<?xml version="1.0" encoding="UTF-8"?>
<!DOCTYPE ArticleSet PUBLIC "-//NLM//DTD PubMed 2.7//EN" "https://dtd.nlm.nih.gov/ncbi/pubmed/in/PubMed.dtd">
<ArticleSet>
<Article>
<Journal>
				<PublisherName>Shahid Beheshti University</PublisherName>
				<JournalTitle>Advanced Environmental Sciences</JournalTitle>
				<Issn>3115-7173</Issn>
				<Volume>7</Volume>
				<Issue>2</Issue>
				<PubDate PubStatus="epublish">
					<Year>2009</Year>
					<Month>12</Month>
					<Day>22</Day>
				</PubDate>
			</Journal>
<ArticleTitle>Evaluation of Potential Nitrate and Ammonium Accumulation in the Soil Profile under Irrigation and Manure Treatments with the LEACHM Model</ArticleTitle>
<VernacularTitle>Evaluation of Potential Nitrate and Ammonium Accumulation in the Soil Profile under Irrigation and Manure Treatments with the LEACHM Model</VernacularTitle>
			<FirstPage></FirstPage>
			<LastPage></LastPage>
			<ELocationID EIdType="pii">95719</ELocationID>
			
			
			<Language>FA</Language>
<AuthorList>
<Author>
					<FirstName>Omid</FirstName>
					<LastName>Bahmani</LastName>
<Affiliation>epartment of Irrigation, Faculty of Agricultural, University of Bu Ali Sina, Hamedan.</Affiliation>

</Author>
<Author>
					<FirstName>Saeed</FirstName>
					<LastName>Broomand Nasab</LastName>
<Affiliation>epartment of Irrigation, Faculty of Water Sciences Engineering, University of Shahid Chamran, Ahvaz.</Affiliation>

</Author>
<Author>
					<FirstName>Majid</FirstName>
					<LastName>Behzad</LastName>
<Affiliation>epartment of Irrigation, Faculty of Water Sciences Engineering, University of Shahid Chamran, Ahvaz.</Affiliation>

</Author>
<Author>
					<FirstName>Abd Ali</FirstName>
					<LastName>Naseri</LastName>
<Affiliation>Department of Irrigation, Faculty of Water Sciences Engineering, University of Shahid Chamran, Ahvaz.</Affiliation>

</Author>
</AuthorList>
				<PublicationType>Journal Article</PublicationType>
			<History>
				<PubDate PubStatus="received">
					<Year>2015</Year>
					<Month>05</Month>
					<Day>17</Day>
				</PubDate>
			</History>
		<Abstract>&lt;span style=&quot;left: 113.472px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.00928);&quot; dir=&quot;ltr&quot;&gt;Nitrate (NO&lt;/span&gt;&lt;span style=&quot;left: 159.552px; top: 560.328px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 163.008px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01788);&quot; dir=&quot;ltr&quot;&gt;-N) and ammonium (NH&lt;/span&gt;&lt;span style=&quot;left: 258.912px; top: 560.328px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 262.08px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02843);&quot; dir=&quot;ltr&quot;&gt;-N) leaching from &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 565.8px; font-size: 9.504px; font-family: serif; transform: scaleX(1.124);&quot; dir=&quot;ltr&quot;&gt;agricultural soils can represent substantial losses of &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 575.304px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05897);&quot; dir=&quot;ltr&quot;&gt;nitrogen (N) fertilizer, but a large variation in N losses &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 584.808px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05666);&quot; dir=&quot;ltr&quot;&gt;has been reported. The objectives of this study were to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 594.024px; font-size: 9.504px; font-family: serif; transform: scaleX(1.08275);&quot; dir=&quot;ltr&quot;&gt;assess the accumulation and movement of nitrate and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 603.528px; font-size: 9.504px; font-family: serif; transform: scaleX(1.13076);&quot; dir=&quot;ltr&quot;&gt;ammonium in the soil profile over the study period &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 612.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02628);&quot; dir=&quot;ltr&quot;&gt;under different irrigation and fertilizer conditions. So, N &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 622.248px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0449);&quot; dir=&quot;ltr&quot;&gt;concentration and its leaching were studied under three &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 631.464px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0542);&quot; dir=&quot;ltr&quot;&gt;N fertilizer and three irrigation treatments during 2007 &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 640.968px; font-size: 9.504px; font-family: serif; transform: scaleX(1.11974);&quot; dir=&quot;ltr&quot;&gt;Khuzestan Province, Iran. The irrigation treatments &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 650.472px; font-size: 9.504px; font-family: serif; transform: scaleX(1.06916);&quot; dir=&quot;ltr&quot;&gt;consisted of full irrigation (I1) and 85 (I2) and 70 (I3) &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 659.688px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01656);&quot; dir=&quot;ltr&quot;&gt;percent of I1. Also, the N treatments were 150 (N1), 250 &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 669.192px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04203);&quot; dir=&quot;ltr&quot;&gt;(N2) and 350 (N3) kg/ha. Soil sampling was conducted &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 678.408px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15634);&quot; dir=&quot;ltr&quot;&gt;in June, July, August and September from the soil &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 687.912px; font-size: 9.504px; font-family: serif; transform: scaleX(1.07377);&quot; dir=&quot;ltr&quot;&gt;surface to 1.2 m depth at intervals of 0.3 m depth. We &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 697.416px; font-size: 9.504px; font-family: serif; transform: scaleX(1.14365);&quot; dir=&quot;ltr&quot;&gt;used the LEACHM model for nitrate (NO&lt;/span&gt;&lt;span style=&quot;left: 295.776px; top: 701.16px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 298.944px; top: 697.416px; font-size: 9.504px; font-family: serif; transform: scaleX(1.14296);&quot; dir=&quot;ltr&quot;&gt;-N) and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 706.632px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05414);&quot; dir=&quot;ltr&quot;&gt;ammonium (NH4-N) simulation, and their comparison &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 716.136px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15498);&quot; dir=&quot;ltr&quot;&gt;with measured data. The amount of application of &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 725.352px; font-size: 9.504px; font-family: serif; transform: scaleX(1.18786);&quot; dir=&quot;ltr&quot;&gt;nitrogen and irrigation treatments indicated their &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 734.856px; font-size: 9.504px; font-family: serif; transform: scaleX(1.18693);&quot; dir=&quot;ltr&quot;&gt;important role in the accumulation of nitrate and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 744.072px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15121);&quot; dir=&quot;ltr&quot;&gt;ammonium in the soil profile. In this study, a high &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 753.576px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02511);&quot; dir=&quot;ltr&quot;&gt;concentration of NO&lt;/span&gt;&lt;span style=&quot;left: 193.536px; top: 757.32px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 196.992px; top: 753.576px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04882);&quot; dir=&quot;ltr&quot;&gt;-N was observed in I3N3 and also &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 763.08px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03319);&quot; dir=&quot;ltr&quot;&gt;a high concentration of NH&lt;/span&gt;&lt;span style=&quot;left: 220.896px; top: 766.824px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 224.064px; top: 763.08px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04703);&quot; dir=&quot;ltr&quot;&gt;-N accrued in the I3N3 and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 772.296px; font-size: 9.504px; font-family: serif; transform: scaleX(1.11441);&quot; dir=&quot;ltr&quot;&gt;I3N2 treatment. After some time, Nitrate leached to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 781.8px; font-size: 9.504px; font-family: serif; transform: scaleX(1.26126);&quot; dir=&quot;ltr&quot;&gt;subsurface depths and by the end of sampling &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 791.016px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03047);&quot; dir=&quot;ltr&quot;&gt;(September) the concentration at the 0-30 cm depth was &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 800.52px; font-size: 9.504px; font-family: serif; transform: scaleX(1.19002);&quot; dir=&quot;ltr&quot;&gt;zero. The model was calibrated with a change in &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 809.736px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05033);&quot; dir=&quot;ltr&quot;&gt;nitrification, denitrification and N volatilization for the &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 819.24px; font-size: 9.504px; font-family: serif; transform: scaleX(1.07446);&quot; dir=&quot;ltr&quot;&gt;three N treatments and model accuracy was increased &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 828.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03147);&quot; dir=&quot;ltr&quot;&gt;after calibration so that Willmott&#039;s index for NO&lt;/span&gt;&lt;span style=&quot;left: 301.824px; top: 832.488px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 305.28px; top: 828.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04781);&quot; dir=&quot;ltr&quot;&gt;-N and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 837.96px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0066);&quot; dir=&quot;ltr&quot;&gt;NH&lt;/span&gt;&lt;span style=&quot;left: 127.296px; top: 841.704px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 130.464px; top: 837.96px; font-size: 9.504px; font-family: serif; transform: scaleX(1.10623);&quot; dir=&quot;ltr&quot;&gt;-N after calibration was 0.56 to 0.98 and 0.76 to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 847.464px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01436);&quot; dir=&quot;ltr&quot;&gt;0.96, respectively. &lt;/span&gt;</Abstract>
			<OtherAbstract Language="FA">&lt;span style=&quot;left: 113.472px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.00928);&quot; dir=&quot;ltr&quot;&gt;Nitrate (NO&lt;/span&gt;&lt;span style=&quot;left: 159.552px; top: 560.328px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 163.008px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01788);&quot; dir=&quot;ltr&quot;&gt;-N) and ammonium (NH&lt;/span&gt;&lt;span style=&quot;left: 258.912px; top: 560.328px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 262.08px; top: 556.584px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02843);&quot; dir=&quot;ltr&quot;&gt;-N) leaching from &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 565.8px; font-size: 9.504px; font-family: serif; transform: scaleX(1.124);&quot; dir=&quot;ltr&quot;&gt;agricultural soils can represent substantial losses of &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 575.304px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05897);&quot; dir=&quot;ltr&quot;&gt;nitrogen (N) fertilizer, but a large variation in N losses &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 584.808px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05666);&quot; dir=&quot;ltr&quot;&gt;has been reported. The objectives of this study were to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 594.024px; font-size: 9.504px; font-family: serif; transform: scaleX(1.08275);&quot; dir=&quot;ltr&quot;&gt;assess the accumulation and movement of nitrate and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 603.528px; font-size: 9.504px; font-family: serif; transform: scaleX(1.13076);&quot; dir=&quot;ltr&quot;&gt;ammonium in the soil profile over the study period &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 612.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02628);&quot; dir=&quot;ltr&quot;&gt;under different irrigation and fertilizer conditions. So, N &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 622.248px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0449);&quot; dir=&quot;ltr&quot;&gt;concentration and its leaching were studied under three &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 631.464px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0542);&quot; dir=&quot;ltr&quot;&gt;N fertilizer and three irrigation treatments during 2007 &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 640.968px; font-size: 9.504px; font-family: serif; transform: scaleX(1.11974);&quot; dir=&quot;ltr&quot;&gt;Khuzestan Province, Iran. The irrigation treatments &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 650.472px; font-size: 9.504px; font-family: serif; transform: scaleX(1.06916);&quot; dir=&quot;ltr&quot;&gt;consisted of full irrigation (I1) and 85 (I2) and 70 (I3) &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 659.688px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01656);&quot; dir=&quot;ltr&quot;&gt;percent of I1. Also, the N treatments were 150 (N1), 250 &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 669.192px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04203);&quot; dir=&quot;ltr&quot;&gt;(N2) and 350 (N3) kg/ha. Soil sampling was conducted &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 678.408px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15634);&quot; dir=&quot;ltr&quot;&gt;in June, July, August and September from the soil &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 687.912px; font-size: 9.504px; font-family: serif; transform: scaleX(1.07377);&quot; dir=&quot;ltr&quot;&gt;surface to 1.2 m depth at intervals of 0.3 m depth. We &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 697.416px; font-size: 9.504px; font-family: serif; transform: scaleX(1.14365);&quot; dir=&quot;ltr&quot;&gt;used the LEACHM model for nitrate (NO&lt;/span&gt;&lt;span style=&quot;left: 295.776px; top: 701.16px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 298.944px; top: 697.416px; font-size: 9.504px; font-family: serif; transform: scaleX(1.14296);&quot; dir=&quot;ltr&quot;&gt;-N) and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 706.632px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05414);&quot; dir=&quot;ltr&quot;&gt;ammonium (NH4-N) simulation, and their comparison &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 716.136px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15498);&quot; dir=&quot;ltr&quot;&gt;with measured data. The amount of application of &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 725.352px; font-size: 9.504px; font-family: serif; transform: scaleX(1.18786);&quot; dir=&quot;ltr&quot;&gt;nitrogen and irrigation treatments indicated their &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 734.856px; font-size: 9.504px; font-family: serif; transform: scaleX(1.18693);&quot; dir=&quot;ltr&quot;&gt;important role in the accumulation of nitrate and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 744.072px; font-size: 9.504px; font-family: serif; transform: scaleX(1.15121);&quot; dir=&quot;ltr&quot;&gt;ammonium in the soil profile. In this study, a high &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 753.576px; font-size: 9.504px; font-family: serif; transform: scaleX(1.02511);&quot; dir=&quot;ltr&quot;&gt;concentration of NO&lt;/span&gt;&lt;span style=&quot;left: 193.536px; top: 757.32px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 196.992px; top: 753.576px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04882);&quot; dir=&quot;ltr&quot;&gt;-N was observed in I3N3 and also &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 763.08px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03319);&quot; dir=&quot;ltr&quot;&gt;a high concentration of NH&lt;/span&gt;&lt;span style=&quot;left: 220.896px; top: 766.824px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 224.064px; top: 763.08px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04703);&quot; dir=&quot;ltr&quot;&gt;-N accrued in the I3N3 and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 772.296px; font-size: 9.504px; font-family: serif; transform: scaleX(1.11441);&quot; dir=&quot;ltr&quot;&gt;I3N2 treatment. After some time, Nitrate leached to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 781.8px; font-size: 9.504px; font-family: serif; transform: scaleX(1.26126);&quot; dir=&quot;ltr&quot;&gt;subsurface depths and by the end of sampling &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 791.016px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03047);&quot; dir=&quot;ltr&quot;&gt;(September) the concentration at the 0-30 cm depth was &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 800.52px; font-size: 9.504px; font-family: serif; transform: scaleX(1.19002);&quot; dir=&quot;ltr&quot;&gt;zero. The model was calibrated with a change in &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 809.736px; font-size: 9.504px; font-family: serif; transform: scaleX(1.05033);&quot; dir=&quot;ltr&quot;&gt;nitrification, denitrification and N volatilization for the &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 819.24px; font-size: 9.504px; font-family: serif; transform: scaleX(1.07446);&quot; dir=&quot;ltr&quot;&gt;three N treatments and model accuracy was increased &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 828.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.03147);&quot; dir=&quot;ltr&quot;&gt;after calibration so that Willmott&#039;s index for NO&lt;/span&gt;&lt;span style=&quot;left: 301.824px; top: 832.488px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;3&lt;/span&gt;&lt;span style=&quot;left: 305.28px; top: 828.744px; font-size: 9.504px; font-family: serif; transform: scaleX(1.04781);&quot; dir=&quot;ltr&quot;&gt;-N and &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 837.96px; font-size: 9.504px; font-family: serif; transform: scaleX(1.0066);&quot; dir=&quot;ltr&quot;&gt;NH&lt;/span&gt;&lt;span style=&quot;left: 127.296px; top: 841.704px; font-size: 6.048px; font-family: serif;&quot; dir=&quot;ltr&quot;&gt;4&lt;/span&gt;&lt;span style=&quot;left: 130.464px; top: 837.96px; font-size: 9.504px; font-family: serif; transform: scaleX(1.10623);&quot; dir=&quot;ltr&quot;&gt;-N after calibration was 0.56 to 0.98 and 0.76 to &lt;/span&gt;&lt;span style=&quot;left: 113.472px; top: 847.464px; font-size: 9.504px; font-family: serif; transform: scaleX(1.01436);&quot; dir=&quot;ltr&quot;&gt;0.96, respectively. &lt;/span&gt;</OtherAbstract>
		<ObjectList>
			<Object Type="keyword">
			<Param Name="value">Keywords: LEACHM model</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Nitrate</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Ammonium</Param>
			</Object>
			<Object Type="keyword">
			<Param Name="value">Soil profile</Param>
			</Object>
		</ObjectList>
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