WHO. 2007. Joint FAO/WHO Expert standards program codex Alimentation Commission. Geneva, Switzerland. Available online http://www.who.int [Accessed 10/09/2012].
Awashthi, S. K. (2000). Prevention of Food Adulteration Act No. 37 of 1954. Central and State rules as amended for 1999 (3rd ed.). New Delhi: Ashoka Law House.
Thank you for your kind information. Can you please share with me the details of the reference (or it's link) you have mentioned so that I will go through it?
I am attaching the copy of the original Document with the list of Maximum permissible (tolerable as you said) concentrations of some pollutants in soil (mg/kg of air dry weight). Sorry that it is in Russian. It can be translated to English as: Enactment of Supreme State Sanitary Doctor (Inspector) of Russian Federation from 23.01.2006 “On introduction into the force of hygienic norms GN 2.1.7.2041-06”.
At the same time I would like to emphasize that it is impossible to establish unique soil pollution standards for all countries. These standards are very dependent on regional geochemical particularities and vary widely. Therefore probably you could not find WHO standards.
Besides that I am in a great doubt that given by Avinash Kumar data for Pb – 250-500 and Ni – 75-150, Zn – 300-600 and Cu – 135-270 are correct. E.g. Cu is highly toxic metal, especially if it in mobile fraction and given concentration is most probably having chronicle toxic impact on soil micro flora. You have to check these figures for correctness.
Thank you for your information. In addition I have checked Mr. Avinash Kumar data and found it's correct for the Indian context. Once again thank you for sharing your information.
Maximum permissible concentrations of heavy metals in agricultural soils of European countries as reported by Kabata-Pendias and Pendias (2001) are listed below:
Cd (cadmium) 5 mg/kg, Co (cobalt) 50 mg/kg, Cr (chromium) 100 mg/kg, Cu (copper) 100 mg/kg, Ni (nickel) 100 mg/kg, Pb (lead) 100 mg/kg, and Zn (zinc) 300 mg/kg.
Reference: Kabata-Pendias A. and Pendias H. (2001) Trace elements in soils and plants. 3rd edition. CRC Press, Boca Raton, Florida, 413 pp.
I also attach PDF copy of an article on this subject. Hope you find this input interesting and useful.
In my country Venezuela there are two differents criteria. First to agricultural purpose which depends on plant uptake and tolerance physiological. Second to irrigation water, ambiental purpose, Pb limited 0,01 mg/L, Na 200 mg/L, Cu 20 mg/L (Standard Methods for Water and Lixiaviations).
Your question leads to a plethora of open problems in soil sciences - and straight on answer would be misleading (unfortunately). There are lots of tables of tolerable, permissible, precautionary levels, etc., all for total concentrations in agricultural soils. On the one hand, few tables present values modified according the soil character (clay / silt / sand), which makes quite a difference for plant availability. On the other hand, as pointed out by Bakhtiyor Karimov most important is the concentration of the mobile fraction. However, the question remains: what is mobile and under which conditions – and how to define mobility. The German Federal Soil Protection Act and Ordinance (1999) recommends the use of ammonium nitrate (1 m) to define plant availability, whereas the US EPA defines a TCLP (Toxicity Characteristic Leaching Procedure) which uses acetic acid; and there are many more suggestions. All these methods are batch procedures, which give no insight into the mobilization characteristics of soil constituents, i.e. information on possible plant availability. An advanced assessment of availability can be derived from a sequential elution method as published by Tessier et al. (1979); since then the method was modified and adapted to different substrates several times. By its main structure the method yields an assessment of bonding form portions, five of which can be mobilized according the environment conditions (adsorbed phase, carbonates, bound to Fe-Mn-Ox-Hydrox., bound to Fe- Ox-Hydrox., sulfides/humic substances). Finally a stable portion is defined (silicates, stable oxides), which is not available. By this an assessment of plant availability is more realistic than knowledge of total values or assessments based on batch experiments, both of which can be quite misleading. I agree that the approach of sequential elution requires much more care, skills in sampling and analysis, and analytical equipment; but under the aspect of ever-increasing soil use and soil pollution this approach should be worth while.
As epressed by many researchers, this is not an easy question to answer. However, apart from the suggestions already made, there other lists with suggestions (guidelines) regarding this issue, for example:
1. The New Dutch List,
2. ICRCL 59-83 (Interdepartmental Committee on the Redevelopment of
Contaminated Land),
3. The Kelly Indices, etc.
One must be very carefull befor jumping into cocnlusions, as many parameters are important (i.e., dissolution techniques, analytical techniques, type of soil etc.).
You can find additional screening values of various derivations (such as US background levels, older Dutch standards, and US EPA Eco-Soil Screening Levels) in the SQuiRT cards [attached ]. Keep in mind these cards have not been updated since 2008. In comparison though, I agree with Bakhtiyor that the values he referenced seem too high.
The "best" answer to your question though truly depends on the objective of your study. If you are merely in a screening level assessment, many of the sources others have provided here would suffice as comparative screening guidelines. If your ultimate goal is a more robust risk assessment of a specific area, the factors that influence form and availability of trace elements in soil, which others have also referred to, cannot be ignored. The next step beyond a screening level assessment would depend on your resources and the scale of your study.
I endorse the suggestion of Dr.Yurij to determine the background levels of heavy metals in dominant soil /soils in a specific area to know build up if any of the contaminated heavy metals in that area.