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Dichlorophenolindophenol

2,6-Dichlorophenolindophenol (DCPIP), systematically named 4-(3,5-dichloro-4-hydroxyphenyl)iminocyclohexa-2,5-dien-1-one, is a synthetic quinone used primarily as a indicator and dye in biochemical and . Its molecular formula is C₁₂H₇Cl₂NO₂, with a molecular weight of 268.09 g/mol, and it features substituents at the 2 and 6 positions of the phenolic ring. In the oxidized state, DCPIP exhibits a color due to maximal light absorption at approximately 600 nm, while converts it to a colorless leuco form, enabling visual or spectrophotometric detection of reactions. The compound's utility stems from its standard reduction potential of about +0.217 , allowing selective interaction with biological reductants without interfering with other cellular components. Commonly prepared as the water-soluble sodium salt (C₁₂H₆Cl₂NNaO₂), which appears as a dark green solid, DCPIP is employed in acid-base and titrations. Its in aqueous solutions facilitates applications in various media, though it is sparingly soluble in non-polar solvents. One of the most prominent applications of DCPIP is in the quantitative determination of ascorbic acid (vitamin C), where it serves as a titrant that undergoes specific reduction by ascorbate, resulting in decolorization at the endpoint for precise measurement via iodometric or direct titration methods. In plant biology, DCPIP acts as an artificial electron acceptor in the Hill reaction to assess photosynthetic electron transport rates in isolated chloroplasts, with the rate of blue-to-colorless transition monitored spectrophotometrically at 600 nm to quantify photosystem II activity under varying light intensities. Beyond these, DCPIP is utilized in biochemical oxygen demand (BOD) assays and enzymatic studies, such as evaluating tyrosine hydroxylase or acyl-CoA dehydrogenase activities through absorbance changes at specific wavelengths like 578 nm or 603 nm. Emerging research highlights DCPIP's potential as a pro-oxidant in , particularly for inducing and in cells by depleting and inhibiting NQO1-dependent reduction, though its clinical use remains investigational. Safety considerations include its classification as an irritant to , eyes, and respiratory tract, necessitating proper handling in laboratory settings.

Chemical Properties

Structure and Formula

2,6-Dichlorophenolindophenol, also known by the acronyms DCPIP, DCIP, or DPIP, is the systematic chemical name for this compound, reflecting its derivation from with dichlorophenol substitution. Its molecular formula is C₁₂H₇Cl₂NO₂, consisting of 12 carbon atoms, 7 atoms, 2 atoms, 1 atom, and 2 oxygen atoms arranged in a specific . The molecular weight of 2,6-dichlorophenolindophenol is 268.09 g/, calculated from the masses in its formula. Structurally, it is a derivative of , characterized by a central cyclohexa-2,5-dien-1-one () ring linked through a C=N to a phenyl ring bearing a and substituents at the positions (2 and 6 relative to the ). The IUPAC name, 4-[(3,5-dichloro-4-hydroxyphenyl)imino]cyclohexa-2,5-dien-1-one, precisely denotes this arrangement, where the linkage and conjugated π-system form the core framework essential to its chemical identity. The specifically refers to the 2,6-isomer, distinguished by the symmetric placement of atoms on the , which is the predominant and standard form documented in chemical for its defined properties and applications. This isomer's structure can be visualized as a bicyclic-like system without fusion, with the featuring alternating double bonds and the bridge connecting to the substituted , highlighting the electron-withdrawing chlorines adjacent to the hydroxyl.

Physical Characteristics

Dichlorophenolindophenol is most commonly encountered as its , which appears as a dark to crystalline powder in its oxidized form. This form is hygroscopic and often supplied as a dihydrate with the molecular C12H6Cl2NNaO2·2H2O. The compound exhibits good in polar solvents, dissolving readily in to approximately 10 mg/mL at , as well as in and alkaline solutions where increases due to its pH-dependent behavior. It is insoluble in non-polar solvents such as or , reflecting its ionic character in the sodium salt form. The melting point of the sodium salt is greater than 300 °C, at which point it typically decomposes rather than melting cleanly. In its dry, solid state, it remains stable under normal laboratory conditions but is sensitive to light exposure and reducing agents, which can lead to gradual discoloration or reduction over time.

Redox and Spectroscopic Properties

Dichlorophenolindophenol (DCPIP), in its oxidized form, exhibits a distinctive blue color due to strong absorption in the , with a maximum at 600 nm and a extinction coefficient (ε) of approximately 21,000 M⁻¹ cm⁻¹ in neutral aqueous solutions. This high absorptivity enables sensitive spectrophotometric detection of changes. Upon reduction, the compound shifts to a colorless or pale yellow leuco form, with the primary absorption moving to the region around 390 nm, rendering it transparent in the visible range and facilitating easy monitoring of the reaction progress via decolorization. The behavior of DCPIP involves a (E°) of approximately +0.217 V versus the (SHE) at 7, positioning it as an effective mediator for biological processes. The mechanism proceeds via one- at the quinone imine moiety, initially forming a semiquinone intermediate (DCPIPH•), which is further reduced to the fully leuco form (DCPIPH₂). This can be represented as: \text{DCPIP (ox, blue)} + e^- \rightarrow \text{DCPIPH• (radical)} \rightarrow \text{DCPIPH}_2 \text{ (colorless)} DCPIP's redox properties are notably pH-dependent, with optimal performance as an indicator in the range of pH 4–8, where the color change is sharp and reversible. Outside this range, protonation affects the stability of both oxidized and reduced forms, potentially shifting the absorption maxima or altering the by up to 60 mV per pH unit due to involvement of protons in the quinone imine reduction. Ultraviolet-visible (UV-Vis) is the primary technique for real-time monitoring of DCPIP reduction, typically at 600 nm, while provides insights into transient radical species during mechanistic studies.

Synthesis and Preparation

Laboratory Synthesis

The classical laboratory synthesis of 2,6-dichlorophenolindophenol (DCPIP) involves the between phenol and 2,6-dichloroquinone-4-chlorimide (also known as Gibbs' ) in an alkaline medium. This method, originally developed for analytical purposes but adaptable for small-scale preparation, proceeds via nucleophilic attack by the phenoxide on the carbon attached to the chloroimino group of the quinone chlorimide, followed by tautomerization to form the indophenol dye. The reaction is typically conducted in aqueous or at 9.4 and , with the mixture stirred for 30-60 minutes until the blue color develops fully. The balanced for the key coupling step is: \ce{C6H5OH + C6H2Cl3NO -> C12H7Cl2NO2 + HCl} where C6H2Cl3NO represents 2,6-dichloroquinone-4-chlorimide and C12H7Cl2NO2 is DCPIP. The product is isolated by acidification to precipitate the free acid form, followed by . Purification is achieved by recrystallization from hot or using dichloromethane-methanol eluents, yielding the dark blue crystalline product. Safety precautions during synthesis include conducting reactions in a due to the volatile and corrosive nature of chlorinating agents and oxidants like the chlorimide; (gloves, goggles, lab coat) is essential to avoid skin and eye irritation from these irritants.

Commercial Production

Dichlorophenolindophenol, commonly available as its sodium salt hydrate, is commercially produced by several major chemical suppliers, including (Merck KGaA), HiMedia Laboratories, and Chem-Impex International, which synthesize and distribute it primarily for and applications. Key raw materials include 2,6-dichlorophenol, derived from phenol via chlorination, along with amines such as and oxidizing agents, processed under controlled acidic conditions with phase transfer catalysts to yield the . The compound is offered in various purity grades to suit different uses: technical grade exceeding 90% purity for general applications, ACS grade at 99% or higher for , and specialized BioReagent or () grades meeting pharmacopeial standards for biochemical assays. Global supply is centered in (e.g., via Merck) and Asia (e.g., via HiMedia), with distribution extending to through subsidiaries and partners, ensuring availability for research institutions worldwide. Production volumes are not publicly detailed but support a for lab reagents, with suppliers handling batches in the range of grams to kilograms per order. Cost factors are influenced by raw material prices, such as phenol (around $1-2 per kg) and chlorinating agents, alongside purification processes like , resulting in pricing of approximately $50-200 per 25 g depending on purity grade and supplier—for instance, ACS-grade material at about $100-150 per 25 g from major vendors.

Applications

Redox Indicator in Analytical Chemistry

Dichlorophenolindophenol (DCPIP) serves as a indicator in , particularly for detecting the in titrations involving reducing agents. In its oxidized form, DCPIP exhibits a color in neutral solutions, which shifts to colorless upon reduction by the analyte. This color change facilitates visual detection in titrations, where the transition occurs near the formal of approximately +0.217 V versus the . In common titrations, DCPIP is employed for direct by analytes such as ascorbic acid, often in to or as an to iodometric methods, which rely on iodine liberation for indication. The involves preparing the sample in an acidic medium, such as metaphosphoric acid, to stabilize the system and adjust the indicator's color to for the oxidized form. The DCPIP solution (typically 0.05–0.1% w/v, standardized against a known reductant) is then added dropwise to the sample until the color persists for 5–30 seconds, marking the where excess oxidized DCPIP is no longer reduced. The sensitivity of DCPIP allows detection of reductants at micromolar concentrations, achieved through visual or spectrophotometric measurement of at 600 nm, where the molar is 19.1 mM⁻¹ cm⁻¹. Standard curves are constructed by plotting against known concentrations of reductant, enabling with limits of detection around 7–10 µg/mL for typical analytes. Advantages of using DCPIP include its rapid response, allowing titrations to be completed in minutes, and its visual detectability without requiring sophisticated in basic setups, making it suitable for routine analyses. However, limitations arise from potential by other colored species in the sample, which can obscure the , and to pH extremes, where the color change may shift or become indistinct outside the optimal acidic range ( 3–4).

Biochemical and Biological Uses

Dichlorophenolindophenol (DCPIP) functions as an artificial in biochemical studies of , particularly in the Hill reaction with isolated chloroplasts from plants such as . During illumination, splits water to release electrons, which reduce DCPIP from its oxidized blue form to a colorless , mimicking the natural transfer to NADP⁺ and enabling . The rate of the Hill reaction is quantified by the of DCPIP decolorization, measured via spectrophotometric changes at 600 nm or 640 nm over time, providing insights into photosynthetic electron transport efficiency under varying light intensities. In enzyme assays, DCPIP evaluates the activity of reductases, including and (complex II), by serving as a two-electron acceptor that undergoes detectable at nm (ε = 21 mM⁻¹ cm⁻¹). NADH generated by the reduces DCPIP to DCIPH₂, allowing real-time monitoring of enzymatic kinetics in isolated systems or coupled reactions, often with mediators like decylubiquinone to ensure complete turnover. This approach reveals function in pathways, though it may underestimate activity due to non-specific interactions with other respiratory components. DCPIP probes the mitochondrial in animal cells, such as bovine heart submitochondrial particles, by measuring NADH-dependent reduction rates that reflect complex I () activity and oxidative damage responses. It is also applied in cellular viability assays to gauge capacity, where cellular reducing agents compete with DCPIP for oxidation, indicating protective mechanisms against . In microbiological contexts, DCPIP assesses bacterial reducing power through color changes upon reduction by NADH-dependent oxidoreductases, with rates correlating to formation and density in species like and . Biologically, DCPIP mimics natural electron acceptors like ferredoxin or quinones due to its redox potential of +0.217 V, facilitating interception of electrons in transport chains without disrupting overall physiology at low concentrations (e.g., 0.1–0.4 mM) for short experimental exposures.

Specific Assays and Measurements

Dichlorophenolindophenol (DCPIP) serves as a key in the Tillmans method for quantifying ascorbic acid () content in biological and food samples through . In this standardized protocol, a sample extract is titrated with a 0.1% (w/v) DCPIP solution (1 mg/mL) under acidic conditions until the color persists for at least 30 seconds, indicating complete oxidation of ascorbic acid to . The reaction proceeds via a 1:1 stoichiometry, where ascorbic acid donates two electrons to reduce the oxidized DCPIP (, absorbing at ~600 nm) to its colorless leuco form. The equivalence factor is established such that 1 mL of 1 mg/mL DCPIP corresponds to 0.5 mg of ascorbic acid, calibrated against pure standards to account for the potentials and molecular weights involved. The ascorbic acid concentration (in mg/mL) is calculated as: concentration = (volume of DCPIP used in mL × 0.5) / volume of sample extract in mL. This method, originally developed in 1932, remains a for routine in juices and pharmaceuticals due to its simplicity and specificity for reduced ascorbic acid. A variant of DCPIP-based assays measures total antioxidant capacity in food extracts and biological fluids by evaluating the dye's reduction rate, analogous to the ferric reducing antioxidant power (FRAP) assay but using DCPIP as the electron acceptor instead of Fe³⁺-TPTZ complex. In this protocol, 1 mL of sample (e.g., plant extract at 100–400 μg/mL) is mixed with 1 mL of 0.05% DCPIP in bicarbonate buffer (pH ~7.5), incubated for 5–30 minutes, and the decrease in absorbance at 600 nm is recorded to quantify inhibition percentage: % inhibition = [(A_control – A_sample) / A_control] × 100, where higher values indicate greater reducing power. This approach captures the cumulative electron-donating ability of antioxidants like phenolics and ascorbic acid, with validation showing linearity up to 400 μg/mL equivalents and insensitivity to pH variations (2–9), making it faster than traditional FRAP for high-sample workloads. Representative results from rosemary and chili extracts demonstrate 80–95% inhibition at 400 μg/mL after 5 minutes, establishing its utility for total reducing capacity in complex matrices. In photosynthetic research, DCPIP quantifies the light-dependent electron transport rate via the Hill reaction in isolated thylakoids or chloroplasts. Chloroplasts (typically 20–50 μg chlorophyll/mL) are suspended in phosphate buffer (pH 7.5) with 50–100 μM DCPIP, illuminated (e.g., 100–500 μmol photons/m²/s), and the reduction rate monitored by decrease at 600 nm (ε = 19,100 M⁻¹ cm⁻¹). Each reduced DCPIP accepts two electrons from , mimicking NADP⁺ reduction while evolving O₂. The rate is expressed as μmol electrons transferred per mg per hour, calculated as: rate = (ΔA₆₀₀ / ε × path length × time in h) × 2 × (total volume / mass in mg), often yielding 100–300 μmol e⁻/mg chl/h in spinach thylakoids under optimal white light. This assay, adapted from Hill's 1937 observations, provides a direct measure of efficiency and is widely used to evaluate environmental stressors or inhibitors like . Assay validation involves against pure ascorbic acid or known donors, ensuring (R² > 0.99) and rates of 95–105% across 0.1–10 mg/L ranges. Interferences from metal ions, such as Fe³⁺ or Cu²⁺ (at >10 μM), arise because they catalyze ascorbic acid oxidation or directly reduce DCPIP, leading to overestimation; corrections include pre-treatment with EDTA (1 mM) or to remove metals, restoring accuracy to <5% error in spiked samples like fruit juices. For photosynthetic assays, omission or uncouplers validate specificity to activity. These steps ensure , with intra-assay coefficients of variation typically <3%. Modern adaptations employ spectrophotometry for high-throughput DCPIP assays, enabling parallel analysis of 48–96 samples. In a miniaturized protocol, 100–200 μL sample aliquots are pipetted into 96-well plates with 50 μL 0.05% DCPIP, mixed, and at 520–600 read kinetically over 1–5 minutes using a (e.g., 200–1000 scan range). This reduces use by 80% and analysis time to 2.5 hours for batches, with from 0–200 mg/L ascorbic acid and precision (CV <2%) comparable to traditional . Similar formats for and assays facilitate screening of extracts or mutant lines, enhancing throughput in control and studies.

Safety and Biological Effects

Toxicity Profile

Dichlorophenolindophenol (DCPIP), typically used as its sodium salt, demonstrates low in available data. Safety assessments indicate no specific oral LD50 value for rats, though related studies suggest moderate with intravenous LD50 values around 180 mg/kg. The compound is classified as a irritant (Category 2) and eye irritant (Category 2) under the Globally Harmonized System (GHS), potentially causing redness, pain, and temporary upon contact. Chronic exposure effects are limited in documentation, with no strong evidence of carcinogenicity in standard classifications such as IARC or NTP. However, its quinone imine structure raises concerns for potential mutagenicity, as it can trigger genotoxic stress responses in cells, including upregulation of genes like GADD45A associated with DNA damage. The primary toxicity mechanism involves redox cycling, where DCPIP accepts electrons from cellular reductants and subsequently reduces oxygen to generate reactive oxygen species (ROS), leading to oxidative stress, glutathione depletion, and disruption of cellular respiration and energy metabolism. This process is particularly pronounced in high-exposure scenarios, contributing to cytotoxicity in sensitive tissues. Common exposure routes in laboratory settings include inhalation of dust particles and direct skin contact during handling, though its low volatility as a solid minimizes vapor inhalation risks. Regulatory evaluations classify DCPIP as non-hazardous under GHS at typical low concentrations used in applications, with the sodium salt registered under EU REACH (EC 210-640-4).

Handling and Environmental Impact

Dichlorophenolindophenol (DCPIP), typically handled as its sodium salt, should be stored in a cool, dry place within tightly sealed, airtight containers to prevent moisture absorption and degradation, ideally at temperatures around -20°C or as specified on the product label, while avoiding exposure to light, reducing agents, and incompatible materials such as strong oxidizers..pdf) Safe handling requires the use of , including chemical-resistant gloves, safety goggles, and protective clothing, with operations conducted in a well-ventilated to minimize of or vapors from solutions; good practices, such as washing hands after use and avoiding eating or drinking in the area, are essential to prevent accidental or ..pdf) In the event of spills, absorb the material with inert absorbents, dilute any residues with large quantities of water, and collect for disposal, ensuring to avoid formation..pdf) Disposal of DCPIP and its solutions, particularly the reduced (leuco) form which may require neutralization through oxidation prior to treatment, must follow local, state, and federal regulations; unused product, residues, and contaminated packaging should be directed to a licensed chemical waste disposal facility, with incineration under controlled conditions or treatment as hazardous waste recommended, avoiding direct release into sewers or waterways..pdf) In the , DCPIP exhibits moderate in aqueous systems, with limited biodegradability (approximately 4% over 28 days under conditions), leading to a on the order of days influenced by factors such as and exposure; its high as a results in low potential in organisms. It poses risks to ecosystems, particularly through inhibition of algal , with an ErC50 of 3.44 mg/L for growth rate in Pseudokirchneriella subcapitata over 72 hours, and broader toxicity evidenced by LC50 values of 1.24 mg/L for fish (Carassius auratus, 96 hours) and EC50 of 2.8 mg/L for immobilization (48 hours). Handling and disposal of DCPIP are governed by general laboratory safety standards from the (OSHA), including requirements for and ventilation under 29 CFR 1910.132 and 1910.134, while the Environmental Protection Agency (EPA) regulates it under the Toxic Substances Control Act (TSCA) inventory, with waste management aligned to (RCRA) guidelines for hazardous chemical disposal to prevent environmental release..pdf)

History and Development

Discovery and Early Research

The development of indophenol dyes, including precursors to dichlorophenolindophenol (DCPIP), traces back to the mid-19th century amid advances in synthetic from derivatives. The formation of was first reported in 1859 by Marcelin Berthelot through the oxidation of phenol in the presence of using , establishing the class of quinone imine dyes known for their intense blue color and properties. These early compounds laid the groundwork for later chlorinated variants, as chemists explored substitutions to enhance stability and electrochemical behavior during the late 19th and early 20th centuries. DCPIP itself emerged in the 1920s through work by German chemists investigating redox-active dyes. , a specializing in oxidation-reduction potentials, conducted foundational electrochemical studies on derivatives, including chlorinated forms, to characterize their reversible mechanisms. Michaelis's experiments, published in the early 1930s, demonstrated the utility of these indicators with defined midpoint potentials around +0.217 V, influencing the adoption of DCPIP in biochemical assays. In , DCPIP gained prominence as a indicator for ascorbic acid () quantification, pioneered by Julius Tillmans and collaborators. Tillmans introduced a method in 1930, where the blue oxidized form of DCPIP is decolorized by with ascorbic acid, allowing precise measurement of the vitamin's concentration in foodstuffs. This approach, detailed in subsequent papers (e.g., Tillmans et al., 1932), became a standard for nutritional analysis before ascorbic acid's full chemical identification in 1933. Key advancements linked DCPIP to research in 1937, when British biochemist Robert Hill demonstrated by isolated chloroplasts using artificial electron acceptors. Although Hill initially employed , his work established the non-cyclic , with DCPIP later serving as a preferred substitute due to its visible color change upon reduction, facilitating spectrophotometric monitoring. This "Hill reaction" provided early evidence for independent of carbon fixation. During , amid food shortages and nutritional deficiencies, DCPIP titrations saw expanded use in biochemical research for assessing in rationed supplies and biological samples. Seminal publications in the during investigated the Tillmans method's reliability and modifications for tissue extracts, solidifying DCPIP's role in quantitative studies. These early applications highlighted DCPIP's , driving its integration into wartime health protocols.

Modern Advancements and Research

Since the early 2000s, dichlorophenolindophenol (DCPIP) has found applications in , particularly as an in biohybrid systems mimicking for . In studies integrating (PSI) into dye-sensitized solar cells, DCPIP serves as a probe to monitor efficiency, enabling the assessment of light-driven charge separation in gel-based devices that achieve enhanced outputs compared to natural systems alone. For instance, in artificial photosynthetic cells combining biotic and abiotic components, DCPIP reduction confirms electron flow from PSI to interfaces, supporting advancements in harvesting. Similarly, electrochemiluminescence-driven systems utilize DCPIP to quantify electron acceptance from , revealing potential for scalable bio-solar technologies. Analytical methodologies involving DCPIP have evolved toward more sensitive detection techniques, including electrochemical and potentiometric sensors that surpass traditional visual . Post-2015 developments include ion-selective electrodes incorporating DCPIP for real-time quantification of total phenolics and ascorbic acid in beverages, offering high selectivity and stability over extended periods. Fluorometric approaches, while less common, complement these by integrating DCPIP in s for ascorbic acid detection, with limits of detection improved through nanostructured probes. In integration, DCPIP-mediated systems have enabled oxygen-insensitive amperometric glucose sensing via flavin adenine dinucleotide-dependent enzymes, facilitating portable devices for clinical and . Ongoing research highlights DCPIP's role in investigating under climate stress and in evaluation for nutraceuticals. In studies addressing elevated temperatures and CO2 levels, DCPIP reduction assays measure electron transport rates in thylakoids, demonstrating how environmental changes impair and informing strategies. For nutraceuticals, DCPIP-based titrations assess and total capacity in fruit peels and herbal extracts, validating its use in quality control for products like and derivatives with pH-independent accuracy. A key 2023 study elucidated DCPIP's dual role as both donor and acceptor in electron transfer, revealing kinetic factors that enhance its utility in bioenergetic models. Future research directions emphasize developing eco-friendly DCPIP variants or biodegradable analogs to mitigate potential environmental persistence, as evidenced by photocatalytic degradation studies showing UV-induced breakdown under controlled conditions.

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