Soil Phosphorus Content Detection: Total Phosphorus, Available Phosphorus, and Inorganic Phosphorus Fraction Analysis
Soil Phosphorus Content Detection: Total Phosphorus, Available Phosphorus, and Inorganic Phosphorus Fraction Analysis
Soil phosphorus content detection is an important method for evaluating the size of the soil phosphorus pool, the phosphorus supply capacity for plants, and the risk of phosphorus accumulation. Total phosphorus reflects soil phosphorus reserves, available phosphorus reflects phosphorus fractions that can be absorbed by plants or readily transformed for use in the short term, and inorganic phosphorus fraction analysis is used to explain the fixation, release, and transformation mechanisms of phosphorus in soil.
Keywords: soil phosphorus; soil total phosphorus; total phosphate; available phosphorus; inorganic phosphorus; phosphorus fractions; molybdenum blue colorimetry; soil fertility evaluation
1 Research Entry Points for Soil Phosphorus Content Detection
1.1 Indicator Boundaries of Total Phosphorus, Available Phosphorus, and Phosphorus Fractions
Phosphorus in soil does not exist in a single form, but is distributed among multiple fractions, including mineral-bound phosphorus, adsorbed inorganic phosphorus, organic phosphorus, and residual phosphorus. Total phosphorus is used to evaluate the overall size of the soil phosphorus pool, but it does not directly represent plant availability. Available phosphorus is closer to the short-term phosphorus supply capacity for crops, but it cannot explain the mechanisms by which phosphorus is fixed or released. Inorganic phosphorus fraction analysis can further distinguish water-soluble phosphorus, weakly adsorbed phosphorus, iron/aluminum-bound phosphorus, calcium-bound phosphorus, and other fractions, and is used to analyze the sources of differences in phosphorus availability.
Detection Indicator | Main Question Answered | Applicable Scenario |
Total phosphorus/total phosphate | Total amount of the soil phosphorus pool | Long-term fertilization, soil background values, phosphorus accumulation evaluation |
Available phosphorus/rapidly available phosphorus | Short-term plant-available phosphorus level | Fertility evaluation, fertilization management, phosphorus supply assessment |
Water-soluble phosphorus | Easily mobile and easily lost phosphorus level | Runoff risk and eutrophication risk evaluation |
Inorganic phosphorus fractions | Phosphorus fixation and release mechanisms | Soil amendment, phosphorus fixation mechanisms, fraction transformation analysis |
Organic phosphorus estimation | Potential size of the organic phosphorus pool | Organic fertilizer, straw return, soil phosphorus transformation research |
1.2 Necessity of Multi-Indicator Combined Detection
A single phosphorus indicator is insufficient to fully reflect soil phosphorus status. High total phosphorus with low available phosphorus usually suggests that soil phosphorus reserves are sufficient but availability is limited. Simultaneous increases in available phosphorus and water-soluble phosphorus may indicate enhanced short-term phosphorus supply capacity along with potential environmental mobility risk. When both total phosphorus and available phosphorus are low, the result more likely reflects an insufficient soil phosphorus pool. By jointly analyzing total phosphorus, available phosphorus, and phosphorus fractions, different issues such as insufficient phosphorus reserves, enhanced fixation, and excessive accumulation can be distinguished.
2 Soil Total Phosphorus and Total Phosphate Detection
2.1 Basic Principle of Total Phosphorus Detection
Soil total phosphorus detection usually requires acid digestion, alkaline fusion, or other complete decomposition methods to convert different forms of phosphorus in soil into measurable orthophosphate, followed by quantification using molybdenum blue colorimetry or instrumental analysis. Therefore, “soil total phosphorus/total phosphate content detection” can be used together in experimental descriptions. However, the pretreatment logic should be clearly stated in the method description: the detection signal usually comes from orthophosphate released after digestion, rather than direct measurement of all original phosphorus forms in soil.
2.2 Digestion-Molybdenum Blue Colorimetric Method
The digestion-molybdenum blue colorimetric method is widely used in soil total phosphorus detection. After acid digestion or other decomposition treatment, orthophosphate reacts with molybdate to form phosphomolybdic heteropoly acid, which is then reduced to form a blue complex. Phosphorus content is calculated based on absorbance.
This method is suitable for batch sample detection and has the advantages of relatively low cost and a mature operating system. Key experimental factors include digestion completeness, stability of reagent blanks, color development time control, the linear range of the standard curve, and correction for sample matrix interference. For soil samples rich in iron oxides, organic matter, or fine mineral particles, attention should be paid to the clarity of the digest, background absorbance, and spike recovery.
2.3 Alkaline Fusion and Instrumental Methods
For soil samples with a high proportion of poorly soluble mineral phosphorus or stable mineral structures, alkaline fusion can be used to improve sample decomposition. Alkaline fusion has strong release capacity, but the procedure is more complex, and reagent blanks and salt matrices may affect subsequent detection. Instrumental methods such as ICP-OES and ICP-MS are suitable for multi-element analysis and can simultaneously detect P, Fe, Al, Ca, and other elements, helping to analyze the relationship between phosphorus fixation and soil mineral composition.
Method | Applicable Samples | Advantages | Limitations |
Acid digestion-molybdenum blue colorimetry | Routine agricultural soils and ecological soils | Low cost and suitable for batch detection | Depends on digestion completeness and color development stability |
Alkaline fusion-colorimetry | Soils with a high proportion of poorly soluble mineral phosphorus | Strong decomposition capacity | Complex operation, with higher blank and salt interference |
Digestion-ICP-OES | Samples requiring multi-element combined detection | Can simultaneously detect P, Fe, Al, Ca, and other elements | Higher instrument requirements and higher cost |
Digestion-ICP-MS | Low-content or refined multi-element analysis | High sensitivity | High requirements for matrix interference control and method development |
3 Soil Available Phosphorus Detection
3.1 Experimental Significance of Available Phosphorus
Available phosphorus reflects phosphorus fractions in soil that are readily absorbed by plants or can be transformed for use in the short term. It is a commonly used indicator in soil fertility evaluation and fertilization management. Available phosphorus does not represent all releasable phosphorus in soil, but rather the active phosphorus fraction obtained under a specific extraction system. Therefore, it is strongly method-dependent.
Available phosphorus results must be interpreted together with soil type. Acidic soils, calcareous soils, and neutral soils differ in phosphorus fixation mechanisms, and the extraction reagents used are also different. Available phosphorus values obtained by different methods should not be directly compared horizontally.
3.2 Available Phosphorus Detection in Acidic and Neutral/Alkaline Soils
In acidic soils, phosphorus often undergoes adsorption, precipitation, or complexation with iron and aluminum oxides or hydroxides. Therefore, rapidly available phosphorus detection should focus on Fe/Al-bound active phosphorus fractions. In neutral to alkaline soils, calcium-bound phosphorus and carbonate systems have a more pronounced effect on phosphorus availability. The method for rapidly available phosphorus detection should match soil pH and the regional fertility evaluation system.
Soil Type | Main Limiting Factor | Detection Focus | Interpretation Point |
Acidic soil | Fe/Al fixation and acidic adsorption sites | Rapidly available phosphorus in acidic soil | Should be interpreted together with pH, Fe/Al background, and fertilization history |
Neutral soil | Adsorbed phosphorus and active inorganic phosphorus | Rapidly available phosphorus in neutral soil | Suitable for evaluating short-term phosphorus supply capacity |
Alkaline soil | Ca-P formation and carbonate effects | Rapidly available phosphorus in alkaline soil | Calcium-bound phosphorus and pH effects should be considered |
Recently fertilized soil | Short-term increase in water-soluble phosphorus | Rapidly available phosphorus + water-soluble phosphorus | Sampling time and fertilization interval should be controlled |
3.3 Interpretation of Available Phosphorus Results
Low available phosphorus may indicate insufficient soil phosphorus supply capacity, but it may also be related to poor compatibility of the extraction method. High available phosphorus usually indicates strong short-term phosphorus supply capacity, but long-term high available phosphorus may increase the risk of phosphorus runoff loss and water eutrophication. In agricultural applications, soil pH, organic matter, crop phosphorus uptake, fertilization history, and regional soil fertility grading standards should be considered for comprehensive interpretation.
4 Soil Inorganic Phosphorus Fraction Analysis
4.1 Significance of Inorganic Phosphorus Fraction Analysis
Soil inorganic phosphorus consists of multiple fractions with markedly different activities. Water-soluble phosphorus and weakly adsorbed phosphorus are highly active but usually present at low levels. Iron/aluminum-bound phosphorus is more common in acidic soils; calcium-bound phosphorus is more prominent in calcareous soils; occluded phosphorus and residual phosphorus are slowly released and have low short-term plant availability.
Inorganic phosphorus fraction analysis is suitable for explaining why “total phosphorus is not low but available phosphorus is insufficient.” It can also be used to evaluate the effects of fertilization systems, soil amendments, straw return, biochar application, or long-term cultivation on phosphorus fixation and release.
4.2 Common Inorganic Phosphorus Fractions
Inorganic Phosphorus Fraction | Activity Characteristics | Common Soil Background | Research Significance |
Water-soluble phosphorus | Highest activity and easily mobile | Short-term increase after fertilization | Phosphorus supply capacity and environmental loss risk |
Weakly adsorbed phosphorus | Relatively easy to desorb | Rhizosphere and soils rich in active surfaces | Short-term source of available phosphorus |
Al-P | Moderate activity | Common in acidic soils | Related to aluminum oxides and acidic fixation |
Fe-P | Moderate to relatively low activity | Soils rich in iron oxides | Strongly affected by redox conditions |
Ca-P | Variable activity | Common in calcareous soils | Affected by pH, organic acids, and carbonate systems |
Occluded phosphorus/residual phosphorus | Low activity and slow release | Weathered minerals or strongly fixed soils | Represents long-term stable phosphorus pools |
4.3 Sequential Extraction Method
Sequential extraction methods use different extractants to release phosphorus fractions with different activities in sequence and are used to distinguish different binding forms. Common fractionation frameworks include resin phosphorus, bicarbonate-extractable phosphorus, sodium hydroxide-extractable phosphorus, hydrochloric acid-extractable phosphorus, and residual phosphorus.
Sequential extraction results are operationally defined fractions and are not equivalent to absolute chemical species. Different methods, extraction sequences, soil properties, and completeness of residue transfer can all affect the results. Therefore, the same study should maintain a consistent method system and avoid directly comparing data obtained from different fractionation methods.
5 Soil Organic Phosphorus and Total Phosphorus Difference Analysis
5.1 Position of Organic Phosphorus in the Soil Phosphorus Pool
Organic phosphorus includes phytate compounds, phospholipids, nucleic acids, and other organic phosphate esters, and is an important component of the potential soil phosphorus pool. Its plant availability is usually lower than that of active inorganic phosphorus. It must first be transformed into inorganic phosphorus through microbial mineralization or rhizosphere processes before entering the available phosphorus pool.
5.2 Estimation Methods for Organic Phosphorus
In routine research, organic phosphorus can be estimated using the difference between total phosphorus and inorganic phosphorus, or it can be characterized in greater detail using more complex chemical fractionation or nuclear magnetic resonance methods. The difference method is relatively simple and suitable for trend comparison, but its error is affected by both total phosphorus and inorganic phosphorus detection errors. Therefore, it should not be used to overinterpret specific organic phosphorus structures.
Analysis Method | Applicable Scenario | Advantages | Limitations |
Total phosphorus minus inorganic phosphorus | Routine organic phosphorus estimation | Relatively simple operation | Error accumulation and inability to identify specific structures |
Organic phosphorus fractionation | Organic fertilizer, straw return, ecological soil research | Can distinguish organic phosphorus fractions with different activities | Complex method and operationally defined results |
Refined analysis such as NMR | Structural analysis of organic phosphorus | Provides more information | High cost and high requirements for samples and instruments |
6 Sample Collection, Pretreatment, and Quality Control
6.1 Sampling Design
Soil phosphorus distribution has obvious spatial heterogeneity and is affected by fertilization position, root distribution, topography, soil depth, and long-term management practices. Farmland soils usually require multi-point composite sampling by plot or field. Rhizosphere studies should distinguish rhizosphere soil from non-rhizosphere soil. Profile studies should clearly define soil layer depth and sampling intervals.
6.2 Air-Drying, Grinding, and Sieving
Air-dried soil samples can usually be used for total phosphorus, available phosphorus, and most phosphorus fraction tests, but pretreatment conditions must be consistent. Plant residues, stones, and obvious impurities should be removed, and samples should be thoroughly mixed before grinding or sieving according to method requirements. Total phosphorus detection requires high sample homogeneity; insufficient grinding may affect digestion representativeness and result stability.
6.3 Dry Weight Correction
Different soil samples vary in moisture content, and detection results should be uniformly converted based on dry soil mass. For wet soils, rhizosphere soils, and long-term refrigerated soil samples, failure to correct for water content may cause bias in concentration results.
6.4 Blanks, Standard Curves, and Recovery
In colorimetric detection, reagent blanks, sample blanks, standard curves, and spike recovery are basic quality control requirements. Soil digests or extracts may contain color, turbidity, or salt interference. When necessary, sample blank correction or matrix-matched standards should be used.
Control Step | Common Problem | Key Handling Point |
Sampling | Insufficient sampling points and poor representativeness | Use multi-point composite sampling and record soil layer and field information |
Air-drying | High-temperature treatment changes fractions | Air-dry at room temperature and avoid external contamination |
Grinding | Sample is not homogeneous | Total phosphorus samples should be fully ground and mixed |
Digestion | Incomplete decomposition | Set digestion blanks, reference materials, or spike recovery |
Extraction | Inconsistent soil-to-solution ratio and extraction time | Standardize shaking time, temperature, and filtration conditions |
Colorimetry | Unstable color development or out-of-range absorbance | Control color development time and keep samples within the standard curve range |
Data conversion | Moisture content is ignored | Report results uniformly based on dry soil mass |
7 Result Interpretation and Combined Analysis
7.1 High Total Phosphorus and Low Available Phosphorus
This result suggests that the soil phosphorus pool is large, but short-term availability is limited. Common causes include fixation by iron/aluminum oxides, calcium fixation, insufficient organic phosphorus mineralization, or unsuitable soil pH. Subsequent testing of inorganic phosphorus fractions, pH, organic matter, and water-soluble phosphorus can further identify the limiting step.
7.2 Low Total Phosphorus and Low Available Phosphorus
This result usually suggests an insufficient soil phosphorus pool and weak short-term phosphorus supply capacity. If it is accompanied by low crop phosphorus uptake, yield limitation, or poor root development, fertilization history and crop demand can be combined to evaluate phosphorus supplementation measures.
7.3 High Total Phosphorus and High Available Phosphorus
Long-term heavy application of phosphate fertilizer, livestock and poultry manure, or sludge return may cause both total phosphorus and available phosphorus to increase. For such soils, phosphorus accumulation and environmental mobility risk should be emphasized. Water-soluble phosphorus, soil phosphorus saturation, or runoff risk evaluation is recommended.
7.4 Low Available Phosphorus but Non-Low Water-Soluble Phosphorus
This situation may be related to recent fertilization, localized phosphorus input, or insufficient sample mixing. Sampling time, fertilization interval, soil moisture status, and composite sample homogeneity should be checked to avoid misinterpreting short-term fluctuations as stable phosphorus supply capacity.
Result Combination | Possible Explanation | Recommended Follow-Up Analysis |
High total phosphorus, low available phosphorus | Strong phosphorus fixation or poorly available forms | Analyze Fe/Al/Ca-bound phosphorus |
Low total phosphorus, low available phosphorus | Insufficient phosphorus pool | Judge phosphorus supplementation needs together with fertilization history and crop phosphorus uptake |
High total phosphorus, high available phosphorus | Long-term phosphorus accumulation | Add water-soluble phosphorus and environmental risk evaluation |
Normal total phosphorus, low available phosphorus | pH or mineral fixation limits release | Detect pH, organic matter, and inorganic phosphorus fractions |
High available phosphorus, high water-soluble phosphorus | Strong phosphorus supply capacity but high mobility risk | Focus on runoff, leaching, and phosphorus saturation |
High inorganic phosphorus, low organic phosphorus | Phosphorus mainly exists in mineral or adsorbed forms | Determine Fe/Al/Ca fixation type |
High organic phosphorus, low available phosphorus | Large organic phosphorus pool but insufficient release | Further study mineralization processes and rhizosphere effects |
8 Common Misinterpretations in Soil Phosphorus Content Detection
8.1 Equating Total Phosphorus with Available Phosphorus
Total phosphorus represents the size of the phosphorus pool, not the phosphorus that plants can directly absorb. High total phosphorus with low available phosphorus is common in strongly fixed acidic soils and calcareous soils with calcium fixation.
8.2 Ignoring the Effect of Soil Type on Available Phosphorus Methods
Available phosphorus is a method-dependent indicator. Different soil pH levels and mineral compositions affect extraction efficiency. Acidic soils and calcareous soils should not be interpreted using the same logic.
8.3 Treating Inorganic Phosphorus Fractionation Results as Absolute Chemical Species
Sequential extraction yields operationally defined fractions rather than completely pure single chemical forms. Fractionation results are more suitable for trend comparison and fixation mechanism analysis, and should not be overinterpreted as absolute species contents.
8.4 Ignoring Time Effects After Fertilization
Within a short time after fertilization, water-soluble phosphorus and available phosphorus may increase rapidly and then undergo adsorption, precipitation, or transformation. If sampling times are not standardized, differences among treatments may mainly reflect fertilization timing effects rather than stable soil phosphorus supply capacity.
Common Misinterpretation | Problem | More Reasonable Approach |
High total phosphorus = sufficient phosphorus supply | Total phosphorus includes a large amount of poorly available phosphorus | Detect available phosphorus and phosphorus fractions together |
Low available phosphorus = definite phosphorus deficiency | The method may not be suitable for the soil type | Select the extraction method according to pH and regional standards |
Low water-soluble phosphorus = no environmental risk | Mobility risk may change shortly after rainfall or fertilization | Analyze together with sampling time and runoff conditions |
Fractionated phosphorus = true single species | Sequential extraction is operationally defined | Focus on relative changes and mechanistic interpretation |
No blanks or recovery tests | Colorimetric methods are easily affected by the matrix | Set reagent blanks, sample blanks, and spike recovery |
No dry weight correction | Moisture content affects concentration conversion | Report results uniformly based on dry soil mass |
9 Product Selection Related to Soil Phosphorus Content and Fraction Detection
9.1 Reagent Kits for Soil Total Phosphorus, Available Phosphorus, and Phosphate Detection
Cat. No. | Product Name | Grade & Purity | Application Module | Application Positioning |
Soil Total Phosphorus, Organic Phosphorus and Inorganic Phosphorus Content Assay Kit (Micro Method) | BioReagent | Combined detection of total phosphorus/organic phosphorus/inorganic phosphorus | Used for joint evaluation of the total soil phosphorus pool and different phosphorus fractions; suitable for small-sample or micro-assay systems | |
Soil Total Phosphorus, Organic Phosphorus and Inorganic Phosphorus Content Assay Kit (Colorimetric Method) | BioReagent | Combined detection of total phosphorus/organic phosphorus/inorganic phosphorus | Used for routine colorimetric analysis of soil total phosphorus, organic phosphorus, and inorganic phosphorus | |
Soil Total Phosphate Assay Kit (Micro Method) | BioReagent | Soil total phosphate detection | Used for determining total phosphate content in soil samples; suitable for the core main table of the article | |
Total Phosphate in Water and Soil Assay Kit (Micro Method) | BioReagent | Total phosphate detection in water and soil | Used for micro-detection of total phosphate in water and soil samples; suitable for soil-water migration evaluation | |
Total Phosphate in Water and Soil Assay Kit (Colorimetric Method) | BioReagent | Total phosphate detection in water and soil | Used for routine colorimetric detection of total phosphate in water and soil samples | |
Soil Inorganic Phosphate (S-PHOS) Content Assay Kit (MB, Micro Method) | BioReagent | Soil inorganic phosphorus detection | Used for determining soil inorganic phosphorus content and supporting phosphorus fraction or availability analysis | |
Acid Soil Available Phosphorous Assay Kit (Micro Method) | BioReagent | Available phosphorus detection in acidic soil | Used for determining rapidly available phosphorus in acidic soils; suitable for evaluating phosphorus supply capacity in acidic soils | |
Acid Soil Available Phosphorus Assay Kit (Colorimetric Method) | BioReagent | Available phosphorus detection in acidic soil | Used for routine colorimetric detection of rapidly available phosphorus in acidic soils | |
Neutral/Alkaline Soil Available Phosphorous Assay Kit (Micro Method) | BioReagent | Available phosphorus detection in neutral/alkaline soil | Used for determining rapidly available phosphorus in neutral and alkaline soils; suitable for Olsen-type phosphorus supply evaluation | |
Neutral/Alkaline Soil Available Phosphorus Assay Kit (Colorimetric Method) | BioReagent | Available phosphorus detection in neutral/alkaline soil | Used for routine colorimetric analysis of rapidly available phosphorus in neutral and alkaline soils | |
Inorganic phosphorus content detection kit (ferrous molybdenum blue sulfate, colorimetric method) | BioReagent | Inorganic phosphorus detection | Used for colorimetric detection of inorganic phosphorus in sample extracts or digests; can support soil phosphorus fraction analysis | |
Inorganic Phosphate Content Assay Kit (MMB, Colorimetric Method) | BioReagent | Inorganic phosphorus detection | Used for colorimetric detection of inorganic phosphorus; suitable for comparison of phosphate quantification methods | |
Inorganic Phosphate Content Assay Kit (UV Micro Method) | BioReagent | Inorganic phosphorus detection | Used for inorganic phosphorus detection in micro-assay systems and can be combined with soil extract analysis | |
Inorganic Phosphate Content Assay Kit (UV Colorimetric Method) | BioReagent | Inorganic phosphorus detection | Used for routine UV colorimetric detection of inorganic phosphorus | |
Malachite Green Phosphate Detection Kit | BioReagent, sterile | Phosphate detection | Used for phosphate content detection; suitable for soil extracts, digests, or water-soil migration samples | |
Phosphate Assay Kit (Phosphomolybdic Acid Method) | BioReagent, sterile | Phosphate detection | Used for colorimetric phosphate detection and can support total phosphate or available phosphorus detection | |
Water quality total phosphorus standard | Analytical standard, 1.000-2.000 mg/L in water (after dilution) | Total phosphorus quality control | Can be used as a method calibration and quality control reference in water-soil total phosphate detection |
9.2 Phosphorus, Phosphate Ion, and Phosphate Standards/Quality Control Products
Cat. No. | Product Name | Grade & Purity | Application Module | Application Positioning |
Phosphorus solution | 100 μg/mL (as P) | Phosphorus standard curve | Used for low-concentration phosphorus standard curves or quality control | |
Dihydrogen Phosphate in Water | 1000 mg/L, matrix: water | Dihydrogen phosphate standard | Used for calibration of dihydrogen phosphate-related detection | |
Standard Reference Material for Dihydrogen Phosphate Composition Analysis in Water | 1000 μg/mL ±1% (20℃) | Dihydrogen phosphate standard | Used for aqueous dihydrogen phosphate standard curves or method validation | |
Phosphate standard | 1000 μg/mL in water (20℃) | Phosphate standard | Used for phosphate detection standard curves and quality control | |
Phosphate standard | 500 μg/mL in water (20℃) | Phosphate standard | Used for quantitative calibration of medium-concentration phosphate ions | |
Phosphate standard | 100 μg/mL in water (20℃) | Phosphate standard | Used for calibration of low-concentration phosphate ion detection | |
Phosphate standard | 100 μg/mL | Phosphate standard | Used for standard curves in phosphate colorimetric methods | |
Phosphate anion standard solution | 1 mg/mL (1,000 ppm) | Phosphate standard | Used for calibration of phosphate anion detection | |
Phosphate anion standard solution | 0.1 mg/mL (100 ppm) | Phosphate standard | Used for calibration of low-concentration phosphate anion detection |
9.3 Auxiliary Products for Mechanistic Interpretation and Result Analysis
Cat. No. | Product Name | Grade & Purity | Application Module | Application Positioning |
Soil Total Iron Content Assay Kit (o-Phenanthroline, Micro Method) | BioReagent | Fe-P interpretation auxiliary indicator | Used to assist in analyzing the background of iron-bound phosphorus fixation; suitable for mechanistic interpretation in acidic or iron-rich soils | |
Soil Total Iron Content Assay Kit (Phenanthroline, Colorimetric Method) | BioReagent | Fe-P interpretation auxiliary indicator | Used for routine colorimetric detection of soil total iron and assisting in interpreting the possibility of Fe-P formation | |
Soil Organic Matter (SOM) Content Assay Kit (Micro Method) | BioReagent | Organic matter auxiliary indicator | Used to interpret phosphorus adsorption, complexation, organic phosphorus pools, and available phosphorus changes | |
Soil Organic Carbon (SOC) Content Assay Kit (Micro Method) | BioReagent | Organic carbon auxiliary indicator | Used to assist in analyzing soil organic matter background and the transformation environment of phosphorus fractions |
The core of soil phosphorus content detection is to distinguish total phosphorus pool size, short-term phosphorus supply capacity, and phosphorus fixation forms. Total phosphorus is used to evaluate soil phosphorus reserves, available phosphorus is used to assess plant availability, and inorganic phosphorus fractions are used to explain phosphorus fixation and release mechanisms.
For more related articles, please see below:
[1] Cadmium, Copper, Zinc and Lead Determination Experiment in Soil
[2] Experimental determination of chromium in soil by colorimetric method of dibenzoyl dihydrazide
