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Analysis of Soils With Historic Arsenical Pesticide Applications for Arsenic and Lead Contentent

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Philip Lavallee Jr E P S C o R 2 0 1 3 U n d e r g r a d u a t e R e s e a r c h D ay B r a n d o n R e y n o l d s · S c o t t S c h e l l · P r o f . K . J. R e d d y D e p t . o f E c o s y s t e m S c i e n c e a n d M a n a g e m e n t C o l l e g e o f A g r i c u l t u r e a n d N a t u r a l R e s o u r c e s U n i v e r s i t y o f Wy o m i n g

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» Discussion with Landowner » Background Research

» Permission and Support for Project » Location/Sampling

» Methods and Materials » Results

» Discussion

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» Scott Schell - UW Extension Service

» Contacted by landowner about orchard in

western Fremont County, Wyoming

Looking into history of 100+ year old apple orchard

Period applications of arsenical pesticides

Landowner interested in fate of relict As and Pb from pesticide application

(4)

Banning of pesticides and lag effect

applications

Residual traces of lead arsenate pesticides

and their fate

(leaching, mobility)

» Arsenic contamination an issue with

increasing research

» Lead contamination » EPA Values

(5)

» Landowner gave permission for study

Results of study shared with landowner

» Proposal written

Support/funding for study by Prof. K.J. Reddy, has conducted extensive arsenic research

» EPSCoR approval and support

Within proposal: background, written sampling methods, processing methods, hypothesis,

(6)

» Gain experience in:

Sample collection

Lab analysis

Interpreting and presenting results

» Work with landowner

Share results of study

Work with landowner on possible

remediation/treatment/course of action if mobility of As or Pb observed

(7)

» Determine presence/absence of relict As

and Pb in water soluble fraction from soil solution

» Determine soil pH, due to influence of pH

on mobility of As and Pb

» Determine mobility if As and Pb are found

to be present

Vertical mobility through soil profile

(8)

» Hypothesis: If present, relict As and Pb

will be bound within 30cm of soil profile and show minimal to no movement across slope

(9)
(10)

» 2 transects (20m long)

» 3 sampling points/transect (A,B,C) » 3 sampling depths/point

(0-10cm,10-20cm,20-30cm)

» 2 control samples (1 above, 1 below

orchard)

(11)

0-10 cm 10-20 cm 20-30 cm 20 meters A B C 10 meters

(12)

T1 T2 Control B (Lower) Control A (Upper) Stream Irrigation Ditch A B C A B C -Rough dimensions -Not to scale

(13)

» Samples brought back to Water Quality

Lab at UW

» Ground and sieved the soil samples to

2mm

» Mixed 100g soil, 100ml DI water; extracted

after 30min

» Samples filtered, acidified and

refrigerated, measured for pH

» ICP-MS analysis for As and Pb performed

by ALS Environmental Labs, Ft. Collins, CO

(14)

» Results showed presence of relict As and

Pb in water soluble form of soil solution

Vertical mobility in the soil profile?

Movement over surface down slope to stream?

» Observed minimal vertical and horizontal

mobility of As and Pb

» Soil pH was similar throughout sampling

(15)

» Mostly uniform and neutral

Increasing with depth due to OM at surface

» At pH < 8.2, calcium carbonate negatively

(16)

5.00 5.50 6.00 6.50 7.00 7.50 8.00 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A B C Cont rol

T1/Control - pH

(17)

5.00 5.50 6.00 6.50 7.00 7.50 8.00 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A2 B2 C2 Contr ol

T2/Control - pH

(18)

» Lead within background levels

Most samples at or below detection limitNo apparent trends in data

» Arsenic within background levels

At or near detection with decreasing amounts in lower profile

No noticeable increase down slope in the orchard, indicating no surface movement

(19)

0.00000 0.00020 0.00040 0.00060 0.00080 0.00100 0.00120 0.00140 0.00160 0.00180 0.00200 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A B C Contr ol

T1/Control - Pb (mg/kg)

Samples at or below detection limit (0.0005 mg/kg)

(20)

0.00000 0.00050 0.00100 0.00150 0.00200 0.00250 0.00300 0.00350 0.00400 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A2 B2 C2 Contr ol

T2/Control - Pb (mg/kg

) Samples at or below detection limit (0.0005 mg/kg)

(21)

0.0000 0.0010 0.0020 0.0030 0.0040 0.0050 0.0060 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A B C Contr ol

T1/Control - As (mg/kg)

Samples lower than detection limit

(22)

0.0000 0.0005 0.0010 0.0015 0.0020 0.0025 0.0030 0.0035 0.0040 0.0045 0.0050 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm 0-10cm 10-20cm 20-30cm ControlA ControlB A2 B2 C2 Contr ol

T2/Control - As (mg/kg)

Samples lower than detection limit (0.002 mg/kg)

(23)

» EPA Drinking Water Regulations

(24)

» Orchard sample levels of As and Pb are

not functionally higher than control samples

» Levels of water soluble As and Pb are

lower than EPA Drining Water Regulation

» Horizontal surface and vertical soil profile

movement is not apparent

» Likely most relict As and Pb tied into soil

carbonates or already leached

Possibly bound in soil in non-water soluble fraction, further investigation needed

(25)

Landowner

Brandon Reynolds – UW ESM Dept.Scott Schell – UW ESM/Ag ExtensionProf. K.J. Reddy – UW ESM Dept.

Wyoming EPSCoR Program

(26)

Cox, Craig A. "Problems Associated with Historic Use of Arsenical Pesticides Still Linger." Arsenical Pesticides. Cox-Colvin and Associates Inc. Environmental Services. 25 Apr. 2013

<http://www.coxcolvin.com/Arsenical_Pesticides.php>. "Arsenic in Drinking Water." Home. 25 Apr. 2013

<http://water.epa.gov/lawsregs/rulesregs/sdwa/arsenic/index.c

References

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