CN107202832B - Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area - Google Patents

Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area Download PDF

Info

Publication number
CN107202832B
CN107202832B CN201710409102.2A CN201710409102A CN107202832B CN 107202832 B CN107202832 B CN 107202832B CN 201710409102 A CN201710409102 A CN 201710409102A CN 107202832 B CN107202832 B CN 107202832B
Authority
CN
China
Prior art keywords
heavy metal
sample
detection method
electrode
mine area
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201710409102.2A
Other languages
Chinese (zh)
Other versions
CN107202832A (en
Inventor
王玉成
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hunan Shuo Yuan Detection Technology Co Ltd
Original Assignee
Hunan Shuo Yuan Detection Technology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hunan Shuo Yuan Detection Technology Co Ltd filed Critical Hunan Shuo Yuan Detection Technology Co Ltd
Priority to CN201710409102.2A priority Critical patent/CN107202832B/en
Publication of CN107202832A publication Critical patent/CN107202832A/en
Application granted granted Critical
Publication of CN107202832B publication Critical patent/CN107202832B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N27/00Investigating or analysing materials by the use of electric, electrochemical, or magnetic means
    • G01N27/26Investigating or analysing materials by the use of electric, electrochemical, or magnetic means by investigating electrochemical variables; by using electrolysis or electrophoresis
    • G01N27/416Systems
    • G01N27/48Systems using polarography, i.e. measuring changes in current under a slowly-varying voltage
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N1/00Sampling; Preparing specimens for investigation
    • G01N1/28Preparing specimens for investigation including physical details of (bio-)chemical methods covered elsewhere, e.g. G01N33/50, C12Q
    • G01N1/34Purifying; Cleaning
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N1/00Sampling; Preparing specimens for investigation
    • G01N1/28Preparing specimens for investigation including physical details of (bio-)chemical methods covered elsewhere, e.g. G01N33/50, C12Q
    • G01N1/44Sample treatment involving radiation, e.g. heat

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Pathology (AREA)
  • General Physics & Mathematics (AREA)
  • Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Biomedical Technology (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Sampling And Sample Adjustment (AREA)

Abstract

The invention belongs to heavy metal analysis technical fields, and in particular to heavy metal detection method in a kind of Near Antimony Mine Area soil water termination contaminated stream.By using anode voltammetry, using three-electrode system, using carboxylated graphene modified glass-carbon electrode as working electrode, carrying out test and data processing based on the sample that Near Antimony Mine Area soil water termination sampled point acquires.The method of the present invention measurement period is only 10min, and precision substantially increases minute up to 0.24%, and precision is high, accuracy is good, convenient, fast and efficient, detection limit is lower, and measurement sensitivity is higher, is suitble to the Pollution System of this complexity of Near Antimony Mine Area soil-water termination.

Description

Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area
Technical field
The invention belongs to heavy metal analysis technical fields, and in particular to heavy metal in a kind of Near Antimony Mine Area soil water termination contaminated stream Detection method.
Background technique
With the progress of human civilization, industrial development process is getting faster, demand of the mankind to mineral resources and exploitation It is growing, at the same time, inevitably along with the deterioration of ecological environment and to nature in the development process to mineral resources Destruction, resulting heavy metal pollution can not look down upon.The buried metal in underground of exploitation of mineral resources movable handle script of the mankind Ore is exposed in atmosphere and earth's surface, by the hydrologic cycles such as rainfall, runoff, sedimentation make heavy metal element be diffused into river, In soil, atmosphere, ecological environment is polluted, while also being constituted a threat to the living environment of the mankind.
Wherein, antimony ore paneling and the solid waste (ore, ettle, CHARACTERISTICS OF TAILINGS SAND, waste residue etc.) for selecting smelting to generate in the process and life Sewage etc. is produced to enter mining soil by different approaches and lead to heavy metal pollution of soil.It is cut by rainfall or snowmelt runoff It cuts, hit, washing away, leaching, the collective effects such as immersion, the various heavy metal contaminants in soil are between soil-diameter stream interface A variety of physical-chemical reactions such as diffusion, disperse, desorption, dissociation occur, ultimately form mining area soil-water termination heavy metal pollution stream, Its pollutant contains one kind of nutrients such as each heavy metal species, persistent organism and nitrogen, phosphorus etc. and non-point pollution Special representing form.It is special that different heavy metal elements shows different spatial distributions in soil-water termination heavy metal pollution stream Sign.Since non-ferrous metal mining area soil-water termination heavy metal pollution stream and ecological environment or even human health are closely bound up, always all It is the research field being concerned in environmental science.This requires fast and accurately to detect Polluted Soil-water termination heavy metal In contaminated stream, the pollution level of heavy metal.
Summary of the invention
Technical problem to be solved by the invention is to provide heavy metal analysis sides in a kind of Near Antimony Mine Area soil water termination contaminated stream Method, detection method includes the following steps for this:
(1) it samples and pre-processes: mining area sampling area area about 2.5~3.0km2, sampled point is evenly distributed in region, Sampling density is 0.03~0.04/km2Point arranges sampled point 125~140 altogether;It is greater than lower seep by force in natural precipitation intensity When degree generates runoff, each sampled point acquires earth's surface runoff water 0.8~2.5L of sample, and collected liquid is kept in dark place and is taken back; Institute's water sampling is shaken up before sample preparation, natural subsidence at least 40min, the non-settlement section in siphon upper layer, then with 0.2 μm of membrane filtration, HNO is added3PH is acidified between 1.5~3.5, gained water sample is stored refrigerated to post label;
(2) Hyperfrequency waves eliminating stove is then placed in as the dissolved oxygen being passed through in inert gas removing water sample in water sample before test sample Carry out micro-wave digestion;
(3) test sample: with anodic stripping voltammetry, using carboxylated graphene modified glass-carbon electrode as working electrode, Pt/ Ti electrode is saturated Ag/AgCl electrode as reference electrode as auxiliary electrode;Specific test condition are as follows: the work of enrichment process Potential is -1.2-1.1V, quiescent time 40s, 300~500s of enrichment time, and scanning speed 10mV/s makes water under agitation On heavy metal ion enrichment to working electrode in sample;Process in leaching working electrode potential is by -0.8-0.3V forward scan, scanning Rate 10mV/s dissolves out the heavy metal particle being enriched on working electrode;Register instrument data after measurement is completed, then carry out The analysis of data;Obtain the content of beary metal in sample;
(4) data processing: data processing is carried out to the content of beary metal in above-mentioned sample, it is more steady to choose measurement result Fixed, numerical value compares the group data of concentration;It is finally calculated, mainly precision, accuracy and recovery of standard addition is calculated, Compare the data obtained and calculated result.
Further, in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method, HNO in the step (1)3 Concentration be 8~13wt%.
Further, lazy in the step (2) in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method Property gas be nitrogen, nitrogen be passed through the time be 10~15min.
Further, the carboxylic in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method, in the step (3) Base graphite alkene modified glassy carbon electrode is prepared by following methods: by the nano-graphene piece of carboxymethyl functionalization according to solid-liquid Ratio than 1:1 is added in secondary distilled water, and 30~40min of ultrasonic disperse obtains carboxy methylation graphene suspension;Glass carbon Electrode is polished in after mirror surface, is successively cleaned by ultrasonic 4min in dehydrated alcohol and secondary distilled water, dries under infrared lamp; It takes 8~10uL carboxy methylation graphene suspension to be added dropwise with microsyringe to dry under glassy carbon electrode surface, infrared lamp.
Further, in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method, the stirring is stirred for magnetic force It mixes, revolving speed is 200~300rpm.
It is compared in the prior art, the beneficial effects of the present invention are: in soil water termination contaminated stream in Near Antimony Mine Area provided by the invention Heavy metal element detection method, by based on the sample that Near Antimony Mine Area soil water termination sampled point acquires, using anode voltammetry, It is tested using three-electrode system using carboxylated graphene modified glass-carbon electrode as working electrode, this method greatly improves Minute, and precision is high, accuracy is good, and convenient, fast and efficient, detection limit is lower, and measurement sensitivity is higher, fits Close the Pollution System of this complexity of Near Antimony Mine Area soil-water termination.In addition, the present invention can rapidly detect the degree of pollution, it is Subsequent improvement maintenance provides help, has great application value and social benefit.
Specific embodiment
The present invention provides heavy metal detection method in a kind of Near Antimony Mine Area soil water termination contaminated stream, the detection method include with Lower step:
(1) it samples and pre-processes: mining area sampling area area about 2.5~3.0km2, sampled point is evenly distributed in region, Sampling density is 0.03~0.04/km2Point arranges sampled point 125~140 altogether;It is greater than lower seep by force in natural precipitation intensity When degree generates runoff, each sampled point acquires earth's surface runoff water 0.8~2.5L of sample, and collected liquid is kept in dark place and is taken back; Institute's water sampling is shaken up before sample preparation, natural subsidence at least 40min, the non-settlement section in siphon upper layer, then with 0.2 μm of membrane filtration, The HNO that concentration is 8~13wt% is added3PH is acidified between 1.5~3.5, gained water sample is stored refrigerated to post label;
(2) Hyperfrequency waves eliminating stove is then placed in as the dissolved oxygen being passed through in inert gas removing water sample in water sample before test sample Carry out micro-wave digestion;
(3) test sample: with anodic stripping voltammetry, using carboxylated graphene modified glass-carbon electrode as working electrode, Pt/ Ti electrode is saturated Ag/AgCl electrode as reference electrode as auxiliary electrode;Specific test condition are as follows: the work of enrichment process Potential is -1.2-1.1V, quiescent time 40s, 300~500s of enrichment time, and scanning speed 10mV/s makes water under agitation On heavy metal ion enrichment to working electrode in sample;Process in leaching working electrode potential is by -0.8-0.3V forward scan, scanning Rate 10mV/s dissolves out the heavy metal particle being enriched on working electrode;Register instrument data after measurement is completed, then carry out The analysis of data;Obtain the content of beary metal in sample;
(4) data processing: data processing is carried out to the content of beary metal in above-mentioned sample, it is more steady to choose measurement result Fixed, numerical value compares the group data of concentration;It is finally calculated, mainly precision, accuracy and recovery of standard addition is calculated, Compare the data obtained and calculated result.
Further, lazy in the step (2) in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method Property gas be nitrogen, nitrogen be passed through the time be 10~15min.
Further, the carboxylic in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method, in the step (3) Base graphite alkene modified glassy carbon electrode is prepared by following methods: by the nano-graphene piece of carboxymethyl functionalization according to solid-liquid Ratio than 1:1 is added in secondary distilled water, and 30~40min of ultrasonic disperse obtains carboxy methylation graphene suspension;Glass carbon Electrode is polished in after mirror surface, is successively cleaned by ultrasonic 4min in dehydrated alcohol and secondary distilled water, dries under infrared lamp; It takes 8~10uL carboxy methylation graphene suspension to be added dropwise with microsyringe to dry under glassy carbon electrode surface, infrared lamp.
Further, in above-mentioned Near Antimony Mine Area soil water termination contaminated stream in heavy metal detection method, the stirring is stirred for magnetic force It mixes, revolving speed is 200~300rpm.
Below in conjunction with specific embodiment, the present invention will be further explained and explanation, but is not intended to limit the present invention Protection scope.
Embodiment
Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area the following steps are included:
(1) research area is located at the precious Daxing Near Antimony Mine Area of Hunan Lengshuijiang City tinnery, it is located at Lengshuijiang City mine township, tin At the township Ji Zhonglian, mine office boundary position, south is east longitude 111 ° 25 ' 47 away from 13 km of Lengshuijiang City, geographical coordinate "~ 111 ° 31 ' 22 ", 27 ° 49 ' 28 of north latitude "~27 ° 43 ' 05 ".Sampling area area about 2.6km2, sampled point more uniform distribution grinding Study carefully in area, sampling density is 0.03/km2Point arranges sampled point 130 altogether;It is produced in natural precipitation intensity greater than infltration intensity When raw runoff, each sampled point acquires earth's surface runoff water sample 2.0L, is put into polyethylene bottle and takes back after being packed with black plastic bag Laboratory.Institute's water sampling is shaken up in laboratory, natural subsidence 40min, the non-settlement section in siphon upper layer, then is filtered with 0.2 μm The HNO that concentration is 10wt% is added in film filtering3It is acidified to pH 2.0, gained water sample is stored refrigerated to post label, carries out sampling note Record;
(2) Hyperfrequency waves eliminating stove is then placed in as the dissolved oxygen being passed through in inert gas removing water sample in water sample before test sample Carry out micro-wave digestion;
(3) test sample: with anodic stripping voltammetry, using carboxylated graphene modified glass-carbon electrode as working electrode, Pt/ Ti electrode is saturated Ag/AgCl electrode as reference electrode as auxiliary electrode;Specific test condition are as follows: the work of enrichment process Potential is -1.2-1.1V, quiescent time 40s, enrichment time 500s, scanning speed 10mV/s, under the conditions of magnetic agitation (revolving speed 200rpm) make on the heavy metal ion enrichment to working electrode in water sample;Process in leaching working electrode potential by -0.8-0.3V just To scanning, sweep speed 10mV/s dissolves out the heavy metal particle being enriched on working electrode;Register instrument after measurement is completed Data, then carry out the analysis of data;Obtain the content of beary metal in sample;
Wherein, carboxylated graphene modified glass-carbon electrode is prepared by following methods: by the nanometer of carboxymethyl functionalization Graphene film is added in secondary distilled water according to the ratio of solid-to-liquid ratio 1:1, ultrasonic disperse 40min, obtains the carboxylic first of 1mg/mL Base graphite alkene suspension;Glass-carbon electrode is polished in after mirror surface, is successively cleaned by ultrasonic in dehydrated alcohol and secondary distilled water 4min is dried under infrared lamp;9uL carboxy methylation graphene suspension is taken to be added dropwise in glass-carbon electrode table with microsyringe Face is dried under infrared lamp;
(4) data processing: data processing is carried out to the content of beary metal in above-mentioned sample, it is more steady to choose measurement result Fixed, numerical value compares the group data of concentration;It is finally calculated, mainly precision, accuracy and recovery of standard addition is calculated, Compare the data obtained and calculated result;
The test result of heavy metal is shown in Table 1 in the soil water termination contaminated stream of Near Antimony Mine Area:
Table 1.
Heavy metal Sb Zn Cu Ni Pb Cd
Average value (mg/L) 1.1597 1.005 0.7991 0.0074 0.0113 0.0048
Detection method measures the period as 10min, and precision is up to 0.24%, and the measurement period is short, and precision is accurate, fits Close native water termination pollution complicated and changeable.
The above is the preferred embodiment of the present invention, it is noted that for those skilled in the art, is not being taken off Under the premise of from structure of the invention, various modifications and improvements can be made, these should also be as being considered as protection scope of the present invention, These all will not influence the practicability of effect and this patent that the present invention is implemented.

Claims (5)

1. heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area, which is characterized in that detection method includes the following steps for this:
(1) it samples and pre-processes: mining area 2.5~3.0km of sampling area area2, sampled point is evenly distributed in region, oversampling Degree is 0.03~0.04/km2Point arranges sampled point 125~140 altogether;It is generated in natural precipitation intensity greater than infltration intensity When runoff, each sampled point acquires earth's surface runoff water 0.8~2.5L of sample, and collected liquid is kept in dark place and is taken back;Before sample preparation Institute's water sampling is shaken up, natural subsidence at least 40min, the non-settlement section in siphon upper layer, then with 0.2 μm of membrane filtration, is added HNO3PH is acidified between 1.5~3.5, gained water sample is stored refrigerated to post label;
(2) dissolved oxygen being passed through before test sample into water sample in inert gas removing water sample, is then placed in Hyperfrequency waves eliminating stove progress Micro-wave digestion;
(3) test sample: with anodic stripping voltammetry, using carboxylated graphene modified glass-carbon electrode as working electrode, Pt/Ti electricity Pole is saturated Ag/AgCl electrode as reference electrode as auxiliary electrode;Specific test condition are as follows: the work potential of enrichment process Make water sample under agitation for -1.2~1.1V, quiescent time 40s, 300~500s of enrichment time, scanning speed 10mV/s In heavy metal ion enrichment to working electrode on;Process in leaching working electrode potential is by -0.8~0.3V forward scan, scanning Rate 10mV/s dissolves out the heavy metal particle being enriched on working electrode;Register instrument data after measurement is completed, then carry out The analysis of data;Obtain the content of beary metal in sample;
(4) data processing: data processing is carried out to the content of beary metal in above-mentioned sample, selection measurement result is more stable, counts Value compares the group data of concentration;It is finally calculated, mainly precision, accuracy and recovery of standard addition is calculated, compared The data obtained and calculated result.
2. heavy metal detection method in soil water termination contaminated stream in Near Antimony Mine Area according to claim 1, which is characterized in that described HNO in step (1)3Concentration be 8~13wt%.
3. heavy metal detection method in soil water termination contaminated stream in Near Antimony Mine Area according to claim 1, which is characterized in that described Inert gas in step (2) is nitrogen, and the time that is passed through of nitrogen is 10~15min.
4. heavy metal detection method in soil water termination contaminated stream in Near Antimony Mine Area according to claim 1, which is characterized in that described Carboxylated graphene modified glass-carbon electrode in step (3) is prepared by following methods: by the nanometer stone of carboxymethyl functionalization Black alkene piece is added in secondary distilled water according to the ratio of solid-to-liquid ratio 1:1, and 30~40min of ultrasonic disperse obtains carboxymethyl fossil Black alkene suspension;Glass-carbon electrode is polished to be successively cleaned by ultrasonic 4min in after mirror surface in dehydrated alcohol and secondary distilled water, then It is dried under infrared lamp;8~10 μ L carboxy methylation graphene suspensions are taken to be added dropwise in glassy carbon electrode surface with microsyringe, it is red It is dried under outer lamp.
5. heavy metal detection method in soil water termination contaminated stream in Near Antimony Mine Area according to claim 1, which is characterized in that described Stirring is magnetic agitation, and revolving speed is 200~300rpm.
CN201710409102.2A 2017-06-02 2017-06-02 Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area Active CN107202832B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710409102.2A CN107202832B (en) 2017-06-02 2017-06-02 Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710409102.2A CN107202832B (en) 2017-06-02 2017-06-02 Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area

Publications (2)

Publication Number Publication Date
CN107202832A CN107202832A (en) 2017-09-26
CN107202832B true CN107202832B (en) 2019-07-02

Family

ID=59906656

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710409102.2A Active CN107202832B (en) 2017-06-02 2017-06-02 Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area

Country Status (1)

Country Link
CN (1) CN107202832B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109304365B (en) * 2018-12-03 2021-09-28 南京迪天高新产业技术研究院有限公司 Electric remediation method for antimony-polluted soil

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB0111118D0 (en) * 2001-05-05 2001-06-27 Univ Durham Sensor and sensing method for detection and process control
SG177021A1 (en) * 2010-06-16 2012-01-30 Univ Nanyang Tech Micoelectrode array sensor for detection of heavy metals in aqueous solutions
KR101424758B1 (en) * 2012-12-27 2014-08-01 한국광해관리공단 Portable heavy metal detector of ground water with mine drainage and method for measuring pollution level of groudwater with mine drainage thereof
CN103604845A (en) * 2013-10-30 2014-02-26 湖北出入境检验检疫局检验检疫技术中心 Electrochemical probe used for rapid detection of trace amount of heavy metal ions, and manufacturing method of electrochemical probe
CN106645371A (en) * 2015-11-03 2017-05-10 吉林天士力矿泉饮品有限公司 Determination method for heavy metal content in mineral water
CN105424781A (en) * 2015-11-05 2016-03-23 北京农业智能装备技术研究中心 Soil heavy metal content detection method based on microelectrode detection technology

Also Published As

Publication number Publication date
CN107202832A (en) 2017-09-26

Similar Documents

Publication Publication Date Title
Adelopo et al. Multivariate analysis of the effects of age, particle size and landfill depth on heavy metals pollution content of closed and active landfill precursors
Kong et al. Levels, risk assessment and sources of PM10 fraction heavy metals in four types dust from a coal-based city
Yang et al. Distribution and speciation of heavy metals in sediments from the mainstream, tributaries, and lakes of the Yangtze River catchment of Wuhan, China
Teng et al. A geochemical survey of trace elements in agricultural and non-agricultural topsoil in Dexing area, China
Gabrielyan et al. Distribution and identification of sources of heavy metals in the Voghji River basin impacted by mining activities (Armenia)
Dong et al. Heavy metals in Changjiang estuarine and offshore sediments: responding to human activities
Sun et al. Tracing of heavy metal sources and mobility in a soil depth profile via isotopic variation of Pb and Sr
Oguchi et al. River water quality in the Humber catchment: an introduction using GIS-based mapping and analysis
Zakir et al. Cadmium and lead pollution in sediments of midstream of the river Karatoa in Bangladesh
Franzmann et al. Microbial biomass in a shallow, urban aquifer contaminated with aromatic hydrocarbons: analysis by phospholipid fatty acid content and composition
Zhou et al. Distribution characteristics and potential ecological risk assessment of heavy metals in soils around Shannan landfill site, Tibet
CN107202832B (en) Heavy metal detection method in the soil water termination contaminated stream of Near Antimony Mine Area
Haiyan et al. Current status and development trend of soil microbial biogeography
Liang et al. Historical trends in atmospheric metal (loid) contamination in North China over the past half-millennium reconstructed from subalpine lake sediment
Saint-Laurent et al. Isotopic record of lead contamination in alluvial soils and tree rings on recent floodplains (Southern Québec, Canada)
Xia et al. Lake sediment archive reveals a distinct response to anthropogenic Pb and Zn deposition with historical periods: Pb–Zn isotope evidence
Ling et al. Spatial distribution and environmental risk assessment of heavy metals identified in soil of a decommissioned uranium mining area
An et al. Seasonal co-pollution characteristics of parent-PAHs and alkylated-PAHs in karst mining area soil of Guizhou, Southwest China
Kwiatkowska-Malina et al. Geostatistical modelling of soil contamination with arsenic, cadmium, lead, and nickel: the Silesian voivodeship, Poland case study
Aravena et al. Chemical and carbon isotopic composition of dissolved organic carbon in a regional confined methanogenic aquifer
Kumar et al. A record on benthic foraminiferal abundance and distribution in Gosthani estuary, Bheemunipatnam, Andhra Pradesh.
Lee et al. Establishing freshwater sediment sample pretreatment methods for monitoring microplastics and its challenges
Li et al. Evaluation of organic-walled dinoflagellate cyst distributions in coastal surface sediments of the China Seas in relation with hydrographic conditions for paleoceanographic reconstruction
You et al. CHEMICAL SPECIATION AND RISK ASSESSMENT OF TRACE ELEMENTS IN THE SOIL OF THE AGRICULTURAL AREA IN HUAINAN, CHINA.
Matschullat et al. Epilithic lichen—atmospheric deposition monitors of trace elements and organohalogens?

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant