.接种根瘤菌对土壤中Cd的溶解没有明显的抑制或促进作用,但改变了红壤中各形态Cd的含量高低顺序.Cd污染红壤中可交换态和有机结合态Cd含量分别增加22%和11%,专性吸附态和氧化锰结合态Cd分别减少14%和29%.根瘤菌对不同类型重金属及不同土壤中重金属形态影响的差异主要与土壤pH降低有关.  相似文献   

3.
模拟酸雨对污染土壤中Cd、Cu和Zn释放及其形态转化的影响   总被引:36,自引:0,他引:36  
研究了模拟酸雨连续浸泡下污染红壤和黄红壤中重金属释放及形态转化.结果表明。随着模拟酸雨pH值下降,污染土壤中重金属释放强度明显增大;Cd、Zn释放量与酸雨pH值呈线性极显著负相关.Cu与酸雨pH值呈线性显著负相关.模拟酸雨作用下,污染红壤和黄红壤中Cd均以交换态为主;Cu则以有机结合态和氧化锰结合态为主;Zn在污染红壤中以残留态和交换态为主.在污染黄红壤中以残留态和有机结合态为主.土壤有机质含量和阳离子交换量对Cd、Cu、Zn的释放产生一定的影响并影响Cd、Zn的形态转化,但对Cu形态转化影响不明显,随着模拟酸雨酸度增大,污染红壤和黄红壤中重金属Cd、Cu的生物可利用态明显增多,但难解吸态Zn向生物有效态转化效应不明显.  相似文献   

4.
鄂尔多斯地区公路沿线土壤重金属形态与生物有效性   总被引:12,自引:2,他引:12  
采用TessierA连续提取法对鄂尔多斯地区公路沿线土壤重金属(Pb、Zn、Cu、Ni、Cr)化学形态进行了测定。同时对土壤pH值、重金属含量和公路绿化植物重金属(Cd、Hg、Pb、Cu、Zn、Ni、Cr、As和Se)含量进行了分析,对该区域重金属的生物有效性与潜在生态风险进行预测。结果表明:土壤重金属有效态占总量百分比的大小序列为Zn〉Pb〉Ni、Cr〉Cu,与重金属元素在绿化植物中含量大小序列Zn〉Cu〉Ni、Cr、As、Pb〉Cd〉Hg并非完全趋于一致。不同公路段土壤重金属与其不同形态存在较大的变幅。公路沿线表层土壤中重金属的有效态占其总量为G109(东胜-准格尔段)15.7%~46.1%,G210(达拉特-东胜段)8.0%-40.9%,G109(东胜-鄂托克段)9.1%~33.9%,而且以有机态和Fe—Mn氧化结合态的比例较大,为各元素有效态的主要形态特征。Cu在不同植物不同器官中的含量较高,可能在鄂尔多斯地区特定环境条件下随植物的蒸腾拉力、水分和营养盐运移的生理生态作用下使其在植物体中富集。土壤重金属Zn的有效态含量较高,而残渣态含量低,须特别注意其对区域生态系统的潜在影响。  相似文献   

5.
强还原过程对设施菜地土壤重金属形态转化的影响   总被引:1,自引:0,他引:1  
设施菜地由于污水灌溉、粪肥施用等导致重金属污染.本文通过土柱淹水同时添加玉米秸秆培养和后期通水淋洗,研究强还原法对设施土壤重金属(Cd、Cu、Pb和Zn)形态转化的影响.结果表明: 强还原处理使土壤pH显著降低,玉米秸秆处理变化更显著;土壤氧化还原电位(Eh)迅速下降至-280 mV左右.玉米秸秆处理可以促进土壤中Cd、Cu、Pb和Zn活化,第9天土壤中有机物及硫化物结合态和残渣态Cd、Cu、Pb和Zn含量比重下降;至15 d培养结束,土壤中4种重金属含量较对照分别减少18.1%、19.0%、16.1%和15.7%.玉米秸秆处理可以增加土壤中Cd和Zn的溶出量,但是Cu的溶出量减少;胶体结合态Cd和Pb含量较对照增加、Cu较对照显著减少、Zn没有显著变化.强还原可以引起设施土壤重金属活化,提高蔬菜积累重金属的风险,而且其随土壤水分的运移可能导致水体的污染.  相似文献   

6.
Yi WP  Sun Z  Wu L  Shi GF  Zhu GL  Li YX  Gu JL  Xu QM 《应用生态学报》2011,22(3):687-693
应用大田试验研究了不同用量的包膜控释尿素(PCU60,释放期为60 d)与普通尿素(U)配合基施(10%PCU60+90%U,PU1;20%PCU60+80%U,PU2;30%PCU60+70%U,PU3;40%PCU60+60%U,PU4)对冬小麦产量、氮肥利用率等生物学性状及土壤硝态氮累积的影响,并对PCU60氮素田间溶出特征及25℃静水溶出特征进行了比较分析.结果表明:在施氮量相等的条件下,与习惯施肥处理相比,PU4处理冬小麦各项指标均显著提高:增产5.6%、氮肥利用率提高14.6%、氮素总累积量提高7.2%、成熟期总茎数提高2.6%、成熟期地上部总生物量提高7.5%、经济效益增加984.3元·hm-2.各处理0~100 cm土层硝态氮总累积量在39.70~49.93 kg·hm-2,其中,PU4处理总累积量最低,为39.70 kg·hm-2.埋袋试验表明,释放期为60 d的包膜控释尿素氮素释放规律与小麦氮素吸收特性基本吻合.  相似文献   

7.
碳酸钙对水稻吸收重金属(Pb、Cd、Zn)和As的影响   总被引:11,自引:0,他引:11  
选用重金属(Pb、Cd、Zn)和As复合污染土壤进行水稻盆栽试验,结果表明,碳酸钙的添加显著提高了土壤pH值,显著降低了土壤中交换态Pb、Cd、Zn和As的含量,与对照相比,交换态Pb、Cd、Zn和As含量分别最多降低了98.35%,93.72%,98.52%和69.48%。碳酸钙对水稻根、稻谷干重和总生物量没有显著影响,添加量过高时显著降低了水稻分蘖数和茎叶干重,说明过量施用碳酸钙对水稻生长会产生负面作用。因为碳酸钙的添加,水稻植株各部位重金属Zn含量显著降低,糙米中Zn含量最多减少了34.95%;根、谷壳中Pb、Cd含量显著降低,但糙米中含量却未显著降低;水稻各部位As含量均没有显著降低。参照《食品中污染物限量》(GB2762—2012),试验糙米中Pb、Cd、无机As含量均未达到限量标准。显然,碳酸钙的添加降低了Pb、Cd、Zn的生物有效性(水稻根系对Pb、Cd、Zn的吸收累积减少),但并未有效地抑制Pb、Cd向糙米转运;碳酸钙显著降低了土壤的交换态As含量,但并未使土壤中As的生物有效性明显降低(水稻植株各部位的As含量并未显著减少)。  相似文献   

8.
对内蒙古西部公路绿化植物油松(Pinus tabulaeformis)、小叶杨(Populus simonii)及其根际土壤中重金属元素(Cd、Hg、Pb、Cu、Zn、Ni、Cr)和类金属元素(As和Se)含量以及根际土壤重金属(Cu、Zn、Pb、Ni和Cr)形态、土壤pH值进行了测定。对比分析了公路沿线不同绿化植物及其不同器官对重金属元素的吸收与积累特征。结果表明:绿化植物根际土壤对重金属元素的吸附及污染程度以Cd为最高。随原子序数的递增,小叶杨和油松两种植物的根部和茎叶两种营养器官中重金属的含量均表现出“N”字形变动趋势。而且重金属元素在不同植物不同器官中的含量具有Zn〉Cu〉Ni,Cr,As,Pb〉Cd〉Hg的基本规律。小叶杨茎叶对重金属元素Cr、Ni和Pb的富集能力较根部为强,油松茎叶对重金属元素Cr、Ni、Cu和Pb的富集能力较根部为强。绿化植物根际土壤重金属元素有效态占总量百分比的大小序列为Zn〉Pb〉Ni、Cr〉Cu,与重金属元素在不同植物不同器官中的含量大小序列Zn〉Cu〉Ni、Cr、As、Pb〉Cd〉Hg并非趋于一致。公路绿化植物对根际土壤中重金属元素的吸收和积累与重金属元素有效态所占的比例有关。  相似文献   

9.
重金属污染区土壤酶活性变化   总被引:5,自引:1,他引:4  
王涵  高树芳  陈炎辉  王果 《应用生态学报》2009,20(12):3034-3042
从福建龙岩新罗区特钢厂污灌区农田采集土壤,测定土壤基本理化性质及脲酶、纤维素酶、碱性磷酸酶、多酚氧化酶、过氧化氢酶活性和Cu、Cd、Pb、Zn含量,探讨重金属污染和土壤性质对土壤酶活性的影响.结果表明: 4种全量或有效态重金属与土壤脲酶、纤维素酶、碱性磷酸酶和多酚氧化酶活性呈显著正相关,与过氧化氢酶活性呈显著或极显著负相关;土壤pH与碱性磷酸酶活性呈极显著正相关,粉粒含量与过氧化氢酶活性呈显著负相关.经通径分析,重金属污染刺激了脲酶、多酚氧化酶和纤维素酶活性,但对碱性磷酸酶活性的影响较小.有效态Cu、Cd、Pb、Zn对过氧化氢酶活性的直接影响并不大,但通过间接途径抑制了过氧化氢酶活性.土壤理化性质对5种土壤酶活性的影响较大,碱解氮直接抑制了脲酶活性;全磷直接刺激了碱性磷酸酶和过氧化氢酶活性,并通过有效磷刺激了纤维素酶活性;有效磷直接刺激了纤维素酶活性,直接抑制了碱性磷酸酶和过氧化氢酶活性;全钾直接抑制了碱性磷酸酶和多酚氧化酶活性;速效钾通过有效磷刺激了纤维素酶活性;土壤颗粒组成明显影响多酚氧化酶和过氧化氢酶活性.5种酶活性与土壤Cu、Cd、Pb、Zn含量之间的关系不明确,因此其活性不是指示土壤Cu、Cd、Pb、Zn污染的良好指标.  相似文献   

10.
稻麦轮作下水稻土重金属形态特征及其生物有效性   总被引:26,自引:0,他引:26  
在成都平原稻麦轮作下86个土样中重金属全量和各形态含量分析的基础上,采集分析相应点位上种植的主要粮食作物小麦和水稻籽粒的重金属含量,通过描述性统计分析、相关性分析及线性回归方程的模拟,研究了土壤中重金属的形态分布特征及其生物有效性。统计分析结果表明:土壤中Cr、Cu、Pb、Zn各形态含量的分配顺序为:残渣态〉有机物结合态〉铁锰氧化物结合态〉碳酸盐结合态〉可交换态,而Cd各形态含量的分配顺序为:铁锰氧化物结合态〉残渣态〉碳酸盐结合态〉有机物结合态〉可交换态。若以活性态(非残渣态含量)而论,Cd的活性最高,Cr的活性最低。除Cr外,各元素全量与各活性形态之间的关系较为密切。土壤中全Cd含量与4种活性形态Cd含量间的相关性均达极显著水平;Cu、Zn全量分别与其铁锰氧化物和有机物结合态含量,Pb全量分别与其可交换态和铁锰氧化物含量间的相关系数达显著或极显著水平。用卫生部颁布的食品中重金属限量卫生标准评价稻麦籽粒重金属累积情况,其结果表明,小麦籽粒(旱作)中的Cd、Cr、Cu、Pb分别超标14.71%、8.70%、6.50%和17.40%,而水稻籽粒(水作)仅有Pb和Cd含量超标10.90%和8.70%。不同形态重金属对水稻和小麦籽粒中重金属累积的影响效应不同,从多元线性回归方程的回归系数来看:稻一麦籽粒中Cd含量受到土壤中各活性形态Cd含量的影响。除铁锰氧化态Cd和有机物结合态Cd含量分别对小麦和水稻籽粒中Cd的累积表现出负效应外,其余均为正效应。可交换态Cu含量对稻-麦籽粒Cu累积的效应最大,其次受碳酸盐结合态Cu含量的影响。稻一麦籽粒Pb含量的累积受土壤各活性态Pb含量影响效应的差异不甚明显。稻-麦籽粒Zn含量与土壤各活性态Zn含量间无显著线性关系。  相似文献   

11.
通过2017—2018两年田间试验,研究了不同土层深度配施缓释(PCU)/普通尿素(PU)对0~30 cm土层土壤无机氮含量、酶活性和玉米产量的影响。试验设置不施氮肥(CK)、普通尿素一次施肥(PU1,5~10 cm土层)、普通尿素传统两次施肥(PU2,5~10 cm土层,60%种肥+40%追肥)、普通尿素一次分层施肥(PU3,5~10 cm土层20%N+15~20 cm土层30%N+25~30 cm土层50%N)、不同土层深度缓释/普通尿素配施[PCU1~PCU4,均为5~10 cm土层20%N(普通尿素)+15~20 cm土层30%N(配施)+25~30 cm土层50%N(配施),其中PCU1~PCU4的15~20和25~30 cm土层PCU:PU分别为3:7、3:7,5:5、5:5, 3:7、5:5, 5:5、3:7]共8个处理。结果表明: 与CK相比,PU1能够满足玉米生育前期对0~10 cm土层氮素的需求,PU2和PU3能够满足玉米发育前期对10~30 cm土层氮素的需求,不同土层深度配施缓释/普通尿素能够满足玉米整个生育时期对氮素的需求。与PU1~PU3相比,不同土层深度配施缓释/普通尿素可显著增加灌浆期和成熟期10~20和20~30 cm土层NO3--N、NH4+-N、碱解氮含量和脲酶、蛋白酶活性。与PU3相比,不同土层深度配施缓释/普通尿素处理2017和2018年玉米产量分别提高2.3%~24.6%和1.3%~16.5%,PCU4产量最高,分别达13899和12439 kg·hm-2。因此,不同土层深度配施缓释/普通尿素既能满足玉米生育前期对氮素的需求,也能提高生育后期10~30 cm土层土壤无机氮含量和酶活性,促进玉米生长,增加玉米产量,其中PCU4处理施肥方式最佳。  相似文献   

12.
Cadmium (Cd) and zinc (Zn) phytoavailability and their phytoextraction by Sedum plumbizincicola using different nitrogen fertilizers, nitrification inhibitor (dicyandiamide, DCD) and urease inhibitor (N-(n-Butyl) thiophosphoric triamide, NBPT) were investigated in pot experiments where the soil was contaminated with 0.99 mg kg?1 of Cd and 241 mg kg?1 Zn. The soil solution pH varied between 7.30 and 8.25 during plant growth which was little affected by the type of N fertilizer. The (NH4)2SO4+DCD treatment produced higher NH4+?N concentrations in soil solution than the (NH4)2SO4 and NaNO3 treatment which indicated that DCD addition inhibited the nitrification process. Shoot Cd and Zn concentrations across all treatments showed ranges of 52.9–88.3 and 2691–4276 mg kg?1, respectively. The (NH4)2SO4+DCD treatment produced slightly higher but not significant Cd and Zn concentrations in the xylem sap than the NaNO3 treatment. Plant shoots grown with NaNO3 had higher Cd concentrations than (NH4)2SO4+DCD treatment at 24.0 and 15.4 mg kg?1, respectively. N fertilizer application had no significant effect on shoot dry biomass. Total Cd uptake in the urea+DCD treatment was higher than in the control, urea+NBPT, urea+NBPT+DCD, or urea treatments, by about 17.5, 23.3, 10.7, and 25.1%, respectively.  相似文献   

13.
Summary Field experiments were conducted to assess the efficiency of different forms and methods of urea application for direct sown rice under intermediate deep water situation (15–50 cm). Basal application of N @ 40 kg/ha in the form of prilled urea (PU); urea super granules (USG); and sulphur coated urea (SCU); were tested with a view to improving the early vigour, tillering and grain yield. Deep placement of prilled urea behind a plough; USG placement between rows in moist soil; and also in shallow water were found to increase the recovery of nitrogen. There was no deleterious effect on stand establishment when the seed and fertilizer @ 40, 8.6 and 16.6 kg N, P and K per hectare respectively were drilled in the same furrow in moist soil. Split application of either conditioned urea or application as a foliar spray did not prove effective in an intermediate deep water rice situation.  相似文献   

14.
In this study, the content characteristics, comprehensive pollution assessment, and morphological distribution characteristics of heavy metals (Mn, Cd, Cr, Pb, Ni, Zn, and Cu) were researched based on the processes of field investigation, sample collection, and experimental analysis. Results showed that the mean concentrations of Mn, Pb, Cr, Cu, Cd, Zn, and Ni in surface soils were 522.77, 22.56, 55.10, 25.41, 0.25, 57.02, and 48.47 mg kg?1, respectively. The surface soil from Sunan mining area was contaminated by Cu, Cd, and Ni in different degrees, and high CV values of Cd, Zn, Pb, and Ni were influenced by local human activities possibly. The evaluation results suggested that the mean Igeo values were in the sequence of Cd (0.657) > Ni (0.052) > Cu (?0.293) > Mn (?0.626) > Zn (?0.761) > Cr (?0.884) > Pb (?0.899). Besides, Cd was the most significant potential risk factor among all elements. Nevertheless, the Cd of bioavailable speciations with higher proportion had stronger migration and toxicity, and was more easier to be absorbed and enriched than other elements by some crops (e.g., vegetables, rice), and being at a relatively higher potential ecological risk in soil.  相似文献   

15.
To identify sources of heavy metal(loid) (HM) contamination in agricultural soils of Huzhou, surface soil samples were sampled from 89 different agricultural regions in 2012. Concentrations of heavy metal(loid)s, along with pH, total phosphorus (TP), total nitrogen (TN), and soil organic matter (SOM), were determined. Ecological risk was then assessed using a modified Hakanson ecological risk index, and the sources of contamination were determined using principal component analysis (PCA). Mean concentrations of heavy metal(loid)s were 10.26, 23.21, 83.75, 22.81, 0.25, 61.86, 33.03, and 0.15 mg kg?1 for As, Cu, Zn, Ni, Cd, Cr, Pb, and Hg, respectively. Cu, Zn, Ni, Cr, Cd, Hg, and Pb were correlated positively with TP and there were obvious positive correlations among Cu, Zn, Ni, Cr, and Cd. Risk index (RI) values varied from 39 to 1246 with a mean value of 137. Enrichment of Pb, Zn, Cu, and especially Cd can be attributed to excessive use of nitrogen and phosphorus fertilizers containing heavy metals, as well to surface irrigation and natural soil formation. While the ecological risk of most agricultural soils in Huzhou is low, it is recommended that the use of phosphate and nitrogen fertilizers be restricted and production technology be improved to reduce the heavy metal(loid) concentrations. Results suggest that the Chinese environmental quality standard for soil should be revised to better address heavy metal(loid) contamination.  相似文献   

16.
以持续9年施用不同缓/控释尿素的水田棕壤为试验对象,以普通大颗粒尿素为对照,研究了持续施用不同缓/控释尿素条件下水田土壤NH3挥发与N2O排放特征.结果表明: 与普通大颗粒尿素(U)相比,除1% 3,4-二甲基吡唑磷酸盐(DMPP)+U处理 NH3挥发增加了25.8%外,其他缓/控释尿素肥料处理对NH3有明显的减排效果.树脂包膜尿素(PCU)对NH3减排效果最明显,为73.4%,硫包膜尿素(SCU)为72.2%,0.5% N-丁基硫代磷酰三胺(NBPT)+1% DMPP+U为71.9%,1% 氢醌(HQ)+3% 双氰胺(DCD)+U为46.9%,0.5% NBPT+U为43.2%,1% HQ+U为40.2%,3% DCD+U为25.5%, 1% DMPP均与施用普通大颗粒尿素差异显著;所有缓/控释尿素处理与对照相比均可显著减少N2O排放.1% DMPP+U对N2O减排效果最明显,为74.9%,PCU为62.1%,1% HQ+3% DCD+U为54.7%,0.5% NBPT+1% DMPP+U为42.2%,3% DCD+U为35.9%,1% HQ+U为28.9%,0.5% NBPT+U为17.7%,SCU为14.5%,均与施用普通大颗粒尿素差异显著.比较0.5% NBPT+1% DMPP+U、SCU、PCU对NH3和N2O减排的综合效果,3种肥料作用相近,且均明显优于其他处理,但包膜材料的成本较抑制剂高数倍.因此,同时添加脲酶和硝化抑制剂的缓释尿素是减少水田氮素损失及环境污染的首选氮肥.  相似文献   

17.
Arbuscular mycorrhizal fungi (AMF) can promote plant growth and reduce plant uptake of heavy metals. Phosphorus (P) fertilization can affect this relationship. We investigated maize (Zea mays L.) uptake of heavy metals after soil AMF inoculation and P fertilization. Maize biomass, glomaline and chlorophyll contents and uptake of Fe, Mn, Zn, Cu, Cd and Pb have been determined in a soil inoculated with AMF (Glomus aggregatum, or Glomus intraradices) and treated with 30 or 60 µg P-K2HPO4 g?1 soil. Consistent variations were found between the two mycorrhizal species with respect to the colonization and glomalin content. Shoot dry weight and chlorophyll content were higher with G. intraradices than with G. aggregatum inoculation. The biomass was highest with 30 µg P g?1 soil. Shoot concentrations of Cd, Pb and Zn decreased with G. aggregatum inoculation, but that of Cd and Pb increased with G. intraradices inoculation. Addition of P fertilizers decreased Cd and Zn concentrations in the shoot. AMF with P fertilization greatly reduced maize content of heavy metals. The results provide that native AMF with a moderate application rate of P fertilizers can be exploited in polluted soils to minimize the heavy metals uptake and to increase maize growth.  相似文献   

18.
In the present work the extent and variation of Zn, Cd, Pb, Cu, and Hg loading in undisturbed surface soil (0–5 cm) and the vertical transport of the metals in soil profiles are studied in the vicinity of a zinc smelter in Norway. Three major controlling factors on the metal concentrations in soil have been assessed: 1) distance from the anthropogenic point source; 2) organic matter content (O.M.); and 3) the prevailing wind directions. Moreover metal distributions in proximal soil profiles in 1972 and 2003 are compared. Current concentrations of Zn, Cd, Pb, Cu, and Hg in surface soil reach 14000, 60, 980, 430, and 7.0 mg·kg ? 1 , respectively, near the smelter and decrease regularly with distance in the northerly direction according to the regression model (y = ax? b ). The Zn concentrations are significantly different from the background range up to 30 km from the smelter, whereas the other metals approach background at only 10 km distance. Subsurface concentration peaks of Pb, Cu, and Hg are found at greater depth in soil profiles than peaks of Zn and Cd. Levels of Zn, Cd, and Pb in surface soil seem to have decreased from 1972 to 2003, whereas for Cu the levels appear not to be significantly different.  相似文献   

19.
Dissolved organic matter in poultry litter could contribute organic ligands to form complexes with heavy metals in soil. The soluble complexes with heavy metals can be transported downward and possibly deteriorate groundwater quality. To better understand metal mobilization by soluble organic ligands in poultry litter, soil columns were employed to investigate the movement of zinc (Zn), cadmium (Cd), and lead (Pb). Uncontaminated soil was amended with Zn, Cd, and Pb at rates of 400, 8, and 200 mg kg ? 1 soil, respectively. Glass tubes, 4.9-cm-diameter and 40-cm-long, were packed with either natural or metal-amended soil. The resulting 20-cm-long column of soils had bulk density of about 1.58 g cm ? 3 . Columns repacked with natural or amended soil were leached with distilled water, 0.01 M EDTA, 0.01 M CaCl 2 , or poultry litter extract (PLE) solutions. Low amounts of Zn, Cd, and Pb were leached from natural soil with the solutions. Leaching of Zn, Cd, or Pb was negligible with distilled water. In the metal-amended soil, EDTA solubilized more Zn, Cd, and Pb than CaCl 2 and PLE. The breakthrough curves of Zn and Pb in the PLE and CaCl 2 were similar, indicating they have similar ability to displace Zn and Pb from soils. Compared with Zn and Cd the PLE had a small ability to solubilize Pb from metal-amended soil. Thus, the application of poultry litter on metal-contaminated soils might enhance the mobility of Zn and Cd.  相似文献   

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